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DRAINAGE REPORT
for
PIPER'S BLUFF
� 1166 Hoquiam Avenue NE Renton,Washington
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DRS Project No. 12029
Renton File No. LUA12-076, ECF, PP
OwnedApplicant
WestPac Development, LLC
7449 W Mercer Way
Mercer Island, WA 98040
Reporf Prepared by
- , •
! D. R. STRONG Consulting Engineers, Inc.
10604 N.E. 38th Place, Suite 232
Kirkland WA 98033
(425) 827-3063
;
Issued August 29, 2012
Revised January 31, 2013
.
Revised April 29, 2013
�2012 D. R. STRONG Consulting Engineers Inc.
DRAINAGE REPORT
_ PIPER'S BLUFF
TABLE OF CONTENTS
� SECTION 1.......................................................................................................................1
ProjectOverview..........................................................................................................1
Predeveloped Site Conditions......................................................................................1
Developed Site Conditions...........................................................................................1
Natural Drainage System Functions.............................................................................2
SECTION11....................................................................................................................11
Conditions and Requirements Summary....................................................................11
SECTION111...................................................................................................................13
Off-Site Analysis.........................................................................................................13
SECTIONIV ..................................................................................................................14
Flow Control and Water Quality Facility Analysis and Design....................................14
Existing Site Hydrolo9Y �Part A)..............................................................................14
Pre-developed Hourly Time Step Modeling Input: ..................................................15
Pre-developed Hourly Time Step Modeling Output:................................................15
Developed Site Hydrolo9Y (Part B).........................................................................17
Developed Site Area Hydrology..............................................................................17
Developed Hourly Time Step Modeling Input:.........................................................18
Developed Hourly Time Step Modeling Output:......................................................18
Performance Standards (Part C)................................................................................20
Flow Control System (Part D).....................................................................................20
Flow Control BMP Selection ...................................................................................20
Flow Control Facility Design Output........................................................................22
Water Quality Treatment System (Part E)..................................................................28
SECTIONV ...................................................................................................................30
Conveyance System Analysis and Design.................................................................30
SECTIONVI ..................................................................................................................36
Special Reports and Studies......................................................................................36
SECTIONVII .................................................................................................................36
Other Permits, Variances and Adjustments................................................................37
SECTIONVIII ................................................................................................................38
ESC Plan Analysis and Design (Part A).....................................................................38
SWPPS Plan Design (Part B).................................................. ........38
...........................
:�:2013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page i of ii
Drainage Report C;ty of Renton
SECTIONIX ..................................................................................................................39
Bond Quantities, Facility Summaries, and Declaration of Covenant..........................39
Stormwater Facility Summary Sheet..........................................................................40
SECTIONX ...................................................................................................................42
Operations and Maintenance Manual ........................................................................42
� List of Figures
Figure1 TIR Worksheet...................................................................................................3
Figure2 Vicinity Map .......................................................................................................6
Figure 3 Drainage Basins, Subbasins, and Site Characteristics......................................7
Figure4 Soils...................................................................................................................8
Figure 5 Predevelopment Area Map..............................................................................15
Figure 6 Post Development Area Map...........................................................................18
Figure 7 Detention & Water Quality Facility Details .......................................................29
Figure 8 Backwater Analysis Map..................................................................................35
Appendices
Appendix A— Stormwater Pollution Prevention Plan .....................................................43
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02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page ii of ii
Drainage Report City of Renton
SECTION I
PROJECT OVERVIEW
The Project is the subdivision of four existing parcels zoned R8 into 28 single-family
residential lots, per the City of Renton's (City) subdivision process. The Tax Parcel
Numbers are 102305-9367, 9312, 9002, and 9144. The Project location (Site) fronts on
the east side of Hoquiam Avenue NE, at 1166 Hoquiam Avenue NE. One detention
pond and a Stormfilter is proposed to serve the subdivision. 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 217,369 s.f. (4.990 ac). Total proposed Project
area is 216,966 s.f. (4.981 ac), which includes 10,337 s.f. (0.237 ac) for the right-of-way
frontage improvements on Hoquiam Avenue NE and excludes 10,740 s.f. (0.247 ac) of
Tract "B" (NGPA). The Parcels are currently developed with two single-family
residences, three out buildings and gravel driveway. The remainder of the Site is lawn,
landscaping, scatter trees, moderately dense forest and underbrush. For the purpose of
hydrologic calculations, the entire Site is modeled as till forest.
DEVELOPED SITE CONDITIONS
The Project will create 28 lots with lot sizes ranging from approximately 4,500 s.f. to
5,725 s.f. All existing improvements will be demolished or removed during plat
construction. Two 16-foot wide alleys are proposed for Lots 1 to 17 for garage access.
The 28 single-family residences combined with their driveways and alleys will create
approximately 86,988 s.f. (1.997 ac) of impervious area. The proposed 45-foot right of
ways will be improved with 18 feet of pavement, vertical curb, gutter, 8-foot planter strip,
5-foot sidewalk and a 8-foot parking lane on one side. The proposed right-of way
adjacent to north property line will be 33-feet wide and will be improved with 15 feet of
pavement, vertical curb, gutter, 8-foot planter strip, 5-foot sidewalk and a 8-foot parking
lane on one side. The half street frontage improvements on Hoquiam Avenue NE will
be improved with the required pavement width (approximately 12.80 feet) to provide 36
feet of pavement face of curb to face of curb, vertical curb, gutter, eight-foot planter strip
and a five-foot sidewalk on the east side of Hoquiam Avenue NE. The 20-foot wide joint
use driveway Tract "D" will be improved with 18 feet of pavement to serve lots 27 and
28. The improvements from right-of ways and joint use driveway tract will add 45,020
s.f. (1.034 ac) of impervious surFace. The paved access to detention facility and sewer
lift station in Tract "A" will add 6,041 s.f. (0.139 ac) of impervious surface. The Project
will result in a total of 138,049 s.f. (3.169 ac) of new impervious surfaces. The
remainder of the developed Site 78,917 s.f. (1.812 ac) will consist of landscaping and
lawns.
The Project is required to provide Basic Water Quality treatment and Level 2 Flow
Control, per the 2009 KCSWDM (Manual}. All surface water runoff from impervious
surfaces will be collected and conveyed to a storm detention pond and media filter
located in Tract "A. A 96-inch diameter Stormfilter manhole will be located downstream
of detention and will provide 0.22 cfs of treatment flow rate. See the attached Contech
02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 1 of 43
Drainage Report City of Renton
Stormwater Solution, Inc, design details in Section X. The vault detention volume
required is 69,132 c.f. and provided is 71,895 c.f. with 14 ft. of live storage depth.
NATURAL DRAINAGE SYSTEM FUNCTIONS
The Site is encompassed within one Threshold Discharge Area (TDA). The Site
topography slopes generally to the east and northeast at approximately 2 to 15%. The
vegetation consists of lawn, landscaping, and scattered trees in the house areas
towards the southwestern and western regions of the Site. The remainder of the Site is
� heavily vegetated with native grasses and shrubs, berry bushes, and moderately dense
forest. Site runoff travels northeasterly and enters a Category 2 Wetland located near
the northeast property corner and then exits to north via Class 4 Stream which is also
located adjacent to the wetland near the northeast property corner.
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) and Alderwood gravelly sandy
loam with 15 to 30 percent slopes (AgD). 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.
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02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 2 of 43
Drainage Report City of Renton
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
PROJECT ENGINEER DESCRIPTION
Project Owner: Project Name:
WestPac Development, LLC Piper's Bluff
Address/Phone: Location:
7449 W Mercer Way Township: 23 North
Mercer Island, WA 98040 Range: 05 East
Section: 10
Project Engineer:
Luay R. Joudeh, P.E.
D. R. STRONG Consulting Engineers Inc.
Address/Phone:
10604 NE 38�' Place, Suite 101
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 � Pond with Structural
❑ Other: Retaining Walls
- ❑ FEMA Floodplain ❑ Other:
❑ COE Wetlands
Part 5 SITE COMMUNITY AND DRAINAGE BASIN
Community:
Renton
Drainage Basin
May Creek
02013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 3 of 43
Drainage Report City of Renton
Part 6 SITE CHARACTERISTICS
❑River: ❑ Floodplain
� Wetland
� Stream: ❑ Seeps/Springs
❑ Critical Stream Reach ❑ High Groundwater Table
❑ Depressions/Swales ❑ Groundwater Recharge
❑ Lake: ❑ Other: ,
❑ Steep Slopes
Part 7 SOILS �,
Soil Type: Slopes: Erosion Potential: Erosive Velocities:
Alderwood 6-15% Slight Slow
(AgC)
Alderwood 15-30% Slight Slow i
(AgD) �
�Additional Sheets Attached: SCS Map and Soil Description, Figure 4
Part 8 DEVELOPMENT LIMITATIONS
REFERENCE LIMITATION/SITE CONSTRAINT
� Level 1 Downstream Anatysis None
� Geotechnical Engineering Study
� Environmentally Sensitive Areas
❑ Level 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 Entrance �Remove and Restore Temporary ESC 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
�2013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 4 of 43
Drainage Report City of Renton
Part 10 SURFACE WATER SYSTEM
❑ Grass Lined ❑ Tank ❑ infiltration Method of Analysis:
Channel � Pond ❑ Depression KCRTS
� Pipe System � Energy Dissipater ❑ Flow Dispersal Compensation/Mitigation
❑ Open Channel � Wetland ❑ Waiver of Eliminated Site
� Dry Pond � Stream ❑ Regional Storage
❑ Wet Pond Detention N/A
� Brief Description of System Operation: Runoff from impervious surfaces will be collected
and conveyed to the detention facility. From there it will be discharged near the existing
wetland located at the Site's northeast corner.
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 obser�ved re incor orated into this worksheet and the attachments. To the best
of m c�ow ge he inf 9fimation provided here is accurate.
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:,2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 5 of 43
Drainage Report City of Renton
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 liabie 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.
C2013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 6 of 43
Drainage Report City of Renton
FIGURE 3
DRAINAGE BASINS, SUBBASINS, AND SITE CHARACTERISTICS
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�2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 7 of 43
Drainage Report City of Renton
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SOILS
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i AgC—Alderwood graveliy sandy loam, 6 to 15 percent slopes
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Map Unit Setting
� Elevation: 50 to 800 feet
Mean annual precipifafion: 25 to 60 inches
li . Mean annual air temperature: 48 to 52 degrees F
' ` Frost-free period: 180 to 220 days
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� Map Unit Composition
( Alderwood and similar soils: 95 percent
�'�I Minor components: 5 percent
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� ` Description of Alderwood
� Setting
Landform: Moraines, till plains
�I Parent material: 8asal till with some volcanic ash
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I G2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 8 of 43
� Drainage Report City of Renton
Properties and qualities
Slope: 6 to 95 percent
Depth to restrictive feature: 24 to 40 inches to dense material
Drainage class: Moderately we!!drained
Capacity of the most limiting layer to transmit water (Ksat): Very low to moderately !ow
(0.00 to 0.06 in/hr)
Depth to water fable: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
Percenf 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 unrt: 1 percent
Landform: Depressions
Shalcar
Percent of map unit: 1 percent
Landform: Depressions
AgD—Alderwood gravelly sandy loam, 15 to 30 percent slopes
Map Unit Setting
Elevafion: 50 to 800 feet
Mean annua!precipitafion: 25 to 60 inches
02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 9 of 43
Drainage Report City of Renton
Mean annua!air temperature: 48 to 52 degrees F
Frost-free period: 980 to 220 days
Map Unit Composition
Alderwood and similar soils: 100 percent
Description of Alderwood
Setting
� Landform: Moraines, til!plains
Parent material: Basa/till with some volcanic ash
Properties and qualities
Slope: 15 to 30 percent
Depth to resfrictive feature: 24 fo 40 inches to dense materia!
Drainage c/ass: Moderately well drained
Capacity of the most limiting layer to transmit water (Ksat): Very !ow to moderately !ow
(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.� Low (about 3.6 inches)
Interpretive groups
Land capability (nonrrrigated): 4e
Typical profile
0 to 12 inches: Gravelly sandy loam
12 to 40 inches: Very gravelly sandy loam
40 to 60 inches: Very gravelly sandy loam
C2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 10 of 43
Drainage Report City of Renton
SECTION II
CONDiTIONS AND REQUIREMENTS SUMMARY
The Project must comply with the following Core and Special Requirements:
• C.R. #1 — Discharge at the Natural Location: Runoff from the Site will discharge at
the natural location which is near the Stream located at the northeast corner of the
Site.
• C.R. #2 — Offsite Analysis: Analysis is included in Section III. The Analysis
describes the Site's runoff patterns in detail.
• C.R. #3 — The Project is located in the Level 2 Flow Control area. A detention pond
will provide flow control as required. The Project is required to match durations for
50% of the two-year peak flow up to the full 50-year peak flow. Also match
developed peak discharge rates to predeveloped peak discharge rates for the 2-year
and 10-year return periods (KCSWDM, Sec. 1.2.)
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 the reduced impervious
surface credit 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 overflow 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 facilities will be the responsibility of the City. An Operation and
Maintenance Manual will be 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
finro-year period following posting of the drainage defect and maintenance financial
guarantee.
02013 D. R.STRONG Consulting Engineers Inc. PipePs Bluff Plat Page 11 of 43
Drainage Report City of Renton
• C.R. #8 - The Project is located in the Basic Water Quality Treatment area. A 96-
inch diameter Stormfilter manhole is proposed to meet this requirement.
• 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.
G2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 12 of 43
Drainage Report City of Renton
SECTION III
OFF-SITE ANALYSIS
An offsite Level One Downstream Analysis was prepared by D.R. STRONG Consulting
Engineers Inc. and is included in this Section.
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02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 13 of 43
Drainage Report City of Renton
LEVEL ONE DOWNSTREAM ANALYSIS
for
PIPER'S BLUFF
' Preliminary Plat
1166 Hoquiam Avenue NE, Renton,Washington ��
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! � DRS Project No. 12029
�; Renton File No.
Owner/Applicant
�� WestPac Development, LLC
i 7449 W Mercer Way
Mercer Island, WA 98040
Report Prepared by
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10604 N.E. 38th Place, Suite 232
Kirkland WA 98033
� (425) 827-3063 '�
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Re o rt I II�I
ssue Date
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August 29, 2012
02012 D. R.STRONG Consulting Engineers Inc.
LEVEL ONE DOWNSTREAM ANALYSIS
PIPER'S BLUFF
TABLE OF CONTENTS
' TASK 1 DEFINE AND MAP THE STUDY AREA .........................................................1
TASK 2 RESOURCE REVIEW.....................................................................................5
TASK 3 FIELD INSPECTION .....................................................................................16
Upstream Tributary Area............................................................................................16
General Onsite and Offsite Drainage Description ......................................................16
TASK 4 DRAINAGE SYSTEM DESCRIPTION AND PROBLEM DESCRIPTIONS...17
Drainage System Description.....................................................................................17
DownstreamPath ...................................................................................................17
TASK 5 MITIGATION OF EXISTING OR POTENTIAL PROBLEMS.........................20
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...........................................................................................18
Figure 13 Downstream Table.........................................................................................19
Appendix
AppendixA Photos ........................................................................................................21
��2012 D. R. STRONG Consulting Engineers Inc. Page i of i
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
TASK 1 DEFINE AND MAP THE STUDY AREA
This Offsite Analysis was prepared in accordance with Core Requirement #2, Section
1.2.2 of the 2009 King County Surface Water Design Manual (Manual). The Site is
located at NE 12th St & Hoquiam Ave NE, Renton, Washington. The Project is the
subdivision of four into 30 single family lots.
See Figure 1, Figure 2, and Figure 3for maps of the study area.
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02012 D. R.STRONG Consulting Engineers Inc. Page 1 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
FIGURE 1
VICINITY MAP
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The infoRnation 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 of 23
Level One Downstream Analysis PipePs Bluff Preliminary Plat City of Renton
FIGURE 2
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02012 D.R.STRONG Consulting Engineers Inc. Page 3 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
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FIGURE 3
KING COUNTY IMAP TOPOGRAPHY
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02012 D. R.STRONG Consulting Engineers Inc. Page 4 of 23
Level One Do�vnstream Analysis Piper's Bluff 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.
• Sensitive Areas Folio Maps: See Figures 4-8 for documentation offhe distance
downstream from the proposed project tothe nearest critical areas.lncluded, are
sections of the King County Sensitive Areas Folio which indicate the following:
• Figure 4 Strearns and 100-Year Floodplains and Floodway:There is a
C/ass 4 Stream locafed near the northeasf property corner of the Site.
There are no 100 year floodplains within one mile of the Site aJong the
downstream path.
• Figure 5 Wetlands:There is a Category 2 Wetland located near the �
northeast property corner of the Site.There are mapped Wetlandswithin
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 downstream path. ',
• Figure 7 Landslide Hazard:There are no 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 pafh.
• DNRP Drainage Complaints and Studies:As shown in Figure 90,there are no
; drainage complaints within 1 mile of the Site along the downstream path.
• Road Drainage Problems: None nofed.
• USDA King County Soils Survey: See Figure 11.
' • Wetlands Inventory: Vol. 3South (1990) — The wetland inventory revealed no
� additiona! wetlands within the downsfream path.
I
; • Migrating River Studies: None are applicable to the site.
i �
, Washington State Department of Ecology's latest published Clean Water Act Section
'i 303d list of polluted waters: None listed along the downstream path.
j ` • King County Designated Water Quality Problems: None at this time.
I, ,
i • Adopted Stormwater Compliance Plans: None applicable to this site.
i • Basin Reconnaissance Summary Reports: None available at this time
�
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02012 D. R. STRONG Consulting Engineers Inc. Page 5 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
, i
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FIGURE 4
' STREAMS AND 100-YEAR FLOODPLAINS AND FLOODWAY
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02012 D.R.STRONG Consulting Engineers Inc. Page 6 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
��
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FIGURE 5 �
KING COUNTY �MAP WETLANDS
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02012 D. R.STRONG Consulting Engineers Inc. Page 7 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
FIGURE 6 I
KING COUNTY IMAP EROSION HAZARD AREAS �
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streets f./ streams
llighway SAO Erosi6n
{cont}
02012 D. R.STRONG Consulting Engineers Inc. Page 8 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
FIGURE 7
KING COUNTY IMAP LANDSLIDE HAZARD AREAS
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(cont}
02012 D. R.STRONG Consulting Engineers Inc. Page 9 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
FIGURE 8
KING COUNTY IMAP SEISMIC HAZARD AREAS
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02012 D. R.STRONG Consulting Engineers Inc. Page 10 of 23
Level One Downstream Analysis Pipe�s Bluff Preiiminary Plat City of Renton
FIGURE 9
FEMA - FLOOD INSURANCE RATE MAP
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02012 D.R.STRONG Consulting Engineers Inc_ Page 11 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
FIGURE '10
KING COUNTY IMAP DRAINAGE COMPLAINTS
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02012 D.R.STRONG Consulting Engineers Inc. Page 12 of 23
Level One Downstream Analysis PipePs Biuff Preliminary Plat City of Renton
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AgC—Alderwood gravelly sandy loam, 6 to 15 percent slopes
Map Unit Setting
• Elevation: 50 to 800 feet
o 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
• Parent material: 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 gravefly sandy loam
Minor Components
Norma
• Percent of map unit: 1 percent
• Landform: Depressions
Bellingham
• Percent of map unit: 1 percent
• Landform: Depressions
Seattle
:�2012 D. R. STRONG Consulting Engineers Inc. Page 14 of 23
Level One Dotivnstream Analysis Piper's Bluff Preliminary Plat City of Renton
• 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
AgD—Alderwood gravelly sandy loam, 15 to 30 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: 100 percent
Description of Alderwood
Setting
• Landform: Moraines, till plains
• Parent material: Basal till with some volcanic ash
Properties and qualities
• Slope: 15 to 30 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: Low (about 3.6 inches)
Interpretive groups
• Land capability (nonirrigated): 4e
Typical profile
• 0 to 12 inches: Gravelly sandy loam
• 12 to 40 inches: Very gravelly sandy loam
• 40 to 60 inches: Very gravelly sandy loam
02012 D. R.STRONG Consulting Engineers Inc. Page 15 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
TASK 3 FIELD INSPECTION
UPSTREAM TRIBUTARY AREA
The upstream basin area was evaluated by examining the King County topographic
map (see Figure 1} and by conducting field reconnaissance.
The Site is situated near the top of ahillsidewhich slopes from the southwest to the
northeast. Runoff from Hoquiam Avenue is intercepted by a ditch/ culvert system prior
to entering the Site. Runoff from the parcel to the south of the Site is collected and
conveyed to a private drainage system (currently under construction). Since there is no
offsite area contributing runoff to the Site, there is no upstream tributary area.
GENERAL ONSITE AND OFFSITE DRAINAGE DESCRIPTION
The entire Site slopes at the northeast at2 to 15 percent toward a single Natural
Discharge Pointat the northeast corner of the lot and is intercepted by an onsite
Category 2 Wetland and a Class 4 stream. From here the st�eam conveys runoff
northerly to an offsite Category 2 Wetland. This wetland extends north and flows
through a culvert under Hoquiam Ave NE and encompasses the remainder of the
quarter mile downstream path.
Runoff from the developed Site will becollected and conveyed by a typical catchbasin/
pipe network to a detention vault in the northeast corner of the Site. The vault will
discharge to the onsite stream.
C�2012 D. R. STRONG Consulting Engineers Inc. Page 16 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
TASK 4 DRAINAGE SYSTEIVI DESCRIPTION AND PROBLEM
DESCRIPTIONS
DRAINAGE SYSTEM DESCRIPTION �
The downstream analysis is further illustrated and detailed in the Downstream Map and I
Downstream Table located in Appendix A. The downstream area is located within the ,
Cedar River/ Lake Washingtonwatershed; more specifically the Honey Creek sub basin '
of the May Creekdrainage basin. The downstream area was evaluated by reviewing
available resources, and by conducting a field reconnaissance on May 16, 2012 unde�
overcast conditions.
Downstream Path
Point "A" is the NDA for the entire Site, which is a Class 4Streamlocated at the
northeast corner of the Site (0').
From Point "A" to Point "B" runoff is conveyed northerlyoff of the Site as channel flow
through the stream. The stream channel is well defined in places and poorly defined in
others. The channel varies in size ±1'-10' wide, 0.5'-1.0' deep, with a slope of ±2-8%.
Steady flow was observed(0' - ±260').
At Point "B" runoff enters an offsite wetland. The wetland area quickly becomes over 3'
deep with no obvious flow path. Steady flow was observed entering the wetland
(±260');
From Point "B" to Point "C" runoff travels northwesterly through the wetland area(±260'
— ±1,034').
Point "C" is a 30-inch diameter concrete culvert which diverts runoff under Hoquiam Ave
NE. The inlet was approximately 3/ full of water and debris. Very slow flow was
observed entering the culvert (±1,034' from the Site);
From Point "C" to Point "D" runoff travels westerly as pipe flow through a 30-inch
diameter concrete culvertunder Hoquiam Ave NE with a slope of 1-3%(±1,034' -
±1,064').
Point "D" is the outfall of the 30-inch diameter concrete culvert on the west side of
Hoquiam Ave NE. The outfall was approximately 3/ full of water and debris.Very slow
flow was observed exiting the culvert (±1,064' from the Site).
Point "D" to End; the remainder of the quarter mile downstream path is within a wetland
area. The analysis was terminated at this point.
��2012 D. R.STRONG Consulting Engineers Inc. Page 17 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
FIGURE 12
DOWNSTREAM MAP
02012 D. R.STRONG Consulting Engineers Inc. Page 18 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
�
I ' W
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GRAPHIC SCALE m
0�1+00 200 400 �
.
NE 12TN ST � `� . ` 1 INCH = 200 FT. �
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.� :� z \ \ . . ,..v.�, e,..�n / r `, \ � _���`/-.:' DRAFTED BY.• pR �
� '� DESIGNED BY• NAK
z� PRO,�FCT ENG1N£ER: LRJ
� DA7E.• Oa�2p12
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PRO.ECT NO.: 12029
�. R:\2G12\0\12029\3\Drawings\Plots\PP\Report Figures\61-3DS�IG12.dwg 7/37/2072 9:35:23 AM PDT F7GURE 12
�� COPYRIGHT OO za�z. D.R. STRO.VG CONSULTING ENGNEERS IVC.
FIGURE 13
DOWNSTREAM TABLE
BASIN:Ma Creek
Symbol Drainage Drainage Component Slope Distance Existing Potential Observations of field
Component Description From site Problems Problems inspector
Type, Name, Discharge resource reviewer, or
and Size resident
Type:sheet flow, Constrictions,under capacity,ponding, tributary area, likelihood of problem,
See map swale drainage basin,vegetation,cover, % 1/4 mi=1,320 ft overtopping,flooding, habitat or organism overflow pathways, potential impacts.
Stream,channel, depth,type of sensitive area,volume destruction,scouring,bank sloughing,
pipe, sedimentation,incision,other erosion
Pond;Size:diameter,
surface area
A DISCHARGE TO ONSITE WETLAND O CREEK FLOWS THROUGH THE SITE
AND STREAM
A-B CHANNEL FLOW t1�-1 O�WIDE, 0.5�-1.0�DEEP 2-8 STEADY FLOW OBSERVED.
CHANNEL IS WELL DEFINED IN
SOME AREAS, POORLY DEFINED IN
OTHER AREAS
B STREAM ENTERS WETLAND ±260'
B-C WETLAND 1-4 � MUCH OF WETLAND IS OVER 3'
DEEP
C CULVERT INLET ±1,034� SEDIMENTATION VERY SLOW FLOW WAS
IN CULVERT OBSERVED, INLET±3/a FULL OF
WATER AND DEBRIS,±6�TO FROM
CROWN OF PIPE TO HOQUTAM
AvE N E
C-D PIPE FLOW 30"QJ CONC. 1-3
D CULVERT OUTFALL ±1,064� VERY SLOW FLOW WAS
OBSERVED. WETLAND
CONTINUES WEST FOR OVER 300'
02012 D. R.STRONG Consulting Engineers Inc. Page 19 of 23
Level One Downstream Analysis Piper's Bluff 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 will be collected and released per the Manual's requirements to
accommodate Level 2 Conservation 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:12 0 1 21011 2 0 2 9131DocumentslReportslPreliminarylLevel 1 AnalysislLevel 1 DS 12029.wbk
02012 D.R.STRONG Consulting Engineers Inc. Page 20 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
I� �
APPENDIX A
PHOTOS
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02012 D. R.STRONG Consulting Engineers Inc. Page 21 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton
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02012 D. R.STRONG Consulting Engineers Inc. Page 22 of 23
Level One Downstream Analysis Pipers Bluff Preliminary Plat City of Renton
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�2012 D. R.STRONG Consulting Engineers Inc. Page 23 of 23
Level One Downstream Analysis Piper's Bluff Preliminary Plat City of Renton �
i
I ,_
SECTION IV
�� FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
I
EXISTING SITE HYDROLOGY (PART A)
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.
Area Breakdown
Predeveloped Area
I Till Forest 216966.00 4.981
Impervious 0.00 0.000
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�J2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 14 of 43
Drainage Report City of Renton
PRE-DEVELOPED HOURLY TIME STEP MODELING INPUT:
- -
� Land Use Summary �,�� � �� .�� ��"�`--� :�
� .,.
_
� F_,: - � a i .
Area ?
Till Forest� 4•9S acres
Till Pasture 0.00 acres ',
Till Grass O.QO acres
� Ouiwash Forest O.OU acres
Ouiwash Pasture 0.00 acres
Outwash Grass 0.00 acres
Wetland O.OU acres
- Impervious 0.�� acres
Total
4.98 acres
� Scale Factor : 1.OU Hourly Reduced
Time Series: predev »
Compute Time Series �
Modify User Input I
� File for computed Time Series [.TSF]
:�
�
PRE-DEVELOPED HOURLY TIME STEP MODELING OUTPUT:
Flow 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
0.314 2 2/09/O1 18:00 0.402 1 100.00 0. 990
0. 085 7 1/06/02 3:00 0.314 2 25. 00 0. 960
0.233 4 2/28/03 3: 00 0.241 3 10. 00 0. 900
0. 008 8 3/24/04 20: 00 0.233 4 5. 00 0.800
0. 139 6 1/05/05 8:00 0.204 5 3.00 0. 667
0. 241 3 1/18/06 21:00 0. 139 6 2.00 0.500
0.204 5 11/24/06 4:00 0. 085 7 1.30 0.231
0 . 402 1 1/09/08 9:00 0. 008 8 1. 10 0 .091
Ccm.puted Peaks 0. 372 50. 00 0 . 980
:,2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 15 of 43
Drainage Report City of Renton
FIGURE 5
PREDEVELOPMENT AREA MAP
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02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 16 of 43
Drainage Report City of Renton
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AREA BREAKDOWN , �
TOTAL EXISTING SlTE AREA: 217,369 S.F. (4.990 ACRES) L E G E N D
TOTAL PROJECT DEVELOPMENT AREA: 216966 S.F. (4.981 AC SITE BOUNDARY N � RT H �
� � � � BASIN BOUNDARY
� (lNCL UDES 10,337 S.F.OF SI TE MOD£LED A S TlLL FOREST
DRAFTED BY.� NAK
FRONTAGE IMPROVEMENTS GRAPHIC SCALE G£S/GNED BY.� NAK
ON HOQUTAM A1/E NE AND EXCLUDES 0 30 60 120 PRO,tiCT ENG7NEER: LRJ
1 D,74 D S.F. OF NGPA AREA) `�i� cA re ot.zasota
PkD,IfCT h'O.: 12p29
1 I NCH =60 FT.
�4:\2C12\C\12029\3\G-cvFngs\Plots\Engioeerirg\Repo-: F'g..�re=_\01-3FIG512029.dwg 4/26/2013 4:�1:27 PM PD? FlGURE.' .5
COFYRGHT Q 20'3, D.R. S?ROKG CCKSU'�_-I�� E�dGYEERS INC.
DEVELOPED SITE HYDROLOGY (PART B)
DEVELOPED SITE AREA HYDROLOGY
KCRTS was used to model the developed peak runoff from the Site. The soil types are
unchanged from the pre-developed conditions. 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.
Area Breakdown
Developed Area
Lot Area 132509 3.04
Impervious 86988 2.00
Pervious 45521 1.05
� ROW, Tract"A","C" &"D" 84457 1.94
Impervious 51061 1.17
Pervious 33396 0.77
Totals
Impervious 138049 3.17
Pervious 78917 1.81
(Till Grass)
G2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 17 of 43
Drainage Report City of Renton
DEVELOPED HOURLY TIME STEP MODELING INPUT:
-- - - -
. . , " �.i4 r`','�`�f,g`�z`�y�g4�'.s�'.� ..
:� Land Use Summary � ���� ,� �-, � � �"' -
.r_
� , ..
. �
_ �_ �_�.,�,.. ...��....:� ,.:;
�Area — ? °
Till Forest 0.00 acres
;'
Till Pasture 0.00 acres
Till Grass 1•S1 acres
Outwash Forest 0.00 acres
Ouiwash Pasture 0.00 acres
Qutwrash Grass 0.00 acres
Wetland 0.00 acres
Imperwious 3.17 acres
Total
4.98 acres -
� Scale Fac#or : 1.UU Haurly Reduced
3
� Time Series: DEV » _
� Compute Time Series LL
i
Modiiy User Input I
File for computed Time Series [.TSFJ
DEVELOPED HOURLY TIME STEP MODELING OUTPUT:
Flow Frequency Analysis
Time Series File:dev.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. 928 6 2/09/O1 2: 00 1.88 1 100.00 0. 9°0 ;
0.757 8 1/05/02 16:00 1. 19 2 25.00 0. 960
1.12 3 2/27/03 7:00 1 . 12 3 10.00 0. 900 '
0.820 7 8/26/04 2:00 0. 987 4 5.00 0. 800 '
0. 987 4 10/28/04 16:00 0. 985 5 3.00 0. 667 I,
0. 985 5 1/18/06 16:00 0. 928 6 2 . 00 0.500 ',
1. 19 2 10/26/06 0:00 0. 820 7 1. 30 0.231 '
1.88 1 1/09/08 6:00 0.757 8 1. 10 0. 091
Computed Peaks 1. 65 50.00 0 . 980 �
02013 D. R.STRONG Consultin En ineers Inc. Pi er's Bluff Plat Pa e 18 of 43
9 9 P 9
Drainage Report City of Renton
I
FIGURE 6
POST DEVELOPMENT AREA MAP '
�?2013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 19 of 43
Drainage Report City of Renton
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PERFORMANCE STANDARDS (PART C)
The Project is located in the Level 2 Flow Control area. The Level 2 performance
requires that the developed condition's durations must match the predeveloped
durations ranging from 50% of the two-year peak flow up to the full 50-year peak flow
and also match developed peak discharge rates to predeveloped peak discharge rates
for the 2-year and 10-year return periods (KCSWDM, Sec. 1.2. The Project was
evaluated for onsite infiltration and dispersion of roof downspout runoff. The lots have
insufficient space to allow for infiltration or dispersion of roof runoff.
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. 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).
FLOW CONTROL SYSTEM (PART D)
The Site will utilize a detention pond meeting the Level 2 Flow Control Criteria. The
King County Runoff Time Series (KCRTS) software was used to size the detention
facility. The detention vault 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).
The reduced Impervious Surface Credit BMP as described in Appendix C, Section C.2.9
of the KCSWDM will be utilized for the Project. The maximum impervious surface
allowed per zoning code for the total lot area (3.042 ac) is 2.281 ac using the maximum
allowable build-out rate of 75% or 4,000 s.f. whichever is less. Lots 1-28 inclusive shall
be restricted to a maximum impervious coverage equal to 65% of each lot area (1.997
ac). A restricted footprint covenant shall be recorded on the face of the final plat map.
This satisfies the flow control BMP requirements in Section 1.2.3.3 and 5.2 of the 2009
KCSWDM.
I
;
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i
j �
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r.�� f . � � s:_=
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02013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat
Drainage Report vuy vi i�cnwi�
i '
�
i
' LOT NO. LOTAREA IMPERVIOUS AREA PER CODE IMPERVIOUS FOOTPRINT
_ _ _ _
_ _
' 1 5308 3981 3450
I � i .. 2 _. 4566 -.... __ 3425 _ _ 2968 3
.._— - - --`4
�, ' 3 � 4566 3425 ; 3543 ;
__ __�__.__.._ _ _..�� -__ -----_.._�_.�
I ` 4 ;� 4566 3425 3543 �
_.. -----_ _.� �_.�_- --- _ _ _. _ -- �
; 5 4566 3425 2968 �
� __.__. __-___ __ ._ ----.
__ ___.__
; 6 : 4566 3425 2968
,�_._ __�_. _ --- .._—�
; 7 _� 4566 � 3425 2968 � 3
� __ _ . ..___ _ - _ . _. __.�_s3
8 4988 3741 3242 �
�._ __te...._ __ �
9 � 4551 3413 2958
_____ __ __ ._ _
10 ; 5197 3898 3378
_ _��_ ��_ � _ �
; 11 ! 4562 3422 _ � 2965 �
. . ..�_.�.._... . . .. .. ._ _. . . . . _ � . ..... . ___._._�..y
12 ;� 4562 3422 2965
_ _ _ __ __ __ __._��
` 13 � 4562 3422 2965
.�. �._. _ _ _..��
14 4562 3422 2965 ;
_ _ �_.__ __ _ _ -----_. ------ -- - ;
15 ; 4562 3422 2965 `
;�.. _ __. _ ----- ---- _ __�_._____.�
16 � 4562 3422 2965 �
__._ _ .- - ___�—��.i
17 i 5309 3982 3451
_ __ __. _ _
18 : i----- 5223 _.__, 3917 � 3395 -_
_ ..____.
_ �
19 '_ 4502 ~ 3377 � 2926 �
_ _ _ __ _ .�
20 j 4501 '• 3376 2926
_ �._._.__ ___ __.__ _._ __ _...� __
21 � 4500 3375 2925
_ _-_, _- - _.__ .� __
22 ; 4500 3375 2925 ;
_ _. _ _ ... �..__._ _i_ _-
23 � 4500 S 3375 2925
___ _ _..���_.__ _. _ -- -
24 i 4500 � 3375 2925
,� _ - -_ __ _ _- -- _- � .. __ _..
25 4500 3375 2925
.�_. _ --_ ___ ----- _.__ _ ._ __----__�_�
26_ .; - 4979 3734 3236 �
_...._, �
27 � 4958 � 3719 3223 �
__.. _ _ _ . _
28* 5725 4294 3428
*PER SECTION 5.2.1.1 OF THE KCSWDM 2009, RESTRICTED FOOTPRINT IS ESTABLISHED BY '
__ _
--
RESTRI CTI N G TH E FOOTP RI NT TO 4,000 SF LESS AN AREA EQUAL TO 10%OF TH E LOT AREA.
�;2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 21 of 43
Drainage Report City of Renton
FLOW CONTROL FACILITY DESIGN OUTPUT
�etent�or/Detention Facility
Type of Facility: Detention Pond
Side Slope: 3.00 H:_���
Pond Bottom Length: 33.00 f�
Pond Bottom Width: 16.00 ft
Pond Bottom Area: 528. sc. ft
Top Area at 1 ft. FB: 13038. sq. ft
0.299 acres
Effective Storage Depth: 14 .0� ft
Stage 0 Elevation: 410.00 �t
Storage Volume: 69132. cu. ft
1.587 ac-ft
Riser Head: 14.00 ft
Riser Diameter: 18.00 inches
Number of orifices: 3
Full Head Pipe
Orifice # Height Diameter Discharge Diameter
(ft) (in) (CFS) (in)
1 0.00 0.88 0. 079
2 10.00 1.50 0. 122 4 . 0 �
3 10.70 "-.�0 �. i;9? 4 . 0
Top Notch Weir: None
Outflow Ratina Curve: No:�e
S�age Elevation Storage Discharge Percolation Surf Area
(ft) (ft) (cu. ft) (ac-ft) (cfs) (cfs) (sq. ft;
0.00 410.00 0. 0.000 0.000 0.00 528 .
0.01 410.01 5. 0.000 0.002 0.00 531.
0.02 410.02 11. 0.000 0.003 0.00 534 .
0.03 410.03 16. 0.000 0.003 0.00 537.
0.04 410.04 21. 0.000 0.004 0.00 540.
0.05 410.05 27. 0.001 0.005 0.00 543.
0.06 410.06 32. 0.001 0.005 0.00 546.
0.07 410.07 38. 0.001 0.006 0.00 599.
0.35 410.35 203. 0.005 0.012 0.00 635.
0. 62 410.62 387. 0.009 0.017 0.00 724 .
0. 90 410.90 603. 0.014 0.020 0.00 822 .
1.17 411.17 838. 0.019 0.023 0.00 921.
1.45 411.45 1111. 0.026 0.025 0.00 1030.
1.72 411.72 1404. 0.032 0.028 0.00 1140.
1. 99 411.99 1727. 0.040 0.030 0.00 1256.
2.27 412.27 2096. 0.048 0.032 0.00 1381.
2.54 412.54 2486. 0.057 0.033 0.00 1507.
2.82 412.82 2927. 0.067 0.035 0.00 1643.
3.09 413.09 3389. 0.078 0.037 0.00 1780.
3.37 413.37 3908. 0.090 0.039 0.00 1928 .
3. 64 413.64 4448. 0.102 0.040 0.00 2075.
3. 92 413.92 5052. 0.116 0.042 0.00 2234 .
4.19 414.19 5676. 0.130 0.043 0.00 2392 .
4.47 414.47 6369. 0.146 0.044 0.00 2561 .
4.74 414.74 7083. 0.163 0.0�6 0.00 2730.
02013 D. R.STRONG Consulting Engineers Inc. PipePs Bluff Plat Page 22 of 43
Drainage Report City of Renton
5. G1 �1�.01 �899 . 0. "�_80 ��. 047 0.�0 29�5.
5.29 415.2� �683. 0. 199 0.048 0.00 3091 .
5.56 415.56 9543. 0.219 0.050 0.00 3276.
�.84 415. 84 10487. 0.241 0.051 0.00 3473.
'o. 11 416.11 11451. 0.263 0.052 0.00 3668.
6. 39 416.39 12507. 0.287 0.053 0.00 3877.
6. 66 416. 66 13582. 0.312 0.054 0.00 4083. '
6. 94 416. 94 14755. 0.339 0.055 0.00 4302.
i .21 417.21 15946. 0.366 0.056 0.00 4519. '�
7.49 417.49 17244. 0.396 0.057 0.00 4750.
7.76 417.76 18557. 0.426 0.058 0.00 4977.
8.03 418.03 19932. 0.458 0. 060 0.00 5210.
8.31 418.31 21425. 0.492 0.061 0.00 5457.
8.58 418.58 22931. 0.526 0.062 0.00 5701.
8.86 418.86 24564. 0.564 0.063 0.00 5959.
9. 13 419.13 26207. 0.602 0.063 0.00 6213.
9.91 419.41 27984. 0.642 0.064 0.00 6482.
9.68 419. 68 29770. 0. 683 0.065 0.00 6747.
9. 96 419.96 31698. 0.728 0.066 0.00 7027.
10.00 420. 00 31980. 0.734 0.066 0.00 7068.
10.02 420.02 32122. 0.737 0.067 0.00 7088.
10.03 420.03 32192. 0.739 0.068 0. 00 7098.
10.05 420.05 32335. 0.742 0.071 0.00 7119.
10.06 420.06 32406. 0.744 0.074 0.00 7129.
10.08 420.08 32549. 0.747 0.078 0.00 7149.
i0.09 420.09 32620. 0.749 0.083 0.00 7160.
10.11 420.11 32764. 0.752 0.087 0.00 7180.
10.12 420.12 32835. 0.759 0.088 0.00 7190.
10.40 420.40 34889. 0.801 0.106 0.00 7479.
10. 67 420. 67 36947. 0.848 0.119 0.00 7764.
10.70 420.70 37180. 0.854 0.120 0.00 7795.
10.71 420.71 37258. 0.855 0.121 0.00 7806.
10.73 420.73 37414. 0.859 0.122 0.00 7827.
10.74 420.74 37493. 0.861 0.125 0.00 7838.
10.76 420.76 37650. 0.864 0.128 0.00 7859.
10.77 420.77 37728. 0.866 0.133 0.00 7870.
"-0.79 420.79 37886. 0.870 0.138 0.00 7892.
10.80 420.80 37965. 0.872 0.141 0.00 7902.
10.82 420.82 38123. 0.875 0. 142 0.00 7924.
11.09 421.09 40302. 0.925 0. 167 0.00 8216.
11.37 421.37 42646. 0.979 0.185 0.00 8525.
11. 64 421. 64 44988. 1.033 0.201 0.00 8828.
11. 91 421 . 91 47413. 1.088 0.216 0.00 9136.
12. 19 422. 19 50017. 1.198 0.228 0.00 9461.
12. 46 422. 46 52614. 1.208 0.241 0.00 9780.
12.74 422.74 55400. 1.272 0.252 0.00 10117.
13.01 423.01 58175. 1.336 0.263 0.00 10446.
i3.29 423.29 61149. 1.404 0.273 0.00 10794 .
13.56 423.56 64109. 1.472 0.282 0.00 11134 .
13.84 423.84 67277. 1.544 0.292 0.00 11493.
14.00 424 .00 69132. 1.587 0.297 0.00 11700.
14. 10 424 .10 70309. 1.614 0.762 0.00 11831.
14 .20 424 .20 71498. 1.641 1. 610 0.00 11962.
14 . 30 424 .30 72701. 1.669 2.710 0.00 12094 .
14 .40 424.40 73917. 1.697 4.010 0.00 12227.
14 .50 424.50 75146. 1.725 5.480 0.00 12360.
14 . 60 424 .60 76389. 1.754 6. 910 0.00 12494 .
�2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 23 of 43
Drainage Report City of Renton
i
14 .70 �24 .70 77645. 1.782 7.440 0.00 12629.
14.80 424 .80 78915. 1. 812 7. 930 0.00 12765.
14. 90 424.90 80198. 1. 841 8.400 0.00 12901.
15.00 425.00 81495. 1.871 8.840 0.00 13038.
15.10 425.10 82806. 1. 901 9.260 0.00 13176.
15.20 425.20 84130. 1. 931 9. 660 0.00 13314 .
15.30 425.30 85469. 1. 962 10.090 0.00 13453.
15.40 425.40 86821. 1.993 10.910 0.00 13593.
15.50 425.50 88187. 2. 025 10.760 0.00 13734 .
15.60 425.60 89568. 2.056 11.110 0.00 13875.
15.70 425.70 90962. 2.088 11.440 0.00 1401?.
15.80 425.80 92371. 2. 121 11.770 0.00 14160.
Hyd Inflow Outflow Peak Storaae
Target Calc Stage Elev (Cu-Ft) (Ac-Ft)
1 1.88 ******* 0.28 13.49 423.49 63386. 1. 455
2 0. 93 0.31 0.25 12.72 422.72 55199. 1.267 Z r, y l•
3 1. 12 ******* 0.22 11. 94 421. 94 47731. 1.096
4 0. 93 ******* 0.22 11.94 421.94 47716. 1.095
5 0.99 ******* 0.16 11.05 421.05 39968. 0. 918
6 0.58 ******* 0.10 10.23 420.23 33669. 0.773
7 0.76 ******* 0.06 9.39 419.39 27883. 0. 640
8 0.82 ******* 0.06 8.21 418 .2? 20902 . �. 48�
----------------------------------
Route Time Series thro�agh Facili�y
Inflow Time Series File:dev.ts=
Outflow Time Series File:rdou�
Inflow/Outflow Analysis
Peak Inflow Discharge: 1. 88 CFS a� 6:OC on Ja-� 9 in Year 8
Peak Outflow Discharge: 0.280 CFS at i4 :00 on Jan 9 i~� Year �
Peak Reservoir Stage: 13. 49 Ft
Peak Reservoir Elev: 423.49 Ft
Peak Reservoir Storage: 63386. Cu-Ft
. 1. 455 Ac-Ft
�'low Frequency Analysis
Time Series File:rdout.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) (ft) Period
0.251 2 2/09/O1 21:00 0.280 13.49 1 100.00 0. 990
0.064 7 1/07/02 4:00 0.251 12.72 2 25.00 0. 960
0.217 3 3/06/03 22:00 0.217 11. 94 3 10.00 0. 900
0.061 8 8/26/04 7:00 0.217 11. 94 4 5. 00 0.800
0.095 6 1/08/05 3:00 0.163 11.05 5 3. 00 0.667
0. 163 5 1/19/06 0:00 0.095 10.23 6 2.00 0.500
0.217 4 11/24/06 8:00 0.064 9.42 7 1.30 0.231
0.280 1 1/09/0�? i9 :00 0.061 8.21 8 1. 10 0.091
. _ , �
s2013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 24 of 43
Drainage Report City of Renton
I
il
Flow Duration from Time Series File:rdout.tsf
Cutoff Count Frequency CDF Exceedence Probability
CFS o o %
0.004 37253 60.752 60.752 39.248 0.392E+00
0.011 2181 3.557 64.309 35. 691 0.357E+00
0.018 2049 3.341 67. 650 32.350 0.323E+00
0.025 2774 4 .524 72.174 27.826 0.278E+00
0.032 2761 4.503 76. 676 23.324 0.233E+00
0.039 3214 5.241 81. 918 18.082 0.181E+00
0.046 3815 6.221 88. 139 11.861 0.119E+00
C.053 2842 4.635 92.774 7.226 0.723E-01
0.060 1950 3.180 95. 954 4.046 0.405E-01
0.067 1952 3.183 99.137 0.863 0.863E-02
0.074 34 0.055 99.193 0.807 0.807E-02
0.081 20 0.033 99.225 0.775 0.775E-02
0.088 43 0.070 99.296 0.705 0.705E-02
0.095 57 0.093 99.388 0. 612 0. 612E-02
0. 102 44 0.072 99.460 0.540 0.540E-02
0. 109 51 0.083 99.543 0.457 0.957E-02
0. 116 51 0.083 99.627 0.373 0.373E-02
0.123 34 0.055 99. 682 0.318 0.318E-02
0.130 9 0.015 99.697 0.303 0.303E-02
0.137 6 0.010 99.706 0.294 0.294E-02
0.145 10 0.016 99.723 0.277 0.277E-02
�.152 12 0.020 99.742 0.258 0.258E-02
0.159 19 0.031 99.773 0.227 0.227E-C2
�.166 19 0.031 99.804 0.196 0.196E-02
0.173 15 0.024 99.829 0.171 0.171E-02
0.180 14 0.023 99.852 0.148 0.148E-02
0.187 7 0.011 99.863 0.137 0. 137E-02
0.194 12 0.020 99.883 0.117 0.117E-02
0.201 9 0.015 99.897 0.103 0.103E-02
0.208 10 0.016 99. 914 0.086 0.864E-03
0.215 10 0.016 99. 930 0.070 0.701E-03
0.222 16 0.026 99. 956 0.044 0.440E-03
0.229 10 0.016 99. 972 0.028 0.277E-03
�.236 4 0.007 99. 979 0.021 0.212E-03
0.243 4 0.007 99. 985 0.015 0.147E-03
0.250 6 0.010 99. 995 0.005 0.489E-04
Duration Comparison Anaylsis
Base File: predev.tsf
New File: rdout.tsf
Cu:off Units: Discharge in CFS
-----Fraction of Time----- ---------Check of Tolerance-------
Ci'�o�i Base New oChange Probability Base New oChange
0.069 I 0. 94E-02 0.83E-02 -11. 6 � 0.94E-02 0.069 0.066 -4 . 5
0.088 � 0. 62E-02 0.70E-02 13.1 I 0. 62E-02 0.088 0.095 7. 4
0.107 � 0.49E-02 0.48E-02 -1.3 � 0.49E-02 0. 107 0.107 -0.3
0.126 � 0.37E-02 0.31E-02 -16.4 � 0.37E-02 0. 126 0.117 -7.0
0.145 � 0.28E-02 0.28E-02 -2.3 I 0.28E-02 0.145 0.142 -1. 6
0.163 I 0.22E-02 0.21E-02 -7.4 I 0.22E-02 0.163 0.160 -1.8
0.182 � 0.15E-02 0.15E-02 -l.l � 0.15E-02 0.182 0.182 -0.3
0.201 � O.10E-02 O.10E-02 1. 6 I O.10E-02 0.201 0.202 0. 6
0.220 � 0. 62E-03 0.49E-03 -21. 1 � 0.62E-03 0.220 0.217 -1.5
0.239 I 0.34E-03 0.18E-03 -47.6 � 0.34E-03 0.239 0.226 -5.2
0.257 � 0.21E-03 O.00E+00 -100.0 � 0.21E-03 0.257 0.238 -7.5
��2013 D. R.STRONG Consulting Engineers Inc. PipePs Bluff Plat Page 25 of 43
Drainage Report City of Renton
G.276 I 0. 16E-03 O.00E+00 -100.0 � 0. 16E-03 0.276 0.243 -12. 1
�.295 I 0.11E-03 O.00E+00 -100.0 I 0.11E-03 0.295 0.246 -16.5
0.314 I 0.16E-04 O.00E+00 -100.0 I 0.16E-04 0.314 0.251 -19. 9
h7aximum positive excursion = 0.007 cfs ( 8. 60)
occurring at 0.081 cfs on the Base Data:predev.tsf
and at 0.088 cfs on the New Data:rdout.tsf
Maximum negative excursion = 0.063 cfs (-19. 9°) �'
occurring at 0.314 cfs on the Base Data:predev.tsf
and at 0.251 cfs on the New Data:rdout.tsf
---------------------------------- '
�oute Time Series through Facility
=nflow Time Series File:dev.tsf
�utflow Time Series F' ' �: r�,�: :-
=rflow/Outflow Analysi
Peak Inflow Discha- : . :
�eak Outflow Discharge: U.2'o0 CFS at -�4 : �u on �an 9 in Yea-
Peak Reservoir Stage: 13.49 Ft
?eak Reservoir Elev: 423.49 Ft
_e�:� Reservoir Storage: 63386. Cu-=t
. 1.455 P_c-F
Flow Frequency Analys-s
Time Series File:rdout.tsf
?roject Location:Sea-T�-�
---Annual Peak Flow Rates�--- Fl_.>: �~ -
-- , _ '��� ---�!��i� --
Flow Rate Rank Time of reak - - ?ea�s - - �an;� Return Pro�
(CFS) (CFS) (ft) Period
0.251 2 2/09/O1 21:00 0.280 13.49 1 100.00 0. 9°G
0.064 7 1/07/02 4:00 0.251 12.72 2 25.00 0.96�
0.217 3 3/06/03 22:00 0.217 11. 94 3 10.00 0.900
0.061 8 8/26/04 7:00 0.217 11. 94 4 5.00 0.800
0.095 6 1/08/05 3:00 0. 163 11.05 5 3.00 0. 667
0.163 5 1/19/06 0:00 0.095 10.23 6 2.00 0.500
0.217 4 11/24/06 8:00 0.064 9.42 7 1.30 0.231
0.280 1 1/09/08 14 :00 0.061 8.21 8 1.10 0.091
Ccmputed Peaks 0.270 13.21 50. 0� 0, ��0
Flow Duration from Time Series File:rdout.tsi
Cutoff Count Frequency CDF Exceedence ProbGbility
CFS ° ° ° -
0 0 �
0.004 37253 60.752 60.752 39.248 0.392E+00
0.011 2181 3.557 64.309 35. 691 0.357E+00
0.018 2049 3.341 67.650 32.350 0.323E+00
0.025 2774 4.524 72.174 27.826 0.278E+00
0.032 2761 4.503 76.676 23.324 0.233E+00
0.039 3214 5.241 81. 918 18.082 0.181E+00
0.046 3815 6.221 88.139 11.861 0.119E+00
0.053 2842 4.635 92.774 7.226 0.723E-01
0.060 1950 3.180 95.954 4.046 0.405E-01
0.067 1952 3. 183 99.137 0.863 0.863E-02
0.074 34 0.055 99.193 0.807 0.807E-02
0.081 20 0.033 99.225 0.775 0.775E-02
��2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 26 of 43
Drainage Report City of Renton
0. 088 43 0.070 99.296 0.705 0.705E-02
0.095 57 0.093 99.388 0.612 0.612E-02
0. 102 44 0.072 99.460 0.540 0.540E-`i2
0. 109 51 0.083 99.543 0.457 0.457E-02
0.116 51 0.083 99. 627 0.373 0.373E-02
0. 123 34 0.055 99.682 0.318 0.318E-02
0. 130 9 0.015 99.697 0.303 0.303E-C2
0. 137 6 0.010 99.706 0.294 0.294E-C2
0. 145 10 0.016 99.723 0.277 0.277E-��
0. 152 12 0.020 99.742 0.258 0.258E-02
0.159 19 0.031 99.773 0.227 0.227E-02
0.166 19 0.031 99.804 0.196 0.196E-02
0. 173 15 0.024 99.829 0.171 0.171E-G2
0. 180 14 0.023 99.852 0.148 0.198E-C2
0. 187 7 0.011 99.863 0.137 0.137E-�2
0.194 12 0.020 99.883 0.117 0.117E-02
0.201 9 0.015 99.897 0.103 0.103E-02
0.208 10 0.016 99.914 0.086 0.864E-G3
� 0.215 10 0.016 99.930 0.070 0.701E-03
0.222 16 0.026 99.956 0.044 0.440E-�3
0.229 10 0.016 99.972 0.028 0.277E-Oj
0.236 4 0.007 99.979 0.021 0.212E-G3
0.243 4 0.007 99. 9R5 �. 0�5 0. 14?_-03
0.250 6 0.010 99.
� DURATION ANALYSIS
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Probabi�iry 6c.eedence
C�2013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 27 of 43
Drainage Report City of Renton
f ' .
I
WATER QUALITY TREATMENT SYSTEM (PART E)
_ The Project is located in the Basic Water Quality Treatment area. The treatment goal is
80% removal of total suspend solids for a typical rainfall year, assuming typical pollutant
concentrations in urban runoff.
A 96-inch diameter Stormfilter manhole with (13) 18-inch cartridges will will provide
0.22 cfs of treatment flow rate. Stormfilter final sizing per CONTECH Stormwater
Solutions, Inc is included in Section X.
G�2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 28 of 43
Drainage Report City of Renton
FIGURE 7
DETENTION & WATER QUALITY FACILITY DETAILS
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C�2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 29 of 43
Drainage Report City of Renton
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Determining Number of
C%.►=NTECH Cartridges for Systems
ENGINEERED SOLUTIONS Downstream of Detention
CONTECH Stormwater Solutions Inc. Engineer: JHR
Date 618/2012
Site Information
Project Name Hazen
Project State Washington
Project Location Renton
Drainage Area, Ad 5.06 ac
Impervious Area,Ai 3.65 ac
Pervious Area,Ap 1.41
% Impervious 72% �
Runoff Coefficient, Rc 0.70
Upstream Detention System �
Peak release rate from detention, Qrelease peak 1.29 cfs
Treatment release rate from detention, Q��ease treai 0.09 cfs
Detention pretreatment credit 50%
(from removal efficiency calcs)
Mass loading calculations
Mean Annual Rainfall, P 36 in
Agency required % removal 80%
Percent Runoff Capture 90%
Mean Annual Runoff,Vt 416,111 ft'
Event Mean Concentration of Pollutant, EMC 60 mg/l
Annual Mass Load, Mtota� 1557.68 Ibs
Filter System
Filtration brand StormFilter
Cartridge height 18 in
Specific Flow Rate 1.0 gpm/ft2
Number of cartridges-mass loading
Mass removed by pretreatment system, MP� 778.84 Ibs
Mass load to filters after pretreatment, MPa�� 778.84 Ibs
Estimate the required filter efficiency, Efi�ter 0.60
Mass to be captured by filters, Mfner 467.30 Ibs
Allowable Cartridge Flow rate, Q�rt 7.50
Mass load per cartridge, Mcart(Ibs) 36.00 Ibs
Number of Cartridges required, Nmass 13
Treatment Capacity 0.22 cfs
Determine Critical Sizing Value
Number of Cartridges using Q�,ease<<ear, Nflo,,,, 6
Method to Use: MASS-LOADING
SUMMARY
Treatment Flow Rate, cfs 0.22
Cartridge Flow Rate, gpm 7.5
Number of Cartridges 13
1 of 1
�
�
CONTRACTOR TO GROUT 70 � W
FINISHED GRADE 2
GRADE RING/RISERS � y �
� STORMFIL7ER DES/GN NOTES W �
GRADE R7NG/RISERS � i N
STORA-fFlLTER TREATI.fENTCAPACITY IS A FUNCTION OF THE CARTRIOGE SELECTION AND THE NUMBER OF CARTRIOGES. TN.E C9 C'1
STANDARD MANNOLE STYLF !S SHOWN W1TN TN£ MAXIMUM NUMBER OF CARTRJDGES (14). ✓OLUMf SYST£A�f IS ALSO Q � , � �
' LVAJLABLE WITH MAXlk1UM 14 CARTRIDGES. � j °� � �
i �%.�� ¢96"'MANHOLE STORMFILTER PEAK HYDRAUUC CAPAClTY IS 1.8 CFS. IF 7NE SITE CONDITIONS EXCfEO 1.8 CFS AN V� t� "� Q
�
UPSTREAM BYPASS STRUCTURE IS Rf0U1R£D. � � � � �
• _ ' I O U � � y�
� � : , " . LARTRIDG£ SELECTION a
CARTR�OG£ HEIGHT 27" )8'" LOW OROP � '`
( �1 RECdMM�4'JcD NYURAULIC DROP (H 3.05" 2.3' 1.B' K � �
FCOATABLES SPECIFlC FLOW Rti7E m sf 2 pm/ft 1 pm /t 2 pm (t 1 pm/lt 2 pm/ff 1 pm/ft � W `�
BAFFLE CARTRIGGE FLOW RATE m 22.5 T 1.25 15 7.5 10 5 � 2 �
� O W �
� �� S1TE SPEC/F1C � '
2� DATA REQU/REMENTS
ti
4i — S7RUCTURE ID *
o�� �e \ WATER OUAL7TY FL0'r�'R�;7� �cls` 0.090
78" !NL£T PIPE �?� ? �-y � � PEAK FLOW RA7E cfs 1.29
c�W W _x x� R£7URN PERlOD Or" PEAK FLOW s 100
j�= - ---:�r.z-�> , OF CARTRlDGES REOUJRED 13
Q?o ~ '� � � CARTRIOGE FLOW RATE 7.5
a= �C�YNTECH''"�
� �`,o I MED1A TYPE CSF, PfRLlTE, ZPG, GAC, PHS z
i 2 i' - _ �I � i
` � PJPE DATA: l.E. MATERIAL DIAMETER
IP1LfT PIPE 1 470.00 LCPE 18-INCNES
. � � _ �3" INLET PIPE 2 s s
OUTLET PlPE 407.70 LCPE 18-INCHES
FIL TER CARTRIOG£ —� ,.
RIM ELEVATIDN
OUTLET SUMP
FLO'N K!T ANT1-FLOTATION BALLAST W/DTN HEIGHT
, HOP� rs" ourcEr RrsER FRAMEAND COVER `
NOTES/SPEClAL REOUlREMENTS:
SECTION A A (DlA�rEN R SVARI�S}
N.L S. • PER ENGiNEER CF RECORD
. � � lll O
• GENERAL NOTES: � Q � �
OUTLET 1. CONTECH TO PROVlDE ALL MATERiALS UNLfSS NOT["D OTHfRW15E. I� Z �
SUMP 2. O/A�ENSIDNS MARKfO WlTH () AR£ REFERENCE D/MENS/ONS. ACTUAL DlMENSlONS MAY VARY. � W �J Z
, �. FOR S1TE SPEClFIC ORAWTNGS W/7H DfTAILED VAlJLT OIA�fENS10NS AND Wf1GHTS, PLEASE CONTACT YOUR CONTEC,Y � O ¢ _
ENGINEER£D SOLUTIONS LLC REPRESENTATlVE. www.contechES.com
I� 4. STORMFlLT£R WATER OUALITY S7RUCTUR£ SHACL B£IN ACCORDAMCf W1TH ALL DES/GN DATA AND INFORMATfON
� � I � C O N T A 1 N£D 1 N T H I S O R A W 1 N G, y W Q �
A �{ 5, STRUC7URf SHALL MEET AASHTO N,S20 LOAD RATING, ASSUMlNG EAR7H COVER OF 0' – 5' AND GROUNOWATER � � �
ELEVATlON AT, OR B£LOW, THE OUTLET PIPE 1NVERT ELEVATION. ENGINE£R OF R£CORD TO CONFIRM ACTUAL � l� � Z
• �� �_ �o _ GROUNDWAT£R ELEVATION. CASTINGS SHALL M££T AASH70 �A306 AND BE CAST WlTN TyE CONTECH LOGO. �
i o E. FILT£R CARTRlDGES SHALL 8E MEDIA–FlLLED, PASS/Vf, S/PHON AC7UA7EQ RADlAL FLOIY, AND SELF CLEANING. ^ � � O
� i I— ' ' � ' RADIAL MEDJA DEPTH SHALL B£ 7–lNCHES. FILTER MEDIA CONTACT TlME SHALL BE AT L£AST 39 SECONDS. ` � Z �
l8" lNLE7 18" 0lITLET i. S P E C I F I C F L O W R A T E 1 S E O U A L T O T H E F I L T E R T R E A T M F N 7 C A P A C 1 7 Y (gpm J D l N D E D B Y T y F F 1 L T E R C O N T A C T SL'�FA�� I� �D W
— � � AREA (sq 1t). � � � �
FLOW �\;L _ S;J_ o �
,� INSTALLA TION NOTES:
' � � � 7. ANY SUB–BASE, BACKFILL D£PT,'!, ti,^J� GR AId7!–FLOiA710PJ FR0�.4'SIG�VS AP,E SliE–SPECIrIC G���G�`i CGPJS,'U£,4A71C`:S
96" I.D. MANHOLE �
STRIJCRJRE AND SHALL B£ SPEClFlEO BY ENGlNEER OF RECORD.
2. CONTRACTOR TO PROVIDE EQUIP�b1ENT WJTH SUFFIGEN7 LIF77NG AND REACH CAPACfTY TO LIFT AND SET 7HE
STORMFILTER STRUCTURE (LIFANG C�UTCNES PRaV1DE0).
(114) O.D. 3. CONTRACTOR TO INSTALL JDlNT SEALANT BE7WEEN ALL STRUCTURE SECTIONS AND ASSEMBLE STRUCTURE.
4. CONTRACTOR TO PROVIDE, INSTALL, AND GROUT INLET PIPE(S).
5. CONTRAC70R TO PR01/lDE AMD lNSTALL CONN£C70R TD THE OUTL£T RISER S7UB. STOh'MFILTER EOUIPPfD W'T'ri A
TOP SLAB ACCESS DUAL DIAM£TER HOPE OU7LET STUB AND SAND COLLAR. !F OUTLET PlPE 1S LARGER TI-'AN 8 INCHfS, CONTRACTOR 70
' SE£ FRAM£ AND COVfR REMDUE 7HE 8 1NCH OUTLET STUB AT MOLDED lN CUT LIN£. CDUPLING BY FERNCO OR EQUAL AND PROVIDED BY
DETAIL CONTRACTOR.
� 6. CONTF,ACTOR TD TAKE APPRO?RlATE McASJR£S TO PROTECT CA,4TRIDGES FROM CO1JS7i'UCT�ON–P,ELAT£D EROSION
PLAN V/EW RUNCiF.
! STAND?.RD OJ7LET RISER
� � �I FLOVSTIT• 43A
STORMFIL TER DETAILS
_`�C NTEC H• � D£SI ED BY: NAK
ENGINEERED SOLlJT10N5 LLC
PRAECT ENGINf£R: LRJ
DATE: 01.29.?013
PRO,.£CT NO.: 12019
a:�,aars�,.��,.�saz91-'10.0.;� a�o�slc^;��^<,n DRAWlNC: 1
gs�, '�'�.'epw.' -;g_resl5ra�m�/er Jer�:�s��g 4��6/�L:7 �-J5:7]FN 7�i
� CO'YRIG^T C�2C13, p,R. STRONG C��.SJLT`1G E"JGI�=EBS VC. SH££T.• �
SECTION V
CONVEYANCE SYSTEM ANALYSIS AND DESIGN
Per C.R. #4 of the KCSWDM, the conveyance 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
will be 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 multiple catch basins. Pipes are 12- II
inch, 18-inch and 24-inch diameter LCPE (N-12) material. The peak flow rate
calculated for the Site is 4.65 cfs theoretically occurring during the 100-year, 15-minute '
storm event. Per the following calculations, the most shallow-sloped pipe proposed in �,
the conveyance system is capable of conveying a quantity greater than this flow. The �
vault primary overflow riser is designed to convey the 100-year peak storm, based on �
the KCRTS 15-minute time series for developed, undetained conditions on site. An 18- ,
inch riser and outfall pipe are provided from the vault to outFall splash pad located near
the edge of existing wetland in Tract "B".
DEVELOPED 15-MINUTE TIME STEP MODELING INPUT:
___ �}� _ -
� =�
i� Land tlse Sumrnary :�:��-��"``` ,��� -'��,��, ��,��„� ���•
�
:�'�`��. �.'� �-���� � a:
,�re a ?
Till Forest 0.00 acres
Till Pas#ure U.00 acres �
Till Grass 7.�1 acres
Outwash Farest 0.00 acres
� Outwrash Pasture 0.00 acres
� Outw�sh Grass 0.00 acres
` Wetland 0.00 acres
Impervious 3.17 acres
' � Total
�
'' � A.9$ acres
�
,', � Scale Factor : 1.00 �5-Min Reduced
� Edit Flaw Paths �
---- - - - — - -
` � Time Series: DEV-15MIN »
` Cnmpute Time Series �
� _ _ __ � �
� Modii}r User Input � �
a
� _
File for computed Time Series [.TSF]
;, ..r. � - .. - _�.�r�.._.�.. ��,����:�.>���. •_���.
02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 30 of 43
Drainage Repo�t City of Renton
DEVELOPED 15-MINUTE TIME STEP MODELING OUTPUT:
Flow Frequency Analysis
Time Series File:dev-15min.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
1. 51 6 8/27/O1 18:00 4 . 65 1 100.00 0. 990
1. 07 8 1/05/02 15:00 3.25 2 25.00 0. 960
3.25 2 12/08/02 17:15 2. 11 3 10.00 0. 900
1.21 7 8/23/04 14:30 1.86 4 5.00 0.800
1. 86 4 11/17/04 5:00 1.81 5 3.00 0. 667
1. 81 5 10/27/05 10:45 1.51 6 2.00 0.500
2. 11 3 10/25/06 22:45 1.21 7 1.30 0.231
4. 65 1 1/09/08 6:30 1.07 8 1. 10 0. 091
Computed Peaks 4 . 19 50.00 0. 980
�
il
FLOW CONTROL PRIMARY OVERFLOW
Using standard orifice equation to determine stand pipe diameter in control structure
Ref. KCSWDM '98 Figure 5.3.4.H i
Q�oo = 100-Year, 24-Hour Peak Storm calculated using KCRTS
Qioo = 1.88 cfs
HM� = Maximum available head in feet measured from crest of weir i
HM� = 0.5 ft.
D = Riser Diameter
D = �Q�oo / (3.782 * HM�.5"0.5
// i
D = 0.84 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, 60 Minute storm
H = Actual head above weir achieved with Q��,=
H = (Q�oo / (9.739 * D))^0.6�
H = 0.25 ft.
�
■
02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 32 of 43
Drainage Report City of Renton
BIRD CAGE EMERGENCY OVERFLOW
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
Q�oo= 4.65 cfs
P= Height of primary overflow above outlet invert elevation
P= 14.25 ft.
D= Control structure diameter
D= 48 in.
L= Control structure circumference
L= 12.57 ft.
C= 3.27+0.4H/P (ft)
use...
Qioo= 3.27+0.4H/P(L-0.2H)H^1.5
H= Emergency overFlow water ���rfa�e e'�evation
H= 0.24 f'
�.iJiiiiiicifi,. t'viiU 'vuiiaii i.'vliv�ydiit,c
Solve For...... Full Flow Capacity
Diameter.......................1.50 ft Velocity.........................8.97 fps
Slope.............................0.0194 ft/ft Flow Area..................1.77 sf
Manning's n...................0.012 Critical Slope ............0.0168 ft/ft
Discharge......................15.85 cfs Critical Depth...........1.42 ft
Depth.............................1.50 ft Percent Fu11..............100.00 %
Froude Number............Full
Full Capacity............15.85 cfs
QMAX @.94D.............17.05 cfs
Rock Protection at Outfall
Per Table 4.2.2.A of the 2009 KCSWDM, a 12' long x 7.5' wide x 2' deep Riprap pad
with a crown height of 1 foot will be required at design discharge velocity of 8.97 fps.
02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 33 of 43
Drainage Report City of Renton
BACKWATER ANALYSIS
_2013 D. R STRONG Consulting Engineers Inc. Piper s Bluff Plat Page 34 of 43
Drainage Report City of Renton
Path: c:\bw
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'98 KCSWM Table 3.2.1A
C�= Composite Runoff Coefficient
C�= S(Cn`An)�Arota�
T� 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
�R= �aR)(T�)"�-bR)
aR,bR= coefficients from'98 KCSWM Table 3.2.1.B used to adjust the equation for the design storm
IR= Peak rainfall intensity factor for a storm of retum frequency'R'
�R- PR �R
PR= total precipitation(inches)for the 24-hour storm event for the given frequency. See Issopluvial Maps in'98 KCSWM Figures 3.2.1.A-D
QR= peak flow(cfs)for a storm of return frequency'R'
QR= CC;�R A
The Q-Ratio describes the ratio of the tributary flow to the main upstream flow. ,
R= 100 -year storm
aR= 2.61 I
bR= 0.63
PR= 3.4 inches
Conveyance System Variables:
d= pipe diameter
n= Manning's Number
1= Iength of pipe
Pipe Structures Subasins E A A C C� T� iR IR QR 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.............cfs............�s..........................
........................ .................... .................... ...................
CB#11A TO INLETI
11A 11A 11 11A 5446 0.13 0.57 6.3 0.82 2.78 0.20 0.20 0.00 12 N-12 0.012 16 1.00 460.D0 459.84 464.00 3.87 4.93 0 2
11 11 10 11 8630 0.20 0.65 6.3 0.82 2.78 0.36 0.56 1.81 12 N-12 0.012 231 2.00 459.84 455.22 464.00 5.47 6.97 90 2
FROM RUN 10A-10 21828 0.50 0.69
10 10 9A 10 24633 0.57 0.67
10 10 9A 10 46461 1.07 0.67 6.3 0.82 2.78 1.98 2.53 3.54 12 N-12 0.012 144 5.01 455.22 448.00 459.38 8.67 11.03 0 2
9A 9A 9 9A 16790 0.39 0.64 6.3 0.82 2.78 0.69 3.22 0.27 12 N-12 0.012 16 1.00 448.00 447.84 452.00 3.87 4.93 21 2
9 9 8 9 15717 0.36 0.64 6.3 0.82 2.78 0.65 3.87 0.20 12 N-12 0.012 75 12.99 447.84 438.10 452.00 13.95 17.76 42 2
8 8 7 8 1726 0.04 0.90 6.3 0.82 2.78 0.10 3.97 0.03 12 N-12 0.012 39 10.08 438.10 434.17 443.26 12.29 15.64 21 2
7 7 6 7 859 0.02 0.90 6.3 0.82 2.78 0.05 4.02 0.01 12 N-12 0.012 99 11.28 434.17 423.00 438.17 13.00 16.55 0 4
FROM RUN 6A-6 5581 0.13 0.90
6 6 1A 6 2201 0.05 0.90
6 6 1A 6 7782 0.18 0.90 6.3 0.82 2.78 0.45 4.47 0.11 18 N-12 0.012 41 5.41 423.00 420.78 427.16 26.55 15.02 0 2
FROM RUN 5•1A 67058 1.54 0.71
1A 1A 1 1A 2671 0.06 0.90
1A 1A 1 1A 69729 1.60 0.90 6.3 0.82 2.78 4.01 8.48 0.90 12 N-12 0.012 18 1.00 420.78 420.60 424.78 3.87 4.93 0 2
1 1 VAULT IN 1 1 4416 0.10 0.68 6.3 0.82 2.78 0.19 0.19 0.02 12 N-12 0.012 143 1.33 420.60 418.70 424.82 4.46 5.68 39 2
74145 1.70 1.92
CB#5 TO CB#1A
5 5 4 5 6994 0.16 0.90 6.3 0.82 2.78 0.40 0.40 0.00 12 N-12 0.012 235 3.42 448.84 440.80 452.84 7.16 9.11 0 2
4 4 3 4 29650 0.68 0.68 7.3 0.75 2.54 1.18 1.18 1.00 12 N-12 0.012 131 11.13 440.80 426.22 444.80 12.91 16.44 91 4
FROM RUN 13-3 11028 0.25 1.15
3 3 2 3 18135 0.42 0.69
3 3 2 3 29163 0.67 0.69 8.3 0.69 2.34 1.07 1.07 2.00 12 N-12 0.012 37 7.81 426.22 423.33 432.05 10.82 13.77 92 4
2 2 1A 2 1251 0.03 0.90 9.3 0.64 2.18 0.06 0.06 3.00 12 N-12 0.012 41 6.22 423.33 420.78 427.33 9.65 12.29 93 2
67058 1.54 0.71
CB#13 TO CB#3
13 13 12 13 3473 0.08 0.90 6.3 0.82 2.78 0.20 0.20 0.00 12 N-12 0.012 162 4.35 445.79 438.75 449.79 8.07 10.27 90 2
12 12 3 12 7555 0.17 0.74 8.3 0.69 2.34 0.30 0.30 2.00 12 N-12 0.012 103 12.17 438.75 426.22 442.75 13.50 17.19 92 2
11028 0.25 1.15
Pipe Structures Subasins E A A C Cc T� iR IR Qa 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............A�..........................Ac Min.................................cfs cfs................................!n..............................................ft...........%.............ft...............ft............._ft.............cfs............fPs..........................
............................... ................... ...................
CB#10A TO CB#10
10A 10A 10 10A 21828 0.50 0.69 6.3 0.82 2.78 0.96 0.96 0.00 12 N-12 0.012 16 1.00 455.38 455.22 459.38 3.87 4.93 0 2
CB#6A TO CB#6
6A 6A 6 6A 5581 0.13 0.90 6.3 0.82 2.78 0.32 0.32 0.00 12 N-12 0.012 16 1.00 423.16 423.00 427.16 3.87 4.93 0 2
CB#19 TO VAULT IN 2
19 19 VAULT IN 2 19 16725 0.38 0.58 6.3 0.82 2.78 0.62 0.62 0.00 12 N-12 0.012 63 31.65 441.94 422.00 441.94 21.77 27.72 0 2
16725 0.38 0.58
EX CB TO SD OTFALL
X CE EX CB 18 EX CB 0 0.00 0.00 6.3 0.82 2.78 0.00 0.00 0.00 12 N-12 0.012 12 6.50 465.11 464.33 467.94 9.87 12.56 0 2
18 18 17 18 0 0.00 0.00 6.3 0.82 2.78 0.00 0.00 0.00 12 N-12 0.012 49 3.71 464.33 462.51 467.33 7.46 9.50 90 2
17 17 16 17 0 0.00 0.00 6.3 0.82 2.78 0.00 0.00 0.00 12 N-12 0.012 299 3.96 462.51 450.67 466.51 7.70 9.81 90 2
16 16 iD OUTFALI 16 0 0.00 0.00 6.3 0.82 2.78 0.00 0.00 0.00 12 N-12 0.012 19 0.53 450.67 450.57 453.38 2.81 3.57 90 2
0 0.00 0.00
BACKWATER COMPUTER PROG:�AM FOR PIPES
Pipe data from file:CB#11A TO INLETl.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:422.72 feet i,
Discharge Range:0.5 to 10. Sfi=^ �= � .� 'c`Gl
Overflow Elevation:964. fee-
� Weir:NONE
�� Upstream Velocity:0. feet/se�
�� PIPE NO. 1: 147 LF - 24"CP @ 1.12o OUTLET: 418.?�=� -`7=L�: <_� . �_ --."_"-P: �.
JLTNC NO. 1: OVERFL04�-EL: 424.82 BEND: 39 DEG DIE:i?^71�i'I=: 4.0 �-��':1I0: U. :J�
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HTv-
**��**�**********�*���*�***�*�*+*���*��*�**************�**�*�**��***�****�***,.+
ill *
0.50 3.09 422.73 0.012 0.25 0.20 4.72 4.72 3.09 3.09 0.3`_
1.00 3.08 422.72 * 0.012 0.35 0.27 4.72 4.72 3.08 3.08 0.45
1.50 3.09 422.73 * 0.012 0.43 0.33 4.72 4.72 3.09 3.08 0.50'
2.00 3.09 422.73 * 0.012 0.50 0.38 4.72 4.72 3.09 3.09 0. 6=
2.50 3.10 422.74 * 0.012 0.56 0.42 4.72 4.72 3.10 3.09 O.i2
3.00 3.10 422.74 * 0.012 0.61 0.46 4.72 4.72 3.10 3.09 0.7:
3.50 3.11 422.75 * 0.012 0.66 0.50 4.72 4.72 3.11 3.10 0.�5
4.00 3.12 �22.76 * 0.012 0.71 0.54 4.72 4.72 3.12 3.11 0. 91
9.50 3.13 422.77 * 0.012 0.75 0.57 9.72 4.72 3.13 3.11 0. 97
5.00 3.14 422.78 * 0.012 0.79 0.60 4.72 4.72 3.14 3.12 1.02
5.50 3.15 422.79 * 0.012 0.83 0.63 4.72 4.72 3.15 3.13 1.06
6.00 3.17 422.81 * 0.012 0.87 0.66 4.72 4.72 3.17 3.14 1.10
6.50 3.18 422.82 * 0.012 0.91 0.69 4.72 4.72 3.18 3.15 1.15
-.00 3.20 422.84 * 0.012 0.94 0.72 4.72 4.72 3.20 3.16 1.18
�.50 3.22 422.86 * 0.012 0.98 0.74 4.72 4.72 3.22 3.17 1.22
8.00 3.24 422.88 * 0.012 1.01 0.77 4.72 4.72 3.24 3.18 1.2�
8.50 3.26 422.90 * 0.012 1.04 0.79 4.72 4.72 3.26 3.20 1.28
9.00 3.28 422.92 * 0.012 1.08 0.82 4.72 4.72 3.28 3.21 1.31
9.50 3.30 422.94 * 0.012 1.11 0.84 4.72 4.72 3.30 3.23 1.34
10.00 3.32 422.96 * 0.012 1.14 0.87 4.72 4.72 3.32 3.24 1.36
PIPE N0. 2: 18 LF - 18"CP @ 2.00s OUTLET: 419.64 INLET: 420.00 INTYP: 5
JUNC NO. 2: OVERFLOW-EL: 424.78 BEND: 0 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.90
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
��x��*x************�*****+*****************�***�*********************�*�*******
G.49 2.74 422.74 * 0.012 0.26 0.18 3.09 3.09 2.74 2.74 0.33
G.gg 2.73 422.73 * 0.012 0.37 0.26 3.08 3.08 2.72 2.73 0.48
1.47 2.74 422.74 * 0.012 0.46 0.31 3.09 3.09 2.73 2.74 0.60
1.96 2.75 922.75 * 0.012 0.53 0.36 3.09 3.09 2.74 2.75 0.71
2.44 2.77 422.77 * 0.012 0.60 0.40 3.10 3.10 2.74 2.77 0.80
2.93 2.79 422.79 * 0.012 0.66 0.44 3.10 3.10 2.75 2.79 0.88
3.42 2.82 422.82 * 0.012 0.71 0.47 3.11 3.11 2.77 2.82 0.96
�.91 2.84 422.84 * 0.012 0.76 0.51 3.12 3.12 2.78 2.84 1.04
4.40 2.88 422.88 * 0.012 0.81 0.54 3.13 3.13 2.80 2.88 1.11
4.89 2.92 422.92 * 0.012 0.86 0.57 3.14 3.14 2.81 2.92 1.18
5.38 2.96 422.96 * 0.012 0.90 0.60 3.15 3.15 2.83 2.96 1.25
5.87 3.00 423.00 * 0.012 0.94 0.63 3.17 3.17 2.86 3.00 1.31
6.36 3.05 423.05 * 0.012 0.98 0.66 3.18 3.18 2.88 3.05 1.3E
6.84 3.10 423.10 * 0.012 1.02 0.69 3.20 3.20 2.91 3.10 1.44
7.33 3.16 423.16 * 0.012 1.05 0.72 3.22 3.22 2.93 3.16 1.51
�.82 3.22 423.22 * 0.012 1.09 0.74 3.24 3.24 2.96 3.22 1.57
8.31 3.28 423.28 * 0.012 1.12 0.77 3.26 3.26 2.99 3.28 1.64
8.80 3.35 423.35 * 0.012 1.15 0.80 3.28 3.28 3.03 3.35 1.72
9.29 3.42 423.42 * 0.012 1.18 0.82 3.30 3.30 3.06 3.42 1.81
9.78 3.50 423.50 * 0.012 1.21 0.85 3.32 3.32 3.10 3.50 1.G0
PIPE NO. 3: �1 Lr - 12"CP @ 7.32� OUTLET: 420.00 INLET: 423.00 INTYP: 5
JUNC NO. 3: OVERFLOW-EL: 427.16 BEND: 0 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.11
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*****�*��**************************�**********��**��*��+�**********************
0.26 0.25 423.25 * 0.012 0.21 0.11 2.74 2.74 0.21 ***** 0.25
0.52 0.37 423.37 * 0.012 0.30 0.16 2.73 2.73 0.30 ***** 0.37
0.77 0.47 423.47 * 0.012 0.37 0.19 2.74 2.74 0.37 ***** 0.47
1.03 0.55 423.55 * 0.012 0.43 0.22 2.75 2.75 0.43 ***** 0.55
1.29 0.63 923.63 * 0.012 0.48 0.24 2.77 2.77 0.48 ***** 0.63
1.55 0.70 423.70 * 0.012 0.53 0.27 2.79 2.79 0.53 ***** 0.70
1.80 0.76 423.76 * 0.012 0.58 0.29 2.82 2.82 0.58 ***** 0.76
2.06 0.83 423.83 * 0.012 0.62 0.31 2.84 2.84 0.62 ***** 0.83
2.32 0.89 423.89 * 0.012 0.66 0.33 2.88 2.88 0.66 ***** 0.89
2.58 0.95 423.95 * 0.012 0.69 0.34 2.92 2.92 0.69 ***** 0.95
2.83 1.01 424.01 * 0.012 0.73 0.36 2.96 2.96 0.73 ***** 1.01
3.09 1.07 429.07 * 0.012 0.76 0.38 3.00 3.00 0.76 ***** 1.07
3.35 1.15 424.15 * 0.012 0.79 0.39 3.05 3.05 0.79 ***** 1.15
3.61 1.24 424.24 * 0.012 0.82 0.41 3.10 3.10 0.82 ***** 1.24
3.86 1.33 424.33 * 0.012 0.84 0.43 3.16 3.16 0.84 ***** 1.33
4.12 1.42 424.42 * 0.012 0.86 0.44 3.22 3.22 0.86 ***** 1.42
4.38 1.52 424.52 * 0.012 0.88 0.46 3.28 3.28 0.88 ***** 1.52
4.64 1.63 424.63 * 0.012 0.90 0.47 3.35 3.35 0.90 ***** 1.63
4.89 1.74 424.74 * 0.012 0.92 0.49 3.42 3.92 0.92 ***** 1.74
5.15 1.86 424.86 * 0.012 0.93 0.50 3.50 3.50 0:93 ***** 1.86
PIPE NO. 4: 99 LF - 12"CP @ 11.28� OUTLET: 423.00 INLET: 434.17 INTYP: 5
JUNC NO. 4: OVERFLOW-EL: 438.17 BEND: 0 DEG DIA/WIDTH: 4.0 Q-RATIO: 0.01 i
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI I
***********�*****�*+�*�*************�************+*�***�**********************�
0.23 0.21 434.38 * 0.012 0.20 0.10 0.25 0.25 0.20 ***** 0.21
0.46 0.33 434.50 * 0.012 0.29 0.13 0.37 0.37 0.29 ***** 0.33
0.70 0.42 434.59 * 0.012 0.35 0.16 0.47 0.47 0.35 ***** 0.42
0.93 0.49 434.b6 * 0.012 0.41 0.19 0.55 0.55 0.41 ***** 0.49
1.16 0.56 434.73 * 0.012 0.46 0.21 0.63 0.63 0.46 ***** 0.56
1.39 0.62 434.79 * 0.012 0.50 0.23 0.70 0.70 0.50 ***** 0.62
1.62 0.68 434.85 * 0.012 0.55 0.24 0.76 0.76 0.55 ***** 0.68
1.85 0.74 434.91 * 0.012 0.59 0.26 0.83 0.83 0.59 ***** 0.74
2.09 0.79 434.96 * 0.012 0.62 0.28 0.89 0.89 0.62 ***** 0.79
2.32 0.84 435.01 * 0.012 0.66 0.29 0.95 0.95 0.66 ***** 0.84
2.55 0.88 435.05 * 0.012 0.69 0.31 1.01 1.01 0.69 ***** 0.88
2.78 0.93 435.10 * 0.012 0.72 0.32 1.07 1.07 0.72 ***** 0.93
3.01 0.98 435.15 * 0.012 0.75 0.33 1.15 1.15 0.75 ***** 0.98
3.25 1.04 435.21 * 0.012 0.78 0.35 1.24 1.24 0.78 ***** 1.04
3.48 1.11 435.28 * 0.012 0.80 0.36 1.33 1.33 0.80 ***** 1.11
3.71 1.17 435.34 * 0.012 0.83 0.37 1.42 1.42 0.83 ***** 1.17
3.94 1.25 435.42 * 0.012 0.85 0.38 1.52 1.52 0.85 ***x* 1.25
4.17 1.32 435.49 * 0.012 0.87 0.40 1.63 1.63 0.87 ***** 1.32
4.40 1.40 435.57 * 0.012 0.88 0.41 1.74 1.74 0.88 ***** 1.40
4.64 1.49 435.66 * 0.012 0.90 0.92 1.86 1.86 0.90 ***** 1.49
PIPE NO. 5: 39 LF - 12"CP @ 10.08g OUTLET: 434.17 INLET: 438.10 INTYP: 5
• JUNC NO. 5: OVERFLOW-EL: 443.26 BEND: 21 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.03
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
****�*�****+*�************�**+**�*�*�*�***�****�***�**************************�
0.23 0.21 438.31 * 0_012 0.20 0_10 0.21 0.21 0.20 ***** 0.21
0.46 0.33 438.43 * 0.012 0.29 0.14 0.33 0.33 0.29 ***** 0.33
0.69 0.42 438.52 * 0.012 0.35 0.17 0.42 0.42 0.35 ***** 0.42
0.92 0.50 438.60 * 0.012 0.41 0.19 0.49 0.49 0.41 ***** 0.50
1.14 0.57 438.67 * 0.012 0.46 0.21 0.56 0.56 0.46 ***** 0.57
1.37 0.63 438.73 * O.a12 0.50 0.23 0.62 0.62 0.50 ***** 0.63
1.60 0.69 438.79 * 0.012 0.54 0.25 0.68 0.68 0.54 ***** 0.69
1.83 0.75 438.85 * 0.012 0.58 0.27 0.74 0.74 0.58 ***** 0.75
2.06 0.80 438.90 * 0.012 0.62 0.28 0.79 0.79 0.62 ***** 0.80
2.29 0.85 438.95 * 0.012 0.65 0.30 0.84 0.84 0.65 ***** 0.85
2.52 0.91 439.01 * 0.012 0.69 0.31 0.88 0.88 0.69 ***** 0.91
2.75 0.95 439.05 * 0.012 0.72 0.33 0.93 0.93 0.72 ***** 0.95
2. 98 1.01 439.11 * 0.012 0.74 0.34 0.98 0.98 0.74 ***** 1.01
3.21 1.07 439.17 * 0.012 0.77 0.35 1.04 1.04 0.77 ***** 1.07
3.43 1.14 439.24 * 0.012 0.80 0.37 1.11 1.11 0.80 ***** 1.14
3.66 1.21 439.31 * 0.012 0.82 0.38 1.17 1.17 0.82 ***** 1.21
3.89 1.29 439.39 * 0.012 0.84 0.39 1.25 1.25 0.84 ***** 1.29
4.12 1.37 439.47 * 0.012 0.86 0.40 1.32 1.32 0.86 ***** 1.37
4.35 1.45 439.55 * 0.012 0.88 0.92 1.40 1.40 0.88 ***** 1.45
4.58 1.54 439.64 * 0.012 0.90 0.43 1.49 1.99 0.90 ***** 1.54
PIPE NO. 6: 75 LF - 12"CP @ 12.99� OUTLET: 438.10 INLET: 447.84 INTYP: 5
JUNC NO. 6: OVERFLOW-EL: 452.00 BEND: 42 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.20
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*****�******�*�*�*************�***�*��**�****��**�****�***********�*�**********
0.22 0.20 448.04 * 0.012 0.20 0.09 0.21 0.21 0.20 ***** 0.20
0.45 0.31 448.15 * 0.012 0.28 0.13 0.33 0.33 0.28 ***** 0.31
0.67 0.40 448.24 * 0.012 0.35 0.15 0.42 0.42 0.35 ***** 0.40
0.89 0.48 448.32 * 0.012 0.40 0.18 0.50 0.50 0.40 ***** 0.48 I
1.12 0.56 498.40 * 0.012 0.45 0.20 0.57 0.57 0.45 ***** 0.5� !
1.34 0.63 448.47 * 0.012 0.49 0.21 0.63 0.63 0.49 ***** 0. �_
1.56 0.70 448.54 * 0.012 0.54 0.23 0.69 0.69 0.54 ***** 0.�
1.79 0.76 448.60 * 0.012 0.57 0.25 0.75 0.75 0.57 ***** 0. �
2.01 0.82 448.66 * 0.012 0.61 0.26 0.80 0.80 0.61 ***** 0. -
2.23 0.89 448.73 * 0.012 0.64 0.28 0.85 0.85 0.64 ***** 0.
2.46 0.95 448.79 * 0.012 0.68 0.29 0.91 0.91 0.68 ***** 0. :
2.68 1.01 448.85 * 0.012 0.71 0.30 0.95 0.95 0.71 ***** 1.
2.90 1.07 448.91 * 0.012 0.74 0.31 1.01 1.01 0.74 ***** 1.
3.13 1.14 448.98 * 0.012 0.76 0.33 1.07 1.07 0.76 ***** 1.14
3.35 1.23 449.07 * 0.012 0.79 0.34 1.14 1.14 0.79 ***** 1.23
3.57 1.32 449.16 * 0.012 0.81 0.35 1.21 1.21 0.81 ***** 1.32 �
3.79 1.41 449.25 * 0.012 0.83 0.36 1.29 1.29 0.83 ***** 1.41
4.02 1.51 449.35 * 0.012 0.85 0.37 1.37 1.37 0.85 ***** 1.51
9.24 1.61 449.45 * 0.012 0.87 0.38 i.45 1.45 0.87 ***** 1.61
9.46 1.72 449.56 * 0.012 0.69 0.39 1.54 1.54 0.89 ***** 1.72
PIPE NO. 7: 16 LF - 12"CP @ 1.00o OUTLET: 447.89 INLET: 448.00 INTYP: 5
JUNC NO. 7: OVERFLOW-EL: 452.00 BEND: 21 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.27
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
************************************�******�*********�*�****��**�*****�*�******
0.19 0.23 448.23 * 0.012 0.18 0.15 0.20 0.20 0.18 ***** 0.23
0.37 0.34 448.34 * 0.012 0.26 0.21 0.31 0.31 0.26 ***** 0.34
0.56 0.42 498.42 * 0.012 0.32 0.26 0.40 0.40 0.32 ***** 0.42
0.74 0.49 448.49 * 0.012 0.37 0.30 0.48 0.48 0.37 ***** 0.49
0.93 0.56 448.56 * 0.012 0.41 0.34 0.56 0.56 0.41 ***** 0.56
1.12 0.62 448.62 * 0.012 0.45 0.37 0.63 0.63 0.45 ***** 0.62
1.30 0.67 448.67 * 0.012 0.99 0.41 0.70 0.70 0.49 ***** 0.67
1.49 0.79 448.79 * 0.012 0.52 0.44 0.76 0.76 0.57 0.79 0.73
1.67 0.84 948.89 * 0.012 0.55 0.47 0.82 0.82 0.65 0.84 0.78
1.86 0.90 448.90 * 0.012 0.59 0.49 0.89 0.89 0.72 0.90 0.83
2.04 0.97 948.97 * 0.012 0.62 0.52 0.95 0.95 0.80 0.97 0.89
2.23 1.05 949.05 * 0.012 0.64 0.55 1.01 1.01 0.89 1.05 0.94
2.42 1.14 949.14 * 0.012 0.67 0.58 1.07 1.07 0.98 1.19 0.99
2.60 1.24 949.24 * 0.012 0.70 0.61 1.14 1.14 1.06 1.29 1.04
2.79 1.37 449.37 * 0.012 0.72 0.63 1.23 1.23 1.15 1.37 1.09
2.97 1.49 449.49 * 0.012 0.74 0.66 1.32 1.32 1.25 1.49 1.14
3.16 1.63 449.63 * 0.012 0.77 0.69 1.41 1.41 1.36 1.63 1.20
3.35 1.77 449.77 * 0.012 0.79 0.72 1.51 1.51 1.47 1.77 1.27
3.53 1.92 449.92 * 0.012 0.81 0.76 1.61 1.61 1.58 1.92 1.34
3.72 2.08 450.08 * 0.012 0.83 0.79 1.72 1.72 1.71 2.08 1.4]
PIPE NO. 8: 144 LF - 12"CP @ 5.01$ OUTLET: 448.00 INLET: 455.22 INTYP: �
JUNC NO. 8: OVERFLOW-EL: 459.38 BEND: 0 DEG DIA/WIDTH: 2.0 Q-RATIO: 3.�4
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
**��****�****�****�**�***�**�***************************�**********�***********
0.15 0.19 455.41 * 0.012 0.16 0.10 0.23 0.23 0.16 ***** 0.19
0.29 0.28 455.50 * 0.012 0.23 0.13 0.34 0.34 0.23 ***** 0.28
0.44 0.35 955.57 * 0.012 0.28 0.16 0.42 0.42 0.28 ***** 0.35
0.58 0.41 455.63 * 0.012 0.32 0.18 0.49 0.49 0.32 ***** 0.4"_
0.73 0.47 455.69 * 0.012 0.36 0.20 0.56 0.56 0.36 ***** 0.47
0.86 0.53 955.75 * 0.012 0.40 0.22 0.62 0.62 0.40 ***** 0.53
1.02 0.58 455.80 * 0.012 0.43 0.24 0.67 0.67 0.43 ***** 0.58
1.17 0.63 455.85 * 0.012 0.46 0.25 0.79 0.79 0.46 ***** 0.63
1.32 0.68 455.90 * 0.012 0.49 0.27 0.84 0.64 0.49 ***** 0.68
1.46 0.72 455.94 * 0.012 0.52 0.28 0.90 0.90 0.52 ***** 0.72
1.61 0.77 455.99 * 0.012 0.54 0.30 0.97 0.97 0.54 ***** 0.77
1.75 0.82 456.04 * 0.012 0.57 0.31 1.05 1.05 0.57 ***** 0.82
1. 90 0.86 456.08 * 0.012 0.59 0.32 1.19 1.14 0.59 ***** 0.86
2.G5 0.91 456.13 * 0.012 0.62 0.34 1.24 1.24 0.62 ***** 0.91
2.i9 0.96 456.18 * 0.012 0.64 0.35 1.37 1.37 0.64 ***** 0.96
2.34 1.00 456.22 * 0.012 0.66 0.36 1.49 1.49 0.66 ***** 1.00
2.�8 1.05 456.27 * 0.012 0.68 0.37 1.63 1.63 0.68 ***** 1.05
2.63 1.10 456.32 * 0.012 0.70 0.38 1.77 1.77 0.70 ***** 1.10
2.78 1.14 456.36 * 0.012 0.72 0.39 1.92 1.92 0.72 ***** 1.14
2. 92 1.20 456.42 * 0.012 0.74 0.41 2.08 2.08 0.74 ***** 1.20
PIP� NO. 9: 231 LF - 12"CP @ 2.00$ OUTLET: 455.22 INLET: 459.84 INTYP: 5 I
JJNC N0. 9: OVERFLOW-EL: 464.00 BEND: 90 DEG DIA/WIDTH: 2.0 Q-RATIO: 1.81
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
�++x+x********�*�**++*********+**�*********************************************
��.03 0.09 459.93 * 0.012 0.08 0.06 0.19 0.19 0.08 ***** 0.09
��.06 0.13 459.97 * 0.012 0.11 0.08 0.28 0.28 0.11 ***** 0.13
��.10 0.16 460.00 * 0.012 0.13 0.10 0.35 0.35 0.13 ***** 0.16
��. 13 0.19 460.03 * 0.012 0.15 0.11 0.41 0.41 0.15 ***** 0.19
0.16 0.21 460.05 * 0.012 0.17 0.12 0.47 0.47 0.17 ***** 0.21
��.19 0.23 460.07 * 0.012 0.19 0.13 0.53 0.53 0.19 ***** 0.23
G.23 0.25 460.09 * 0.012 0.20 0.14 0.58 0.58 0.20 ***** 0.25
G.26 0.27 460.11 * 0.012 0.21 0.15 0.63 0.63 0.21 ***** 0.27
G.29 0.29 960.13 * 0.012 0.23 0.16 0.68 0.68 0.23 ***** 0.29
_�.32 0.31 460.15 * 0.012 0.24 0.17 0.72 0.72 0.24 ***** 0.31
0.35 0.33 460.17 * 0.012 0.25 0.18 0.77 0.77 0.25 ***** 0.33
G.39 0.34 960.18 * 0.012 0.26 0.19 0.82 0.82 0.26 ***** 0.34
0.42 0.36 460.20 * 0.012 0.27 0.19 0.86 0.86 0.27 ***** 0.36
G.45 0.37 460.21 * 0.012 0.28 0.20 0.91 0.91 0.28 ***** 0.37
G.48 0.39 460.23 * 0.012 0.29 0.21 0.96 0.96 0.29 ***** 0.39
0.51 0.40 460.24 * 0.012 0.30 0.21 1.00 1.00 0.30 ***** 0.40
G.55 0.41 460.25 * 0.012 0.31 0.22 1.05 1.05 0.31 ***** 0.91
0.58 0.43 460.27 * 0.012 0.32 0.23 1.10 1.10 0.32 ***** 0.43
0.61 0.44 460.28 * 0.012 0.33 0.23 1.14 1.14 0.33 ***** 0.94
G.59 0.45 460.29 * 0.012 0.34 0.24 1.20 1.20 0.34 ***** 0.45
F=?E NO.10: 16 LF - 12"CP @ 1.00$ OUTLET: 459.84 INLET: 460.00 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
x*��+�+**�****�*�*************�********************�***��*�****��**************
r�.01 0.05 460.05 * 0.012 0.05 0.04 0.09 0.09 0.05 ***** 0.05
0.02 0.08 460.08 * 0.012 0.07 0.06 0.13 0.13 0.07 ***** 0.08
0.03 0.10 460.10 * 0.012 0.08 0.07 0.16 0.16 0.08 ***** 0.10
0.05 0.11 460.11 * 0.012 0.09 0.08 0.19 0.19 0.09 ***** 0.11
0.06 0.13 46G.?3 * 0.012 0.10 0.09 0.21 0.21 0.10 ***** 0.13
0.07 0.14 460.14 * 0.012 0.11 0.10 0.23 0.23 0.11 ***** 0.14
0.06 0.15 460.15 * 0.012 0.12 0.10 0.25 0.25 0.12 ***** 0.15
0.09 0.16 460.16 * 0.012 0.13 0.11 0.27 0.27 0.13 ***** 0.16
0.10 0.17 460.17 * 0.012 0.14 0.12 0.29 0.29 0.14 ***** 0.17
0.11 0.21 460.21 * 0.012 0.14 0.12 0.31 0.31 0.15 0.21 0.18
0.13 0.22 460.22 * 0.012 0.15 0.13 0.33 0.33 0.17 0.22 0.19 i
0.19 0.23 460.23 * 0.012 0.16 0.13 0.34 0.34 0.18 0.23 0.20
0.15 0.24 460.24 * 0.012 0.16 0.14 0.36 0.36 0.20 0.24 0.21
0.16 0.25 460.25 * 0.012 0.17 0.14 0.37 0.37 0.21 0.25 0.22
0.17 0.26 460.26 * 0.012 0.17 0.15 0.39 0.39 0.22 0.26 0.22
0.18 0.28 460.28 * 0.012 0.18 0.15 0.40 0.40 0.24 0.28 0.23 i
0.19 0.29 460.29 * 0.012 0.19 0.16 0.41 0.41 0.25 0.29 0.24 �
0.21 0.30 460.30 * 0.012 0.19 0.16 0.43 0.43 0.27 0.30 0.25 '
0.22 0.31 460.31 * 0.012 0.20 0.17 0.44 0.44 0.28 0.31 0.25 �I
0.23 0.32 460.32 * 0.012 0.20 0.17 0.45 0.45 0.29 0.32 0.26
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BACKWATER COMPUTER PROGRF.M FG� PIPES
Pipe data from file:CB#5 TO CB�1A.b���p
Surcharge condition at intermediate junctions
Tailwater Elevation:423.35 feet
Discharge Range:0.5 to 5. Step of 0.� [cfs]
Overflow Elevation:452.84 feet
Weir:NONE
Opstream Velocity:0. feet/se�
PIPE NO. 1: 41 LF - 12"CP @ 8.12s OUTLET: 420.00 INLET: 423.33 IN1YP: 5
JUNC N0. 1: OVERFLOW-EL: 427.33 BEND: 90 DEG DIA/WIDTH: 2.0 Q-RATIO: 0.02
Q(CFS) HW(FT) HW ELEV. * N-rAC DC DN TW DO DE HWO HWI
**��**********�*�*****��*�*����************�*�*****�***********�**�******�***�*
0.50 0.36 423.69 * 0.012 0.30 0.15 3.35 3.35 0.30 ***** 0.36
1.00 0.56 423.89 * 0.012 0.43 0.21 3.35 3.35 0.43 ***** 0.56
1.50 0.74 424.07 * 0.012 0.52 0.25 3.35 3.35 0.52 ***** 0.74
2.00 0.91 424.24 * 0.012 0.61 0.29 3.35 3.35 0.61 ***** 0. 91
2.50 1.09 424.42 * 0.012 0.68 0.33 3.35 3.35 0.68 ***** 1.09
3.00 1.28 424.61 * 0.012 0.75 0.36 3.35 3.35 0.75 ***** 1.28
3.50 1.52 424.85 � 0.012 0.80 0.39 3.35 3.35 0.80 ***** 1.52
�.00 1.79 425.12 * 0.012 0.85 0.42 3.35 3.35 0.85 ***** 1.79
�.50 2.10 425.43 * 0.012 0.89 0.45 3.35 3.35 0.89 ***** 2.10
5.G0 2.4� 425.�8 * O.Q12 0.92 0.�8 3.35 3.35 0.92 ***x* 2.�5
PIFE NO. 2: 37 �F - 12"�P ? �.8-_`o CJ^LET: 423.33 _v'_E�: �26.22 INTY�: 5 I
JUNC NO. 2: OVERFLOW-EL: 432.05 BEND: 90 DEG DIA/WIDTH: 4.0 Q-RATIO: 0.68 �
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
x���x*******�*********�****���***�+��**�*�**�**�***************�**�******�*****
0.49 0.36 426.58 * 0.012 0.30 0.15 0.36 0.36 0.30 ***** 0.36
0.98 0.55 426.77 * 0.012 0.42 0.21 0.56 0.56 0.42 ***** 0.55
1.97 0.73 426.95 * 0.012 0.52 0.25 0.74 0.74 0.52 ***** 0.73
1.96 0.89 427.11 * 0.012 0.60 0.29 0.91 0.91 0.60 ***** 0.89
2.45 1.06 427.28 * 0.012 0.68 0.33 1.09 1.09 0.68 ***** 1.06
2.94 1.24 427.46 * 0.012 0.74 0.36 1.28 1.28 0.74 ***** 1.24
3.43 1.47 427.69 * O.Oi2 0.80 0.39 1.52 1.52 0.80 ***** 1.47
3.92 1.72 427.94 * 0.012 0.85 0.42 1.79 1.79 0.85 ***** 1.72
4.41 2.01 428.23 * O.Oi2 0.89 0.45 2.10 2.10 0.89 ***** 2.01
4.90 2.39 42�.56 * 0.0"_2 G. 92 0.48 2.45 2.45 0.92 �**** 2.34
PIPE N0. 3: 131 L� - 12"CP @ 11.13� OUTLET: 4�6.22 INLET: 440.80 InTYP: 5
JJNC N0. 3: OVERFLOW-EL: 444.80 BEND: 90 DEG DIA/WIDTH: 4.0 Q-RATIO: 2.93
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
�x�x�+**********�**********��**�*****�**�**�*�***�***�***********�********�****
0.29 0.25 441.05 * 0.012 0.23 0.11 0.36 0.36 0.23 ***** 0.25
0.58 0.38 441.18 * 0.012 0.32 0.15 0.55 0.55 0.32 ***** 0.38
G.87 0.50 441.30 * 0.012 0.90 0.18 0.73 0.73 0.40 ***** 0.50
"�.17 0.60 441.40 * 0.012 0.46 0.21 0.89 0.89 0.46 ***** 0.60
1.46 0.70 441.50 * 0.012 0.52 0.23 1.06 1.06 0.52 ***** 0.70
1.75 0.79 441.59 * 0.012 0.57 0.25 1.24 1.24 0.57 ***** 0.79
2.04 0.89 441.69 * 0.012 0.61 0.27 1.47 1.47 0.61 ***** 0.89
2.33 0.98 441.78 * 0.012 0.66 0.29 1.72 1.72 0.66 ***** 0.98
2.62 1.08 441.88 * 0.012 0.70 0.31 2.01 2.01 0.70 ***** 1.08
2.92 1.18 441.98 * O.Q12 0.74 0.33 2.39 2.34 0.74 ***** 1.18
PIPE NO. 4: 235 LF - 12"CP @ 3.42$ OUTLET: 440.80 INLET: 448.64 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
**************���**�+***�*****************+***�*��*�*��**+�*�*�**********�*****
0.07 0.13 448.97 * 0.012 0.12 0.08 0.25 0.25 0.12 ***** 0.13
0.15 0.20 449.04 * 0.012 0.16 0.10 0.38 0.38 0.16 ***** 0.20
0.22 0.25 449.09 * 0.012 0.20 0.13 0.50 0.50 0.20 ***** 0.25
0.30 0.29 449.13 * 0.012 0.23 0.14 0.60 0.60 0.23 ***** 0.29
0.37 0.33 449.17 * 0.012 0.26 0.16 0.70 0.70 0.26 ***** 0.33
0.45 0.36 449.20 * 0.012 0.28 0.17 0.79 0.79 0.28 ***** 0.36
0.52 0.39 449.23 * 0.012 0.30 0.19 0.89 0.89 0.30 ***** 0.39 i
0.59 0.43 449.27 * 0.012 0.33 0.20 0.98 0.96 0.33 ***** 0.43
0.67 0.46 449.30 * 0.012 0.35 0.21 1.08 1.06 0.35 ***** 0.46 �
0.74 0.48 449.32 * 0.012 0.36 0.22 1.16 1.18 0.36 ***** 0.48 I
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BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:CB#13 TO CB#3.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:432.05 feet
Discharge Range:0.5 to 3. Step of 0.5 [cfs]
Overflow Elevation:449.79 feet
Weir:NONE
Upstream Velocity:0. feet/sec
PIPE NO. 1: 103 LF - 12"CP @ 12.17$ OUTLET: 426.22 INLET: 438.75 INTYP: 5
JUNC NO. 1: OVERFLOW-EL: 442.75 BEND: 90 DEG DIA/WIDTH: 2.0 Q-RATIO: 1.50
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
- ****�*�***�**�*************�******�*�*�*+****�*�**�****�*�****�****�***********
0.50 0.34 439.09 * 0.012 0.30 0.14 5.83 5.83 0.30 ***** 0.34
1.00 0.54 439.29 * 0.012 0.43 0.19 5.83 5.83 0.43 ***** 0.54
1.50 0.71 439.46 * 0.012 0.52 0.23 5.83 5.83 0.52 ***** 0.71
--• 2.00 0.68 439.63 * 0.012 0.61 0.27 5.83 5.83 0.61 ***** 0.88
2.50 1.04 439.79 * 0.012 0.68 0.30 5.83 5.83 0.66 ***** 1.04
� 3.00 1.22 439.97 * 0.012 0.75 0.33 5.83 5.83 0.75 ***** 1.22
F=PE NO. 2: 162 LF - 12"CP @ 4.35g OUTLET: 438.75 INLET: 445.79 INTYP: 5
� Q;CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
**��***�**�********�**+�**+*�********��*�************************+***�*********
0.20 0.23 446.02 * 0.012 0.19 0.11 0.34 0.34 0.19 ***** 0.23
�� 0.40 0.34 446.13 * 0.012 0.27 0.16 0.54 0.54 0.27 ***** 0.34
0.60 0.42 446.21 * 0.012 0.33 0.19 0.71 0.71 0.33 ***** 0.42
0.80 0.50 446.29 * 0.012 0.36 0.22 0.88 0.88 0.38 ***** 0.50
1.00 0.5� 446.36 * 0.012 0.43 0.24 1.04 1.04 0.43 ***** 0.57
1.20 0.6� 44C.43 * 0.��12 0.4? �.�? '_.22 1.22 0.47 �**** O.o4
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BACfCti9ATER COMPUTER PRO�RAh1 F03 PIPES
Pipe data from file:CB#6A TO CB #6.bwp
Surcharge condition at intermediate junctions '
Tailwater Elevation:424.63 feet
Discharge Range:0.5 to 3. Step of 0.5 [cfs]
Overflow Elevation:427.16 feet
Weir:NONE
lipstream Velocity:0. feet/sec
P=FE N0. 1: 16 LF - 12"CP @ 1.00% OUTLET: 423.00 INLET: 423.16 INTYP: 5
Q;CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
,�_�******�*�*�����**�*���*x�x****�****+****�*****�********�**�*******�*��+****�
0.50 1.49 424.65 * 0.012 0.30 0.25 1.63 1.63 1.46 1.49 0.40
1.00 1.52 424.68 * 0.012 0.43 0.35 1.63 1.63 1.48 1.52 0.59
1.50 1.58 424.74 * 0.012 0.52 0.44 1.63 1.63 1.49 1.58 0.76
2.00 1.66 424.82 * 0.012 0.61 0.52 1.63 1.63 1.51 1.66 0.92
2.50 1.77 424.93 * 0.012 0.68 0.59 1.63 1.63 1.54 1.77 1.07
3.00 '.91 425.07 * 0.012 0.75 0.67 1.63 1.63 1.5? 1. 91 1.24
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BACKWATER COMPUTER PROGRAM FOR PIPES
Pipe data from file:CB#l0A TO CB #l0.bwp
Surcharge condition at intermediate junctions
Tailwater Elevation:456.32 feet
Discharge Range:0.5 to 3. Step of 0.5 [cfs]
Overflow Elevation:459.38 feet
Weir:NONE
Upstream Velocity:0. feet/sec
PIPE NO. 1: 16 LF - 12"CP @ 1.00$ OUTLET: 455.22 INLET: 455.38 INTYP: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
**�*�**�**********��***********************���**�**�**�************�**�*��***�*
0.50 0.96 456.34 * 0.012 0.30 0.25 1.10 1.10 0.95 0.96 0.40
1.00 0.99 456.37 * 0.012 0.43 0.35 1.10 1.10 0.95 0.99 0.59
1.50 1.06 456.44 * 0.012 0.52 0.44 1.10 1.10 0.97 1.06 0.76
2.00 1.13 456.51 * 0.012 0.61 0.52 1.10 1.10 0.98 1.13 0.92
2.50 1.25 456.63 * 0.012 0.68 0.59 1.10 1.10 1.01 1.25 1.07
3.00 1.38 456.76 * 0.012 0.75 0.67 1.10 1.10 1.04 1.38 1.24
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BACKWATER COMPUTER PROGRA� rOR PIPES
Pipe data from file:CB#20 TO VAULT IN 2.bwp
- Surcharge condition at intermediate junctions
Tailwater Elevation:422.72 feet
Discharge Range:0.5 to 3. Step o` C.5 [cfs]
Overflow Elevation:441.94 feet
Weir:NONE
Upstream Ve1o�i�y:0. feet/sec
PIPr, NO. 1: c3 L= - -iZ"CP Ca �c.89`s JU"LE'1': 422.OJ 1P."LE'1': �38.94 1N:'Y'Y: 5
Q(CFS) HW(FT) HW ELEV. * N-FAC DC DN TW DO DE HWO HWI
*****�*****���********************��*��*:**�*********���*******�****�******�**�
0.50 0.30 439.24 * 0.012 0.30 0.11 0.72 0.72 0.30 ***** 0.27
1.00 0.46 439.40 * 0.012 0.43 0.16 0.72 0.72 0.43 ***** 0.46
1.50 0.63 939.57 * 0.012 0.52 0.19 0.72 0.72 0.52 ***** 0. 63
2.00 0.79 939.73 * 0.012 0.61 0.22 0.72 0.72 0.61 ***** 0.79
2.50 0.95 439.89 * 0.012 0.68 0.24 0.72 0.72 0.68 ***** 0. 95
3.00 1.11 940.0� * 0.012 0.75 0.2� 0.72 0.�2 0.75 ***** 1.1"_
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BACKWATER ANALYSIS MAP I
,:2013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 35 of 43
Drainage Report City of Renton
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_ 1
SECTION VI
SPECIAL REPORTS AND STUDIES
The following report and studies have been provided with this submittal.
1. Traffic Impact Analysis — Jake Traffic Engineering, Inc. July 30, 2012
2. Critical Areas Report & Supplemental Stream Study) — Sewall Wetland Consulting.
April 15, 2013
3. Geotechnical Engineering Study — Terra Associates, Inc. .,August 9, 2012 and
Addendum to Geotechnical Report dated February 1, 2013.
4. Structural Analysis and Design — Kosnik Engineering, PC. January 25th, 2013.
2013 D R STRCNG Corsul;irg Engineers Inc. Piper s 6!uff PIGt Page 36 of 43
Drainage Report City of Renton
SECTION VII
OTHER PERMITS, VARIANCES AND ADJUSTMENTS I
1. Structural retaining and rockery wall permit.
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02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 37 of 43
Drainage Report City of Renton
SECTION VIII
ESC PLAN ANALYSIS AND DESIGN (PART A)
The Erosion and Sedimentation Control Design meets the nine minimum requirements:
1. Clearing Limits — Areas to remain undisturbed shall be delineated with a high-
visibility plastic fence prior to any site clearing or grading.
2. Cover Measures — Disturbed Site 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 — Permanent storm detention pond will be utilized for
sediment retention. Pond outlet will be plugged and water will be pumped as
necessary to avoid overflow. Sediment-laden water will be disposed of in a
manner approved by the City. Permanent storm detention pond shall be
installed prior to grading of any contributing area.
6. Surface Water Control —Interceptor berms or swales shall be installed to control
and intercept all surface water from disturbed areas and shall be routed to the
detention pond for retention.
7. Dewatering Control —Will be provided as needed.
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 — During construction, runoff will be conveyed to the permanent
flow control facility. The vault outlet will be plugged, preventing runoff from
leaving the site until final stabilization.
SWPPS PLAN DESIGN (PART B)
The complete CSWPPP is included in Appendix A.
�2013 D. R. STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 38 of 43
Drainage Report City of Renton
SECTION IX
BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
1. Bond Quantity Worksheet — will be provided prior to final engineering
approval.
2. The Stormwater Facility Summary Sheet is included in this section
3. Declaration of Covenant—will be provided prior to final engineering approval.
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02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 39 of 43
Drainage Report City of Renton
King County Department of Development&Environmental Services
900 Oakesdale Avenue Southwest
Renton,Washington 98055-1219
Project Name: Piper's Bluff Date: 2/4/2013
�ocat�or,: 1166 Hoquiam Ave NE, Renton, Washin ton Project No.: LUA12-078, ECF, PP
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.
x yes no
If yes,
Forest Practice Permit Number:
(RCW 76.09)
Page 1 of 9
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Unit #of
Reference# Price Unit Quantity Applications Cost
EROSION/SEDIMENT CONTROL
Backfill &compaction-embankment $ 5.62 CY 290 1 1,629.80
Check dams,4"minus rock SWDM 5.4.6.3 $ 67.51 Each 10 1 675.10
Crushed surfacing 1 1/4"minus WSDOT 9-03.9(3) $ 85.45 CY
Ditching $ 8.08 CY 290 1 2,343.20
Excavation-bulk $ 1.50 CY 1
Fence, silt SWDM 5.4.3.1 $ 1.38 LF 1001 1 1,381.38
Fence,Temporary(NGPE) $ 1.38 LF 223 1 307.74
Hydroseedin SWDM 5.4.2.4 $ 0.59 SY 24108 1 14,223.72
Jute Mesh SWDM 5.4.2.2 $ 1.45 SY 0.00
Mulch, by hand, straw, 3"deep SWDM 5.4.2.1 $ 2.01 SY 0.00
Mulch, by machine, straw, 2"deep SWDM 5.4.2.1 $ 0.53 SY 24108 1 12,777.24
Pipin ,tem orary, CPP, 6" $ 10.70 LF 0.00
Piping, temporar , CPP, 8" $ 16.10 LF 0.00
Piping,tempora , CPP, 12" $ 20.70 LF 205 1 4,243.50
Plastic coverin , 6mm thick, sandba ged SWDM 5.4.2.3 $ 2.30 SY 0.00
Ri Rap, machine placed; slopes WSDOT 9-13.1(2) $ 39.08 CY 3 1 117.24
Rock Construction Entrance, 50'x15'x1' SWDM 5.4.4.1 $ 1,464.34 Each 0.00
Rock Construction Entrance, 100'x15'x1' SWDM 5.4.4.1 $ 2,928.68 Each 1 1 2,928.68
Sediment pond riser assembly SWDM 5.4.5.2 $ 1,949.38 Each 0.00
Sediment trap, 5' hi h berm SWDM 5.4.5.1 $ 17.91 LF 0.00
Sed. ond, 5'high, riprapped spillwa berm section SWDM 5.4.5.1 $ 68.54 LF 0.00
Seeding, by hand SWDM 5.4.2.4 $ 0.51 SY 0.00
Sodding, 1"deep, level round SWDM 5.4.2.5 $ 6.03 SY 0.00
Soddin , 1"dee , sloped ground SWDM 5.4.2.5 $ 7.45 SY 0.00
TESC Supervisor $ 74.75 HR 24 1 1,794.00
Water truck, dust control SWDM 5.4.7 $ 97.75 HR 16 1 1,564 00
WRITE-IN-ITEMS **,�* (see page 9) ��,�a��'m,�. ���i������ � � � � .� ���, �,< ;
SWEEPER TRUCK $ 85.00 HR 6 1 510
INLET PROTECTION $ 25.00 Each 19 1 475
ESC SUBTOTAL: $ 44,970.60
30%CONTINGENCY&MOBILIZATION: $ 13,491.18
ESC TOTAL: $ 58,461.78
COLUMN: A
Page 2 of 9
Existing Future Pubiic Private Quantity Completed
Right-of-Way Road Improvements Improvements (Bond Reduction)`
&Draina e Facilities Quant.
Unit Price Unit Quant Cost Quant. Cost Quant. Cost Com lete Cost
\7E�ERl1� �=J�MS �` `�`, ,,:�.�i �rr�a�,r,! �^g r ��..'�,5 � �...t .. �,�. ..�.,x�N���n,nN�AHI��i�i91���r b" '4'�'M �d�.. ,�-,�.V 15�.-. �����J��.i+h�II�"�i:u� +�3���� � ..' I�L�.r,..,.. I ,�.�a.;.x �� . .,��1
�'r«p XI I l�C �"s �..� ,�,.• `#., §����k��� .� . `� n .. �,.�r Y x _q �. ' .v
-,a ,�>: ,T_:..n�.. 7 . , � . ,x . . _ .
Backfill&Compaction-embankment $ 5.62 CY $0.00 $0.00 $0.00 $0.00
Backfill&Compaction-trench $ 8.53 CY 210 $1,791.30 427 $3,642.31 237 $2,021.61 $0.00 '
Clear/Remove Brush, b hand $ 0.36 SY $0.00 $0.00 $0.00 $0.00 i
Ciearin /Grubbin /Tree Removal $ 8,876.16 Acre 0.237 $2,103.65 1.128 $10,012.31 3.616 $32,096.19 $0.00 I
Excavation-bulk $ 1.50 CY 604 $906.00 3892 $5,838.00 8351 $12,526.50 $0.00 I
Excavation-Trench $ 4.06 CY 215 $872.90 560 $2,273.60 248 $1,006.88 $0.00 i
Fencin , cedar,6'hi h $ 18.55 LF $0.00 $0.00 3319 $61,567.45 $0.00
Fencin ,chain link,vin I coated, 6'hi h $ 13.44 LF $0.00 $0.00 $0.00 $0.00
Fencin ,chain link, ate,vin I coated, 20' $ 1,271.81 Each $0.00 $0.00 $0.00 $0.00
Fencin , split rail,3'hi h $ 12.12 LF $0.00 50 $606.00 $0.00 $0.00
Fill&compact-common barrow $ 22.57 CY $0.00 $0.00 $0.00 $0.00
Fill&com act- ravel base $ 25.48 CY $0.00 $0.00 $0.00 $0.00
Fill 8�compact-screened to soil $ 37.85 CY $0.00 $0.00 $0.00 $0.00
Gabion, 12"deep,stone filled mesh $ 54.31 SY $0.00 $0.00 $0.00 $0.00
Gabion, 18"deep,stone filled mesh $ 74.85 SY $0.00 $0.00 $0.00 $0.00
Gabion,36"dee ,stone filled mesh $ 132.48 SY $0.00 $0.00 $0.00 $0.00
Gradin ,fine, b hand $ 2.02 SY $0.00 $0.00 $0.00 $0.00
Gradin ,fine,with rader $ 0.95 SY $0.00 $0.00 $0.00 $0.00
Monuments, 3'long $ 135.13 Each 2 $270.26 $0.00 $0.00 $0.00
Sensitive Areas Si n $ 2.88 Each $0.00 $0.00 $0.00 $0.00
Soddin , 1"deep,sio ed round $ 7.46 SY $0.00 $0.00 $0.00 $0.00
Surve in , line& rade $ 788.26 Da 1 $788.26 1 $788.26 $0.00 $0.00
Surve in , lot location/lines $ 1,556.64 Acre $0.00 $0.00 3 $4,669.92 $0.00
Traffic control crew(2 fla ers) $ 85.18 HR 48 $4,088.64 $0.00 $0.00 $0.00
Trail,4"chip ed wood $ 7.59 SY $0.00 $0.00 $0.00 $0.00
Trail,4"crushed cinder $ 8.33 SY $0.00 $0.00 $0.00 $0.00
Trail,4"to course $ 8.19 SY $0.00 $0.00 $0.00 $D.00
Wall, retainin ,concrete $ 44.16 SF $0.00 $0.00 $0.00 $0.00
Wall, rockery $ 9.49 SF $0.00 $0.00 653 $6,196.97 $0.00
Page 3 of 9 SUBTOTAL $10,821.01 $23,160.48 $120,085.52 $0.00
Existing Future Public Private Bond Reduction`
Right-of-way Road Improvements Improvements
&Draina e Facilities Quant.
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Com lete Cost
���+I '-M M I � � h 11 : .��k A �" Y 1.t
ROAD IMPROVEMENT� `�� � ���� �,�,a ����� ��,�� �F_�,:� „ . �=eGp��:�,."� �� �:�. � � .,
AC Grindin ,4'wide machine< 1000sy $ 23.00 SY $0.00 $0.00 $0.00 $0.00
AC Grindin ,4'wide machine 1000-2000s $ 5.75 SY $0.00 $0.00 $0.00 $0.00
AC Grinding,4'wide machine>2000s $ 1.38 SY $0.00 $0.00 $0.00 $0.00
AC Removal/Dis osal/Re air $ 41.14 SY 468 $19,253.52 $0.00 $0.00 $0.00
Barricade,t e I $ 30.03 LF $0.00 $0.00 $0.00 $0.00
Barricade, pe III Permanent $ 45.05 LF $0.00 $0.00 $0.00 $0.00
Curb&Gutter, rolled $ 13.27 LF $0.00 $0.00 $0.00 $0.00
Curb&Gutter,vertical $ 9.69 LF 326 $3,158.94 1839 $17,819.91 $0.00 $0.00
Curb and Gutter,demolition and disposal $ 13.58 LF 15 $203.70 $0.00 $0.00 $0.00
Curb,extruded as halt $ 2.44 LF $0.00 $0.00 $0.00 $0.00
Curb,extruded concrete $ 2.56 LF $0.00 $0.00 $0.00 $0.00
Sawcut,as halt,3"depth $ 1.85 LF 370 $684.50 $0.00 $0.00 $0.00
Sawcut,concrete, er 1"de th $ 1.69 LF $0.00 $0.00 $0.00 $0.00
Sealant, asphalt $ 0.99 LF 345 $341.55 $0.00 $0.00 $0.00
Shoulder,AC, (see AC road unit rice $ - SY $0.00 $0.00 $0.00 $0.00
Shoulder, ravel,4"thick $ 7.53 SY $0.00 $0.00 $0.00 $0.00
Sidewalk,4"thick $ 30.52 SY $0.00 $0.00 $0.00 $0.00
Sidewalk,4"thick,demolition and disposal $ 27.73 SY $0.00 $0.00 $0.00 $0.00
Sidewalk, 5"thick $ 34.94 SY 200 $6,988.00 1036 $36,197.84 $0.00 $0.00
Sidewalk,5"thick,demolition and dis osal $ 34.65 SY 9 $311.85 $0.00 $0.00 $0.00
Si n, handicap $ 85.28 Each $0.00 $0.00 $0.00 $0.00
Stri in , er stall $ 5.82 Each $0.00 $0.00 $0.00 $0.00
Stripin ,thermoplastic, for crosswalk) $ 2.38 SF $0.00 $0.00 $0.00 $0.00
Striping,4"reflectorized line $ 0.25 LF $0.00 $0.00 $0.00 $0.00
Page 4 of 9 SUBTOTAL $30,942.06 $54,017.75 $0.00 $0.00
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
8�Drainage Facilities Quant. '
Unit Price Unit Quant. Cost Quant. Cost Quant. Cost Complete Cost
ROAD SURFACING`��'�;;4",RoCk�=2.5`base&1,.5,;tqp�Coul'S2)`�'<For'93 KCIi aCk=5"base&;, ,"N�irs��e) y; ' *� �p�h' ..��M�yu�r '.,,�; , � �� `'�?
?� t :��,����:»�°�i;���
For KCRS'93, (additional 2.5"base)add: $ 3.60 SY $0.00 $0.00 $0.00 $0.00
AC Overla , 1.5"AC $ 7.39 SY $0.00 $0.00 $0.00 $0.00
AC Overla ,2"AC $ 8.75 SY 643 $5,626.25 2625 $22,968.75 1075 $9,406.25 $0.00
AC Road,2",4"rock, First 2500 SY $ 17.24 SY 185 $3,189.40 2625 $45,255.00 1075 $18,533.00 $0.00
AC Road,2",4"rock,Qt . over 2500SY $ 13.36 SY $0.00 $0.00 $0.00 $0.00
AC Road, 3",4"rock, First 2500 SY $ 19.69 SY $0.00 $0.00 $0.00 $0.00
AC Road,3",4"rock,Qt .over 2500 SY $ 15.81 SY $0.00 $0.00 $0.00 $0.00
AC Road,5", First 2500 SY $ 14.57 SY $0.00 $0.00 $0.00 $0.00
AC Road,5",Qt .Over 2500 SY $ 13.94 SY $0.00 $0.00 $0.00 $0.00
AC Road,6", First 2500 SY $ 16.76 SY $0.00 $0.00 $0.00 $0.00
AC Road,6",Qt .Over 2500 SY $ 16.12 SY $0.00 $0.00 $0.00 $0.00
Asphalt Treated Base,4"thick $ 9.21 SY 185 $1,703.85 2625 $24,176.25 1075 $9,900.75 $0.00
Gravel Road,4"rock, First 2500 SY $ 11.41 SY $0.00 230 $2,624.30 $0.00 $0.00
Gravel Road,4"rock,Qt .over 2500 SY $ 7.53 SY $0.00 $0.00 $0.00 $0.00
PCC Road, 5", no base, over 2500 SY $ 21.51 SY $0.00 $0.00 $0.00 $0.00
PCC Road, 6", no base,over 2500 SY $ 21.87 SY $0.00 $0.00 $0.00 $0.00
Thickened Edge $ 6.89 LF $0.00 $0.00 $0.00 $0.00
Page 5 of 9 SUBTOTAL $10,519.50 $95,024.30 $37,840.00 $0.00
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
8�Drainage Facilities Quant.
Unit Price Unit Quant. Cost Quant, Cost Quant. Cost Complete Cost
DRAINAGE����(CPP=CorrugatedPlasticPipe,`I���wor�Equivalent) �� ���; ��� ,�;�orCuivertpr�ces, A3�r.aq �.� erti�a�H�`ssumea�;assittn���, , �'�ipriceas�soi�dpt��.; ���%����,�„�
Access Road, R/D
$ 16.74 SY $0.00 230 $3,850.20 $0.00 $0.00
Boilards-fixed $ 240.74 Each $0.00 $0.00 $0.00 $0.00
Bollards-removable $ 452.34 Each $0.00 $0.00 $0.00 $0.00
" CBs include frame and lid
CB T e I $ 1,257.64 Each 4 $5,030.56 15 $18,864.60 3 $3,772.92 $0.00
CB T e IL $ 1,433.59 Each $0.00 1 $1,433.59 $0.00 $0.00
CB T pe II,48"diameter $ 2,033.57 Each $0.00 1 $2,033.57 $0.00 $0.00
for additional depth over 4' $ 436.52 FT $0.00 1 $436.52 $0.00 $0.00
CB T pe II, 54"diameter $ 2,192.54 Each $0.00 2 $4,385.08 $0.00 $0.00
for additional de th over 4' $ 486.53 FT $0.00 2 $973.06 $0.00 $0.00
CB T e II,60"diameter $ 2,351.52 Each $0.00 $0.00 $0.00 $0.00
for additional depth over 4' $ 536.54 FT $0.00 $0.00 $0.00 $0.00
CB T e II,72"diameter $ 3,212.64 Each $0.00 $0.00 $0.00 $0.00
for additional de th over 4' $ 692.21 FT $0.00 $0.00 $0.00 $0.00
Throu h-curb Inlet Framework Add $ 366.09 Each $0.00 2 $732.18 $0.00 $0.00
Cleanout, PVC,4" $ 130.55 Each $0.00 49 $6,396.95 $0.00 $0.00
Cleanout, PVC,6" $ 174.90 Each $0.00 $0.00 $0.00 $0.00
Cleanout, PVC,8" $ 224.19 Each $0.00 $0.00 $0.00 $0.00
Culvert, PVC,4" $ 8.64 LF $0.00 $0.00 $0.00 $0.00
Culvert, PVC,6" $ 12.60 LF $0.00 $0.00 1202 $15,145.20 $0.00
Culvert, PVC, 8" $ 13.33 LF $0.00 $0.00 $0.00 $0.00
Culvert, PVC, 12" $ 21.77 LF $0.00 $0.00 $0.00 $0.00
Culvert,CMP,8" $ 17.25 LF $0.00 $0.00 $0.00 $0.00
Culvert,CMP, 12" $ 26.45 LF $0.00 $0.00 $0.00 $0.00
Culvert,CMP, 15" $ 32.73 LF $0.00 $0.00 $0.00 $0.00
Culvert, CMP, 18" $ 37.74 LF $0.00 $0.00 $0.00 $0.00 ,
Culvert,CMP,24" $ 53.33 LF $0.00 $0.00 $0.00 $0.00 ��
Culvert,CMP,30" $ 71.45 LF $0.00 $0.00 $0.00 $0.00
Culvert,CMP,36" $ 112.11 LF $0.00 $0.00 $0.00 $0.00
Culvert, CMP,48" $ 140.83 LF $0.00 $0.00 $0.00 $0.00
Culvert,CMP,60" $ 235.45 LF $0.00 $0.00 $0.00 $0.00
Culvert,CMP,72" $ 302.58 LF $0.00 $0.00 $0.00 $0.00
Page 6 of 9 SUBTOTAL $5,030.56 $39,105.75 $18,918.12 $0.00
Existing Future Public Private Bond Reduction*
Right-of-way Road Improvements Improvements
DRAINAGE CONTINUED &Drainage Facilities Quant.
Unit Price Unit Quant Cost Quant. Cost Quant. Cost - Com lete Cost -
Culvert, Concrete,8" $ 21.02 LF $0.00 $0.00 $0.00 $0.00 ,
Culvert,Concrete, 12" $ 30.05 LF $0.00 $0.00 $0.00 $0.00
Culvert,Concrete, 15" $ 37.34 LF $0.00 $0.00 $0.00 $0.00
Culvert,Concrete, 18" $ 44.51 LF $0.00 $0.00 $0.00 $0.00 li
Culvert,Concrete,24" $ 61.07 LF $0.00 $0.00 $0.00 $0.00 �I
Culvert, Concrete,30" $ 104.18 LF $0.00 $0.00 $0.00 $0.00
Culvert, Concrete,36" $ 137.63 LF $0.00 $0.00 $0.00 $0.00
Culvert, Concrete,42" $ 158.42 LF $0.00 $0.00 $0.00 $0.00
Culvert,Concrete,48" $ 175.94 LF $0.00 $0.00 $0.00 $0.00
Culvert,CPP,6" $ 10.70 LF $0.00 23 $246.10 $0.00 $0.00
Culvert, CPP, 8" $ 16.10 LF $0.00 $0.00 $0.00 $0.00
Culvert, LCPE, 12" $ 20.70 LF 379 $7,845.30 1153 $23,867.10 63 $1,304.10 $0.00
Culvert, CPP, 15" $ 23.00 LF $0.00 $0.00 $0.00 $0.00
Culvert, LCPE,24" $ 38.30 LF $0.00 147 $5,630.10 $0.00 $0.00
Culvert,CPP, 18" $ 27.60 LF $0.00 197 $5,437.20 $0.00 $0.00
Culvert, CPP,24" $ 36.80 LF $0.00 $0.00 $0.00 $0.00
Culvert, CPP, 30" $ 48.30 LF $0.00 $0.00 $0.00 $0.00
Culvert,CPP,36" $ 55.20 LF $0.00 $0.00 $0.00 $0.00
Ditchin $ 8.08 CY $0.00 $0.00 $0.00 $0.00
Interceptor Trench (1,436 base+ $ 25.99 LF $0.00 $0.00 $0.00 $0.00
French Drain (3'depth) $ 22.60 LF $0.00 $0.00 $0.00 $0.00
Geotextile, laid in trench, pol ro lene $ 2.40 SY $0.00 $0.00 $0.00 $0.00
Infiltration pond testin $ 74.75 HR $0.00 $0.00 $0.00 $0.00
Mid-tank Access Riser,48"dia, 6'dee $ 1,605.40 Each $0.00 $0.00 $0.00 $0.00
Pond Overtlow S illwa $ 14.01 SY $0.00 $0.00 $0.00 $0.00
Restrictor/Oil Se arator, 12" $ 1,045.19 Each $0.00 $0.00 $0.00 $0.00
Restrictor/Oil Separator, 15" $ 1,095.56 Each $0.00 $0.00 $0.00 $0.00
Restrictor/Oil Separator, 18" $ 1,146.16 Each $0.00 1 $1,146.16 $0.00 $0.00
Riprap,placed $ 39.08 CY 4 $156.32 $0.00 12 $468.96 $0.00
Tank End Reducer(36"diameter $ 1,000.50 Each $0.00 $0.00 $0.00 $0.00
Trash Rack, 12" $ 211.97 Each 1 $211.97 $0.00 $0.00 $0.00
Trash Rack, 15" $ 237.27 Each $0.00 $0.00 $0.00 $0.00
Trash Rack, 18" $ 268.89 Each $0.00 $0.00 $0.00 $0.00
Trash Rack,21" $ 306.84 Each $0.00 $0.00 $0.00 $0.00
Trash Rack,24" $ 344.79 Each $0.00 1 $344.79 $0.00 $0.00
Page 7 of 9 SUBTOTAL $8,213.59 $36,326.66 $1,773.06 $0.00
Existing Future Public Private Bond Reduction'
Right-of-way Road Improvements Improvements
8.Drainage Facilities Quant
Unit Price Unit Quant. Price Quant. Cost Quant. Cost Complete Cost
PARKING LOT SURFACING ,��,�� �'�'�'�'���'�°,� ;�x .,..,_ .. �,� �_;3 . ..., , � ����.��;" °�"�..� ���
:. . ,.
�� 4 . : �. . r ... _,�:�. �.. r � :
2"AC,2"top course rock&4"borrow $ 15.84 SY $0.00 $0.00 $0.00 $0.00
2"AC, 1.5" top course& 2.5"base course $ 17.24 SY $0.00 $0.00 $0.00 $0.00
4"select borrow $ 4.55 SY $0.00 $0.00 $0.00 $0.00
1.5"to course rock&2.5"base course $ 11.41 SY $0.00 $0.00 $0.00 $0.00
WRITE•-1N-ITEMS ''"`�` �'. -
, , , ,a , , �
A ;,r� � :� . ,a.:
. > � � � . ,
� t ... : l F•, . . . , .... �r.i Fe
� � �, yG� }�
�r -..�- .. �, ���Mk�`1�l'S?3 . � .,a a'� , �"9�� ��.'.. fl��'���'aX�S�-av�-n-�`�n��'wi�', -�'+,�,� .
�� a �e,
Detention Pond Retainin Wall $ 350 CY $0.00 294 $102,900.00 $0.00 $0.00
StormFilter,96"dia. Manhole $37,700 EA. $0.00 1 $37,700.00 $0.00 $0.00
LF $0.00 $0.00 $0.00 $0.00
EA. $0.00 $0.00 $0.00 $0.00
EA. $0.00 $0.00 $0.00 $0.00
EA. $0.00 $0.00 $0.00 $0.00
LF $0.00 $0.00 $0.00 $0.00
SF $0.00 $0.00 $0.00 $0.00
LF $0.00 $0.00 $0.00 $0.00
LF $0.00 $0.00 $0.00 $0.00
SUBTOTAL $0.00 $140,600.00 $0.00 $0.00
SUBTOTAL(SUM ALL PAGES): $65,526.72 $388,234.94 $178,616.70 $0.00
30%CONTINGENCY&MOBILIZATION: $19,658.02 $116,470.48 $53,585.01 $0.00
GRANDTOTAL: $85,184.74 $504,705.42 $232,201.72 $0.00
COLUMN: B C D E
Page 8 of 9
Original bond computations prepared by: LUBy R.JOUd@h, P.E. I
Name: Piper's Bluff Date: 4-Feb-13
PE Registration Number: 32162 Tel.#: (425)827-3063
Firm Name: D. R. STRONG Consulting Engineers, Inc.
Address: 10604 NE 38th P18Ce,#101; Kirkland,WA 98033 ProjectNo: LUA12-078, ECF, PP
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) $ 58,461.8 TEMPORARY OCCUPANCY'•'
Existing Right-of-Way Improvements (B) $ 85,184.7
Future Public Road Improvements&Drainage Fa (C) $ 504,705.4
Private Improvements (D) $ 232,201.7
Calculated Quantity Completed (E) $ -
Total Right-of Way and/or Site Restoration Bond* (A+B) $ 143,646.5
(First$7,500 of bond'shall be cash.)
Performance Bond"Amc(A+B+C+D) = TOTAL (T) $ 880,553.7 T x 0.30 $ 264,166.1 OR
Minimum bond'amount is$1000.
Reduced Performance Bond*Total*** (T-E) $ 880,553.7
Use larger of Tx30%or(T-E) (B+C)x
Maintenance/Defect Bond'Total 0.25= $ 147,472.5
NAME OF PERSON PREPARING BOND'REDUCTION Date:
*NOTE: The word"bond"as used in this document means any financial guarantee acceptable to King County.
**NOTE: KCC 27A authorizes right of way and site restoration bonds to be combined when both are required.
The restoration requirement shall include the total cost for ail TESC as a minimum,not a maximum. In addition,corrective work,both on-and off-site needs to be included.
Quantities shail reflect worse case scenarios not just minimum requirements. For example,if a salmonid stream may be damaged,some estimated costs for restoration
needs to be reflected in this amount. The 30%contingency and mobilization costs are computed in this quantity.
"'NOTE: Per KCC 27A,total bond amounts remaining after reduction shall not be less than 30%of the original amount(T)or as revised by major design changes.
SURETY BOND RIDER NOTE: If a bond rider is used,minimum additional pertormance bond shall be $ - (C+D)-E
REQUIRED BOND'AMOUNTS ARE SUBJECT TO REVIEW AND MODIFICATION BY DDES
STORMWATER FACILITY SUMMARY SHEET
Development Piper's Biuff Date Januarv 23, 2012
Location 1166 Hoquiam Avenue NE, Renton, Washinqton
ENGINEER DEVELOPER
Name Luay R. Joudeh, P.E. Name
Firm D. R. STRONG Consulting Firm WestPac Development, LLC
En ineers, Inc.
Address 10604 NE 38 Place, #101 Address 7449 W. Mercer Wa
Kirkland, WA 98033 Mercer Island, WA 98040
Phone (425) 827-3063 Phone (206) 770-6546
Developed Site: 4.98 acres
Number of lots 28
Number of detention facilities on site: Number of infiltration facitities on site:
vaults vaults
1 pond 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 Ma Creek May Creek
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_CONTECH Stormfilter
combined detentionNVQ vault sand filter vault (basic or large?)
combined detention/wetvault stormwater wetland
compost filter wetvault (basic or large?)
filter strip Wetvault
flow dispersion pre-settling pond
farm management plan flow-splitter catchbasin
landscape management plan
oil/water separator (baffle or coalescing plate?)
catch basin inserts:
G�2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 40 of 43
Drainage Report City of Renton
Manufacturer
pre-settling structure:
Manufacturer
DESIGN INFORMATION INDIVIDUAL BASIN
Water Quali design flow
Water Quali treated volume
Draina e basin s)
Onsite area (inlcudes fronta e 4.98
Offsite area 0
T e of Stora e Facilit Pond
Live Stora e Volume (required) 69,132
Predev Runoff Rate 2- ear 0.139
10- ear 0.241
100- ear 0.402
Developed Runoff Rate 2- ear 0.928
10- ear 1.12
100- ear 1.88
T pe of Restrictor Frop-Tee
Size of orifice/restriction No. 1 0.88
No. 2 1.50
No. 3 1.40
I
I I
;
02013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 41 of 43
Drainage Report City of Renton
SECTION X
OPERATIONS AND MAINTENANCE MANUAL
The Type 1-L catch basins have a one-foot deep sump, and the Type 2 catch basins
have a two-foot deep sump for sediment accumulation. These sumps should be
periodically checked and the sediment removed when accumulated to more than 1/3 of
the depth from the bottom of the basin to the invert of the lowest pipe into or out of the
basin. Grates should be cleaned when trash or debris of more than '/ cubic foot is
located immediately in front of the basin opening, or is blocking capacity of the basin by
more than 10%. Conveyance pipes should be periodically checked and cleaned when
more than 20% of the pipe diameter is obstructed by accumulated sediment or debris.
Accumulated sediment and stagnant conditions may cause noxious gases to form and
accumulate in the vertical wall pond. Sediment in the vertical wall pond should be
removed when the 1/2-foot sediment zone is full plus 6 inches. Sediment should be
tested for toxicants in compliance with current disposal requirements if visual or
olfactory indications of pollution are noticed. Water drained or pumped from pond prior
to sediment removal may be discharged to the downstream conveyance (i.e. roadside
ditch), if it is not excessively turbid (i.e. if water appears translucent when held to light),
and if floatable debris and visual petroleum sheens are removed. Excessively turbid
water (i.e. water appears opaque when held to light) should be discharged only after the
solids have been removed.
Floating debris and accumulated petroleum products should be removed as needed, but
at least annually. The floating oil should be removed from wetpond used as oil/water
separators when oil accumulation exceeds one inch.
The vertical wall pond should be maintained similarly to the vault with the following
additional requirements. Site vegetation should be trimmed as necessary to keep the
pond free of leaves and to maintain the aesthetic appearance of the site. Slope areas
that have become bare should be revegetated and eroded areas should be regraded
prior to being revegetated.
Perform inspections of all components quarterly during the first year of operation, then
annually thereafter. For more detailed maintenance instructions, refer to the standards
contained at the end of this section.
The maintenance of the Stormfilter vault is described in the following summary provided
by the manufacturer with annual maintenance recommendations.
:,2013 D. R.STRONG Consulting Engineers Inc. PipePs Bluff Plat Page 42 of 43
Drainage Report City of Renton I
__ __ _ ___
I
, �i
A���%\�TCA�.■a � Important: Inspection should be performed by a person who is
�����,����r� TheStormw.ee�Ma�gemrnt familiar with the StormFilter treatment unit. �
STORMWATER StormFilter ,
SOLUTIONS_ 1.If applicable, set up safety equipment to protect and notify �
surrounding vehicle and pedestrian traffic.
StormFilter Maintenance Guidelines 2.Visually inspect the external condition of the unit and take notes
Maintenance requirements and frequency are dependent on the concerning defects/problems.
pollutant load characteristics of each site,and may be required in 3.Open the access portals to the vault and allow the system vent.
the event of a chemical spill or due to excessive sediment loading. 4.Without entering the vault,visually inspect the inside of the unit,
Maintenance Procedures and note accumulations of liquids and solids.
Although there are other effective maintenance options,CONTECH 5. Be sure to record the level of sediment build-up on the floor of
recommends the following two step procedure: the vault, in the forebay,and on top of the cartridges. If flow
is occurring, note the flow of water per drainage pipe. Record
1. Inspedion: Determine the need for maintenance. all observations. Digital pictures are valuable for historical
2. Maintenance:Cartridge replacement and sediment removal. documentation.
Inspection and Maintenance Acti�ity Timing 6.Close and fasten the access portals.
' At least one scheduled inspection activity should take place per year 7. Remove safety equipment.
with maintenance following as warranted. 8. If appropriate,make notes about the local drainage area relative
First, inspection should be done before the winter season. During to ongoing construdion,erosion problems, or high loading of
which,the need for maintenance should be determined and, if other materials to the system.
disposal during maintenance will be required,samples of the 9.Discuss conditions that suggest maintenance and make decision
accumulated sediments and media should be obtained. as to weather or not maintenance is needed.
Second, if warranted, maintenance should be performed during Maintenance Decision Tree
periods of dry weather. The need for maintenance is typically based on results of the inspection.
In addition,you should check the condition of the StormFilter unit Use the following as a general guide. (Other factors,such as regulatory
after major storms for potential damage caused by high flows and requirements,may need to be considered)
for high sediment accumulation. It may be necessary to adjust the 1. Sediment loading on the vault floor. If>4"of accumulated
inspection/maintenance adivity schedule depending on the actual sediment,then go to maintenance.
operating conditions encountered by the system. 2.Sediment loading on top of the cartridge. If >1/4"of
Generally, inspection activities can be conducted at any time,and accumulation,then go to maintenance.
maintenance should occur when flows into the system are unlikely. 3.Submerged cartridges. If >4"of static�vater in the cartridge
Maintenance Activity Frequency bay for more that 24 hrs after end of rain event,then go to
P�laintenance is performed on an as needed basis, based on maintenance.
inspection. Average maintenance lifecycle is 1-3 years. The primary 4. Plugged media. If pore space between media granules is absent,
factor controlling timing of maintenance of the StormFilter is then go to maintenance.
sediment loading. Until appropriate timeline is determined, use the 5. Bypass condition. If inspection is conducted during an average
following: rain fall event and StormFilter remains in bypass condition
Inspection: (water over the internal outlet baffle wall or submerged
One time per year cartridges),then go to maintenance.
After major storms 6. Hazardous material release. If hazardous material release
(automotive fluids or other) is reported,then go to
Maintenance: maintenance.
As needed 7.Pronounced scum line. If pronounced scum line(say>_ t/4"
Per regulatory requirement thick)is present above top cap,then go to maintenance.
In the event of a chemical spill 8.Calendar Lifecycle. If system has not been maintained for 3
Inspection Procedures years,then go to maintenance.
Assumptions:
It is desirable to inspect during a storm to observe the relative
flow through the filter cartridges. If the submerged cartridges are No rainfall for 24 hours or more.
see�erely plugged,then typically large amounts of sediments will be No upstream detention (at least not draining into StormFilter).
present and very little flow will be discharged from the drainage Structure is online. Outlet pipe is clear of obstruction. Construction
pipes. If this is the case,then maintenance is warranted and the bypass is plugged.
cartridges need to be replaced.
Maintenance
Warning: In the case of a spill,the worker should abort inspedion Depending on the configuration of the particular system, workers
activities until the proper guidance is obtained. Notify the Will be required to enter the vault to perform the maintenance.
local hazard control agency and CONTE�H immediately.
To conduct an inspection:
1
Important: If vault entry is required, OSHA rules for confined space Method 2:
entry must be followed. A. Enter the vault using appropriate confined space protocols.
Filter cartridge replacement should occur during dry weathec It may
be necessary to plug the filter inlet pipe if base flow is occurring. B• Unscrew the cartridge cap.
Replacement cartridges can be delivered to the site or customers C. Remove the cartridge hood screws(3)hood and float.
facility. Contact CONTECH for more information. D. At location under structure access,tip the cartridge on its
Warning: In the case of a spill,the worker should abort side.
maintenance activities until the proper guidance is obtained. Notify
the local hazard control agency and CONTECH immediately. Important: Note that cartridges containing media other than
the leaf inedia require unscrewing from their threaded
To conduct cartridge replacement and sediment removal: connectors.Take care not to damage the manifold
1. If applicable, set up safety equipment to protect workers and connectors.This connector should remain installed in the
pedestrians from site hazards. manifold and capped if necessary.
2.Visually inspect the external condition of the unit and take notes E. Empty the cartridge onto the vault floor. Reassemble the
concerning defects/problems. empty cartridge.
3.Open the doors(access portals)to the vault and allow the system
to vent. F. Set the empty, used cartridge aside or load onto the hauling
truck.
4.Without entering the vault, give the inside of the unit, including
components,a general condition inspection. G. Continue steps a through E until all cartridges have been
5. Make notes about the external and internal condition of removed.
the vault. Give particular attention to recording the level of g, Remove accumulated sediment from the floor of the vault and
sediment build-up on the floor of the vault, in the forebay,and from the forebay. Use vacuum truck for highest effectiveness.
on top of the internal components.
9. Once the sediments are remo�ed, assess the condition of the
6. Using appropriate equipment offload the replacement cartridges vault and the connectors.The connectors are short sections
(up to 150 Ibs. each)and set aside. of 2-inch schedule 40 PVC,or threaded schedule 80 PVC that
7. Remove used cartridges from the vault using one of the should protrude about 1"above the floor of the vault. Lightly
following methods: wash down the vault interior.
Method 1: a. If desired,apply a light coating of FDA approved silicon
A. This activity will require that workers enter the vault to lube to the outside of the exposed portion ot the
remove the cartridges from the under drain manifold and connectors.This ensures a watertight connection between
place them under the vault opening for lifting {removal). the cartridge and the drainage pipe.
Unscrew(counterclockwise rotations)each filter cartridge
from the underdrain connector. Roll the loose cartridge,on b. Replace any damaged connectors.
edge,to a convenient spot beneath the vault access. 10. Using the vacuum truck boom,crane,or tripod, lower and
Using appropriate hoisting equipment,attach a cable from install the new cartridges.Take care not to damage connections.
the boom,crane,or tripod to the loose cartridge. Contact 11.Close and fasten the door.
CONTECH for suggested attachment devices. 1�. Remove safety equipment.
Important:Cartridges containing leaf inedia (CSF)do not 13. Finally,dispose of the accumulated materials in accordance with
require unscrewing from their connectors. Do not applicable regulations. Make arrangements to return the used
damage the manifold connectors.They should remain empty cartridges to CONTECH.
installed in the manifold and can be capped during the Material Disposal
maintenance activity to prevent sediments from entering The accumulated sediment must be handled and disposed of in
the under drain manifold. accordance with regulatory protocols. It is possible for sediments
B. Remove the used cartridges(up to 250 Ibs.)from the vault. to contain measurable concentrations of heavy metals and organic
chemicals.Areas with the greatest potential for high pollutant
Important:Avoid damaging the cartridges during removal and loading include industrial areas and heavily traveled roads.
installation. Sediments and water must be disposed of in accordance with
C. Set the used cartridge aside or load onto the hauling truck. applicable waste disposal regulations. Coordinate disposal of solids
D. Continue steps A through �until all cartridges have been and liquids as part of your maintenance procedure. Contact the
removed. local public works department to inquire how they disposes of their
street Uiaste residuals.
��2007 CONTECH Stormwater Solutions 800.925.5240
contechstormwateccom
Nothing in this catalog should be construed as an expressed warranty or an implied warranty of inerchantability or fitness for any particular purpose.
See the CONTECH standard quotation or acknowledgement for applicable warranties and other terms and conditions of sale.
The productls)described may be protected 6y one or more of the following US patents: 5,322,629;5,624,576;5,707,527;5,759,415;5,788,848;5,985.157;
6,027.639;6,350,374;6,406,218;6,611,720;6,511,555;6,649,048;6,991,114;6,998,038;7,186,058;related foreign patents or other patents pending.
2
APPENDIX A MAINTENANCE STANDARDS FOR PRIVATELY MAINTAINED DRAINAGE FACII.ITIES
NO. 3-CLOSED DETENTION SYSTEMS(PIPESfTANKS)
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Storage Area Plugged Air Vents One-half of tt�e cross section of a vent is blocked at Vents free of debris and
any point with debris and sediment sediment
Debris and Accumulated sediment depth exceeds 10%of the All sediment and debris
Sediment diameter of the storage area for'/z length of storage removed from storage area.
vault or any point depth exceeds 15%of diameter. '
Example:72-inch storage tank would require cleaning
when sediment reaches depth of 7 inches for more
than'/z length of tank.
Joints Between Any crack ailowing material to be transported into All joint between tank/pipe
Tank/Pipe Section facility sections are sealed
Tank Pipe Bent Any part of tank/pipe is bent out of shape more than TanW pipe repaired or replaced
Out of Shape 10%of iYs design shape to design.
Manhole Cover Not in Place Cover is missing or oniy partially in place.Any open Manhole is closed.
manhole requires maintenance.
Locking Mechanism cannot be opened by one maintenance Mechanism opens with proper
Mechanism Not person with proper tools.Bolts into frame have less tools.
Working than 3'z inch of thread(may not appfy to self-locking
lids.)
Cover Difficuft to One maintenance person cannot remove lid after Cover can be removed and
Remove applying 801bs of lift. Intent is to keep cover from reinstalled by one maintenance
sealing off access to maintenance. person.
Ladder Rungs King County Safety Office and/or maintenance person Ladder meets design standards
Unsafe judges that ladder is unsafe due to missing rungs, allows maintenance person safe
misalignment,rust,or cracks. access.
Catch Basins See"Catch Basins"Shndards No.5 See"Catch Basins"Standards
No.5
1998 Surface Water Design Manual 9/1/98
A-3
APPENDIX A MAINTEN.ANCE STANDARDS FOR PRNATELY MAINTAIIv'ED DRAINAGE FACILITIES
NO. 4-CONTROL STRUCTURE/FLOW RESTRICTOR
Maintenance Defect Condition When Maintenance is Needed Results Expected When
Component Maintenance is Pertormed
General Trash and Debris Distance between debris build-up and bottom of All trash and debris removed.
(Includes Sediment) orifice plate is less than 1-1/2 feet
Structura!Damage Structure is not securely attached to manhofe wall Structure securely attached to
and outlet pipe structure should support at least wall and ouUet pipe.
1,�00 Ibs of up or down pressure.
Structure is not in upright position(allow up to Structure in correct position.
109'o from plumb).
Connections to oudet pipe are not watertight and Connections to outfet pipe are
show signs of rust water tight;structure repaired or
replaced and works 2s
designed.
Any holes—otherthan designed holes—in the Structure has no holes other
structure. than designed holes.
Cleanout Gate Damaged or Missing Cleanout gate is not watertight or is missing. Gate is watertight and works as
� designed.
Gate cannot be moved up and down by one Gate moves up and down easily '
maintenance person. and is watertight.
Chain teading to gate is missing or damaged. Chain is in place and works as
designed.
Gate is rusted over 50%of its surface area. Gate is repaired or replaced to
meet design standards.. -
Orifice P(ate Damaged or Missing ConVol 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 Vash,debris,s?dim�nt,or vegetation Plate is free of all obstructions
blocking the plate. and works as designed.
Overflow Pipe Obstructions Any trash or debris blocking(or having the Pipe is free of all obstructions
potential of blocking)the overflow pipe. and works as designed.
Manhole See"Closed Detention Systems"Standards No.3 See"Closed Detention Systems'
Standards No.3
Catch Basin See°Catch Basins"Standards No.5 See'Catch Basins"Standards
No.5
9/1/98 1998 Surface�'��ater Desi�n Aianual
A-4
APPENDIX A MAIIVTENAIv'CE STANDARDS FOR PRIVATELY NIAINTAINED DRAL'VAGE FACILITTES
NO.5-CATCH BASlNS
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component Maintenance is pertormed
General Trash&Debris Trash or debris of more than 1/2 cubic foot which is No Trash or debris located
(Includes Sediment) located immediately in front of the catch basin immediately in front of catch
opening or is blocking capacity of the basin by basin opening.
more than 10%
Trash or debris(in the basin)that exceeds 1/3 the No trash or debris in the catch
depth from the bottom of basin to invert ihe lowest basin.
pipe into or out of the basin.
Trash or debris in any inlet or outlet pipe blocking Inlet and outiet pipes free of
more than 1/3 of its height trash or debris.
Dead animals or vegetation that could generate No dead animals or vegetation
odors that could cause complaints or dangerous present within the catch basin.
gases(e.g.,methane).
Deposits of garbage exceeding 1 cubic foot in No condition present which
volume would attract or support the
breeding of insects or rodents.
Structure Damage to Comer of frame extends more than 3/4 inch past Frame is even with curb.
Frame and/or Top Slab curb face into the street(If applicable).
Top slab has holes larger than 2 square inches or Top slab is free of holes and
cracks wider than 1/4 inch Cntent is to make sure cracks.
atl material is running into basin).
Frame not sitting flush on top slab,i.e.,separation Frame is sitting flush on top
of more than 3/4 inch of the frame from the top slab.
slab.
Cracks in Basin Walls/ Cracks wider than 1/2 inch and longer than 3 feet, Basin rep{aced or repaired to
Bottom any evidence of soil particles entering catch basin design standards.
through cracks,or maintenance person judges that
structura is unsound.
Cracks wider than 1/2 inch and longer than 1 foot N�cracks more than 1/4 inch
at the joint of any inleU outlet pipe or any evidence wide at the jant of inleVoutlet
of soil particles entering catch basin through pipe.
cracks.
SedimenU Basin has settled more than 1 inch or has rotated Basin replaced or repaired to
Misalignment more than 2 inches out of alignment. design standards.
1998 Surface Water Desi�►Manual 9/1/98
A-5
�PPENDIX A I�ZAINTENANCE ST?��TDARDS FO�PRIVATELY 47AINT:�INED DRAihAGE FACILI i fES
NO. 5-CATCH BASINS (CONTINUED�
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component Maintenance is performed
______._._
Fire Hazard Presence of chemicals such as naturaJ gas,oil and No flammable chemicals
gasoline. present
Vegetation Vegetation growing across and biocking more than No vegetation blocking open!
' • 10%of the basin opening. to basin.
Vegetation growing in inleUoutfet pipe joints that is No vegetation or root growth
more than six inches tall and less than six inches present.
apart.
Pollution Nonflammable chemicals of more than 1/2 cubic foot No pollution present other than
per three feet of basin length. surface film.
Catch Basin Cover Cover Not in Place' Cover is missing or only partially in place.Any open Catch basin cover is closed
catch basin requires maintenance. .
Locking Mechanism Mechanism cannot be opened by on maintenance Mechanism opens with proper
Not Working person with proper tools.Bolts into frame have less tools.
than 1/2 inch of thread.
Cover Difficult to One maintenance person cannot remove lid after Cover can be removed by one
Remove applying 80 Ibs.of lift;intent is keep cover from maintenance person.
seating off access to maintenance.
Ladder Ladder Rungs Ladder is unsafe due to missing rungs,misalignment, Ladder meets design standards
Unsafe rust,cracks,or sharp edges. and allows maintenance person
safe access.
Metal Grates Grate with opening wider than 7/8 inch. Grate opening meets design
(If Applicable) standards.
Trash and Debris Trash and debris that is blocking mare than 20%of Grate ftee of trash and debris. �
grate surtace. '
Damaged or Grate missing or broken member(s)of the grate. Grate is in place and meets
Missing. design standards.
NO. 6 DEBRtS BARR{ERS(E.G.,TRASH RACKS)
Maintenance Defect Condition When Maintenance is Needed Results Expected When
Components Maintenance is Performed.
General Trash and Debris Trash or debris that is plugging more than 20%of Barrier Gear to receive capacity
the openings in the barrier. flow.
Metal Damaged/Missing Bars are bent out of shape more than 3 inches. Bars in place with no bends more
Bars. than 314 inch.
Bars are missing or entire barrier missing. Bars in place according to
design.
Bars are loose and rust is causing 509'o deterioration Repair or replace barrier to
to any part of barrier. design standards.
9/1/98 1998 Surface Water Desi�n Manual
A-6
I�� APPENDIX A MAINTENANCE ST.ANDARDS FOR PRNATELY MAINTAINED DRAINAGE FACILITIES
NO. 7- ENERGY DISSIPATERS
Maintenance Defect Conditions When Maintenance is Needed Resuits Expected When
' Components Maintenance is Performed.
i� Extemal: �
� Rock Pad Missing or Moved Only one layer of rock exisis above native soil in Replace rocks to design
Rock area five square feet or larger,or any exposure of standards.
j native soil. .
'i Dispersion Trench Pipe Plugged with Accumulated sediment that exceeds 20%of the Pipe cleaned/flushed so that it
� Sediment design depth. matches design.
I�� Not Discharging Visuat evidence of water discharging at Trench must be redesigned or
� Water Properly concentrated p�ints along trench(normal condition rebuilt to standards.
is a"sheet flov�l'of water along trench).Intent is to
� prevent erosion damage.
� Perforations Over 1!2 of rforations in i e are lu ed with Clean or re lace erforated i e.
Pe P P P 99 P P P P
Plugged. debris and sediment
j Water Flows Out Maintenance person observes water flowing out Facility must be rebuilt or
I ' T�p of"Distributo�' during any storm fess than the design storm or its redesigned to standards.
Catch Basin. causing or appears likely to cause damage.
�I Receiving Area Water in receiving area is causing or has potential No danger of fandslides.
I Over-Saturated of causing tandsCde problems.
I �
i Intemal:
� Manhole/Chamber Wom or Damaged Struchtre dissipating flow deteriorates to 1/2 or Replace struciure to design '
Post.Baffles,Side original size or any concentrated wom spot standards. I
of Chamber exceeding on2 square foot which would make ,
structure unsound. '�
� Other Defects See"Catch Basins"Standard No.5 See"Catch Basins"Standard No. I'
5 �
il
II
i
�
!
_..__ _ _ __. ____ _ _ ._ __ _ _ _ _ _. _ _. _ __ _ _ _ . _
1998 Surface Water Design Manual 9/1i9�
A-7
APPENDIX A Iv1AL'�ITEN�\TCE STANDARDS FOR PRNA'F'ELY MAINTAIIv�ED DR�IN?GE FACIL i� S
NO.8-FENCING
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Components Maintenance is Performed
I Generai Missing or Broken Any defect in the fence that permits easy entry Parts in place to provide adequate
Parts to a facility. security.
� Erosion Erosion more than 4 inches high and 12-18 No opening under the f�nc�that
I inches wide permitting an opening under a exceeds 4 inches in height.
fence. �
Wire Fences Damaged Parts Post out of plumb more than 6 inches. Post plumb to within 1-1!2 inches.
Top rails bent more than 6 inches. Top rail free of bends greater than
1 inch.
, Any part of fence(inciuding 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.
Missing or loose barbed wire that is sagging Barbed wire in place with less than
more than 2-1/2 inches between posts. 3/4 inch sag between post.
Extension arm missing,broken,or bent out of Extension arm in place with no '
shape more than 1 1/2 inches. bends larger than 3/4 inch.
Deteriorated Paint or Part or parts that have a rusting or scaling Structurally adequate posts or
Protective Coating condition that has affected structural adequacy. parts with a uniform protective
� coating.
Openings in Fabric Openings in fabric are such that an 8-inch- No openings in fabric.
diameter ball could fit through.
NO. 9- GATES
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component , Maintenance is Performed
General Damaged or Missing Missing gate or locking devices. Gates and Locking devices in
Members place.
Broken or missing hinges such that gate cannot Hinges intact and I ubed. Gate is
be easily opened and closed by a maintenance woricing 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.
Openings in Fabric See`Fencing"Standard No.8 See"Fencing"Standard No. 8
9/1/98 1998 Surface�ti'ater Desisn I�1anua1
A-8
APPENDIX A MAINT�NANCE STAI�IDARDS FOR PRIVATELY MAINTAINED DRAINAGE FACII.I'TIES
N0. 10-CONVEYANCE SYSTEMS{PIPES & DtTCHES)
Maintenance Defect Conditions When Maintenance is Needed Results Expected When
Component Maintenance is Performed
Pipes Sediment&Debris Accumulated sediment that exceeds 20%of the Pipe cleaned of ail sediment
diameter of the pipe. and debris.
Vegetation Vegetation that reduces free movement of water Ali vegetation removed so water
through pipes. flows freely through pipes.
Damaged Protective coating is damaged;rust is causing Pipe repaired or replaced.
more than 50%deterioration to any part of pipe. I
Any dent that decreases the cross section area of Pipe repaired or replaced. I,
pipe by more than 20%. I
Open Ditches Trash&Debris Trash and debris exceeds 1 cubic foot per 1,000 Trash and debris cleared from
square feet of ditch and slopes. ditches. I
Sediment Accumulated sediment that exceeds 20%of the Ditch cleaned/flushed of all '�
design depth. sediment and debris so that it
matches design.
Vegetation Vegetation that reduces free movement of water Water flows freely through
through ditches. ditches.
Erosion Damage to See"Ponds"Standard No.1 See"Ponds"Standard No.1
Slopes
Rock Lining Out of Maintenance person can see native soil beneath Replace rocks to design
Pface or Missing(If the rock lining. standards.
Applicable).
Catch Basins See"Catch Basins:Standard No.5 See"Catch Basins"Standard
No.5
Debris Barriers See"Debris Barriers"Standard No.6 See"Debris Barriers"Standard
(e.g.,Trash Rack) No.6
NO. 1� -GROUNDS(LANDSCAPING)
Maintenance Defect Conditians When Maintenance is Needed Results Expected When
Component " Maintenance is Pertormed
General Weeds Weeds growing in more than 20%of the landscaped Weeds present in less than 5%
(Nonpoisonous) area(trees and shrubs only). of the landscaped area.
5afety Hazard Any presence of poison ivy or other poisonous No poisonous vegetation
vegetation. presentinlandscaped area.
Trash or Litter Paper,cans,bottles,totaling more than 1 cubic foot Area clear of litter.
� within a landscaped area(trees and shrubs only)of
1,000 square feet.
Trees and Shrubs Damaged Limbs or parts of trees or shrubs that are split or Trees and shrubs with less than
broken which affect more than 25%of the total 5%of total foliage with split or
foliage of the tree or shrub. broken limbs.
Trees or shrubs that have been blown down or Tree or shrub in place free of
knocked over. injury.
Trees or shrubs which are not adequately supported Tree or shrub in place and
or are leaning over,causing exposure of the roots. adequately supported;remove
any dead or diseased trees.
1998 Surface Water Design Manual 9!1/98
A-9
APPENDIX A MAINTENANCE STANDARDS FOR PRNATELY MAINTAINED DRAINAGE FACLITIES
NO. 12-ACCESS ROADS/EASEMENTS
Maintenance Defect Condition When Maintenance is Needed Results E�ected When
Component Maintenance is PerFormed
General Trash and Debris Trash and debris exceeds 1 cubic foot per 1,000 Roadway free of det '� �.`
square feet i.e.,trash and debris would fill up could damage tires.
one standards size garbage can.
Blodced Roadway Debris which could damage vehicie tires(glass Roadway free of debris wi�.
or metal). could damage tires.
My obstruction which reduces dearance above Roadway overhead clear tc .
road surface to less than 14 feet high.
Any obstruction resUicting the access to a 10 to Obstruction removed to atlow at
12 foot width for a dstance of more than 12 feet least a 12 foot access.
or any point restricting access to less than a 10
foot width.
Road Surface Settlement,Potholes, When any surface defect exceeds 6 inches in Road surface uniformty smooth
Mush Spots,Ruts depth and 6 square feet in area In general,any with no evidence of settlement,
surface defect which hinders or prevents potholes,mush spots,or n�ts.
maintenance access.
� Vegetation in Road Weeds growing in the road surface that are Road surface free of weeds taller
� SurFace more than 6 inches tall and less than 6 inches than 2 inches. ,
tall and less than 6 inches apart within a 400-
square foot area.
Modular Grid Build-up of sediment mildly contaminated with Removal of sediment and disp�:
Pavement petroleum hydrocarbons. in keeping with Health Departme
recommendations for mildly
contaminated soils or catch basi
sediments.
�I Shoulders and Erosion Damage Erosion within 1 foot of the roadway more than 8 Shoulder free of erosion and
' Ditches inches wide and 6 inches deep. matching the surrounding road.
Weeds and Brush Weeds and brush exceed 18 inches in height or Weeds and brush cut to 2 inche�
hinder maintenance access. in height or cleared in such a wa
as to allow maintenance access.
9/7/9R ]99R Serface«ater DeeiRr.�1�-
APPENDIX A
STORMWATER POLLUTION PREVENTION PLAN
i �
� ,
�--;
I ,
�2013 D. R.STRONG Consulting Engineers Inc. Piper's Bluff Plat Page 43 of 43
Drainage Report City of Renton
STORIVIWATER POLLUTION PREVENTION PLAN
For
PIPER'S BLUFF
Prepared For
WestPac Development, LLC
7449 W Mercer Way
Mercer Island, WA 98040
206-619-2992
Owner Developer Operator/Contractor
WestPac Development, LLC WestPac Development, LLC WestPac Development, LLC
7449 W Mercer Wa 7449 W Mercer Wa 7449 W Mercer Wa
Mercer Island, WA 98040 Mercer Island, WA 98040 Mercer Island, WA 98040
Project Site Location
1166 Hoquiam Ave NE, Lynnwood, Washington
Certified Erosion and Sediment Control Lead
Peter O'Kane
206-619-2992
SWPPP Prepared By
D.R. Strong Consulting Engineers, Inc.
10604 NE 38th Place, Suite 101
Kirkland, Washington 98033
Luay R. Joudeh, P.E.,Project Engineer
SWPPP Preparation Date
January 31, 2012
Approximate Project Construction Dates
April 2013
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STORMWATER POLLUTION PREVENTION PLAN
TABLE OF CONTENTS
1. INTRODUCTION .........................................................................................................1
2. SITE DESCRIPTION ...................................................................................................3
2.1 Existing Conditions.........................................................................................3
2.2 Proposed Construction Activities..................................................................3
3. CONSTRUCTION STORMWATER BMPS..................................................................5
3.1 The 12 BMP Elements .....................................................................................5
3.1.1 Element #1 — Mark C�earing Limits.............................................................5
3.1.2 Element#2 — Establish Construction Access .............................................5
3.1.3 Element#3 — Control Flow Rates...............................................................6
3.1.4 Element#4 — Install Sediment Controls .....................................................6
3.1.5 Element#5 — Stabilize Soils.......................................................................7
3.1.6 Element#6 — Protect Slopes......................................................................8
3.1.7 Element#7— Protect Drain Inlets...............................................................8
3.1.8 Element#8 — Stabilize Channels and Outlets ............................................9
3.1.9 Element#9— Control Pollutants.................................................................9
3.1.10 Element#10 — Control Dewatering...........................................................10
3.1.11 Element#11 — Maintain BMPs .................................................................10
3.1.12 Element#12 — Manage the Project ..........................................................11
3.2 Site Specific BMPs ........................................................................................13
3.3 Additional Advanced BMPs..........................................................................13
4.0 CONSTRUCTION PHASING AND BMP IMPLEMENTATION................................14
5.0 POLLUTION PREVENTION TEAM.........................................................................15
5.1 Roles and Responsibilities...........................................................................15
5.2 Team Members ..............................................................................................15
6.0 SITE INSPECTIONS AND MONITORING...............................................................16
6.1 Site Inspection...............................................................................................16
6.1.1 Site Inspection Frequency........................................................................16
6.1.2 Site Inspection Documentation.................................................................16
6.2 Stormwater Quality Monitoring ....................................................................17
6.2.1 Turbidity Sampling .........................................................................................17
6.2.2 pH Sampling ..................................................................................................18
6.2.3 Temperature Monitoring ...........................................................................18
7.0 REPORTING AND RECORDKEEPING ..................................................................19
7.1 Recordkeeping...............................................................................................19
7.1.1 Site Log Book...........................................................................................19
7.1.2 Records Retention....................................................................................19
7.1.3 Access to Plans and Records...................................................................19
7.1.4 Updating the SWPPP...............................................................................19 I
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7.2 Reporting .......................................................................................................19
7.2.1 Discharge Monitoring Reports..................................................................19
7.2.2 Notification of Noncompliance..................................................................20
7.2.3 Permit Application and Changes ..............................................................20
Appendices
AppendixA— Site Plans ................................................................................................21
Appendix B — Construction BMPs..................................................................................22
Appendix C —Alternative BMPs.....................................................................................23
Appendix D — General Permit........................................................................................24
Appendix E— Site Inspection Forms (And Site Log)......................................................25
Appendix F — Engineering Calculations.........................................................................32
Appendix A Site Plans
• 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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1. INTRODUCTION
This Stormwater Pollution Prevention Plan (SWPPP) has been prepared as part of the
NPDES stormwater permit requirements for the Piper's Bluff residential subdivision
�I project located at 1166 Hoquiam Ave NE, in Renton, Washington. The existing Site is
'� approximately 217,369 s.f. (4.990 ac). Total proposed Project area is 216,966 s.f.
(4.981 ac), which includes 10,337 s.f. (0.237 ac) for the right-of-way frontage
improvements on Hoquiam Avenue NE and excludes 10,740 s.f. (0.247 ac) of Tract "B"
(NGPA). The proposed development is the subdivision of the Site into 28 single-family
residential lots, with the associated infrastructure consisting of road frontage
improvements, plat access road, storm drainage conveyance system, detention and
water quality treatment facilities, water and sanitary sewer main extensions and sewer
lift station.
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
record keeping 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 March 20, 2012. This SWPPP was prepared based on the
requirements set forth in the Construction Stormwater General Permit, Stormwater
Management Manual for Western Washington (SWMMWW 2005). 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—
construction 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 — RECORDKEEPWG. This section describes the requirements I
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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2. SITE DESCRIPTION
2.1 Existing Conditions
The Site is 4.990 acres in size. It contains two single-family residences, three
out buildings and gravel driveway. The remainder of the Site is lawn,
landscaping, heavily vegetated with native grasses and shrubs, scatter trees,
berry bushes and moderately dense forest and underbrush. There is a Category
2 Wetland and a Class 4 Stream located near the northeast property corner. Site
runoff travels northeasterly and enters a Category 2 Wetland located near the
northeast property corner and then exits to north via Class 4 Stream. The Site
topography slopes generally to the east and northeast at approximately 2 to 15%.
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) and Alderwood
gravelly sandy loam with 15 to 30 percent slopes (AgD). Per the Manual, this soil
type is classified as "Till" material.
2.2 Proposed Construction Activities
The applicant is seeking approval to subdivide the Site into 28 single-family
residential lots through the City of Renton subdivision process.
All surface water runoff from Site pollution generating impervious surfaces
(roads, driveways and frontage improvement on Hoquiam Ave) will be collected
in a series of catch basins and pipes and conveyed to the detention and water
quality treatment facilities. The following summarizes details regarding Site
areas:
• Total Site area: 4.990 ac.
• Total Project area: 4.981 ac.
• Percent impervious area before construction: 5.5 %
• Percent impervious area after construction: 63.6 %
• Disturbed area during construction: 4.981 ac.
• Disturbed area that is characterized as impervious (i.e.,
access roads, staging, parking): 1.00 ac.
I • 2-year stormwater runoff peak flow prior to construction
(existing): 0.173 cfs
• 10-year stormwater runoff peak flow prior to construction
(existing): 0.289 cfs
• 2-year stormwater runoff peak flow during construction: 0.414 cfs
• 10-year stormwater runoff peak flow during construction: 0.624 cfs
• 2-year stormwater runoff peak flow after construction: 0.930 cfs
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• 10-year stormwater runoff peak flow after construction: 1.880 cfs
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3. 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 possible. The BMPs relevant to
marking the clearing limits that will be applied for this project include:
• Preserving Natural Vegetation (BMP C101)
• High Visibility Plastic or Metal Fence (BMP C103)
High-visibility orange plastic construction fencing will mark the clearing limits and
trees to be retained.
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 abo�e 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 installed south of the existing
residence's southwest corner, along the street frontage. This will allow
construction equipment access around the west and north sides of the structure.
The existing paved driveway will be utilized for parking for three vehicles, as well
as construction equipment and material staging.
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
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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.
3.1.3 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:
• No BMPs to be implemented
An Alternative BMP includes straw wattles and silt fencing down slope of
disturbed areas. The Project is unlikely to result in downstream erosion, due to
minimal Site grading, and construction runoff will not drain to a combined sewer
system.
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.
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:
• Straw Bale Barrier (BMP C230)
• Silt Fence (BMP C233)
• Straw Wattles (BMP C235)
• Storm Drain Inlet Protection (BMP C220)
Silt fencing and/or straw wattles will be installed down slope of disturbed areas.
Storm drain filter socks will be installed in the four catch basins adjacent to the
Site on the Ridge Road and 84th Ave NE frontages.
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Stormwater Pollution Prevention Plan
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 I�
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
j 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.
• Temporary Sediment Pond (BMP C241)
• 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:
Temporary and Permanent Seeding (BMP C120)
Mulching (BMP C121)
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Dust Control (BMP C140)
Mulching will be implemented on exposed soils as necessary for temporary
stabilization during construction. Permanent seeding and planting will stabilize
disturbed areas upon Project completion.
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.
_ 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
that minimizes erosion. The following specific BMPs will be used to protect
slopes for this project:
� • Temporary and Permanent Seeding (BMP C120)
• Straw Wattles (BMP C235)
Slope grading is confined to small areas to the east of the driveway, and
southwest and northwest of the residence. Grade changes are in the range of
one to two feet of cut or fill. Retaining walls are proposed west of the residence
in conjunction with a new walk-out patio from the basement. Straw wattles will
provide temporary slope stabilization. Permanent seeding and planting will be
implemented after Project completion.
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 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
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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
o Catch Basin Filter
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 to be implemented
o No temporary or permanent channels or outlets are proposed.
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.
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. 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 bel�w.
• Vehicles, construction equipment, and/or petroleum product
storage/dispensing:
o 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.
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�i o On-Site fueling tanks and petroleum product storage containers shall
� , include secondary containment.
I ; '
� o Spill prevention measures, such as drip pans, will be used when
conducting maintenance and repair of vehicles or equipment.
� o In order to perForm emergency repairs on Site, temporary plastic will be
placed beneath and, if raining, over the vehicle.
o Contaminated surfaces shall be cleaned immediately following any
discharge or spill incident.
• Demolition:
o Dust released from demolished sidewalks, buildings, or structures will
be controlled using Dust Control measures (BMP C140).
o 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).
o 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:
o 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).
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.
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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:
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
o 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.
o 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
o 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.
� o 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:
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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
o 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
o 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:
o Assess the Site conditions and construction activities that could impact
the quality of stormwater, and
o Assess the effectiveness of erosion and sedimen : ;
used to control the quality of stormwater discharges
o A Certified Erosion and Sediment Control Lead shaii be on-5ite or ,
call at all times.
o 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 imple���ented as soon as
possible.
• Maintaining an Updated Construction SWPPP
o This SWPPP shall be retained on-Site or within reasonable access to
the Site.
o 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.
o 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
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Stormwater Pollution Prevention Plan
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 I
(7) days following the inspection. ---
o Alternate dewatering 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 I
control issues that may cause a violation(s) of the NPDES ;
Construction Stormwater permit (as provided in Appendix D), the I
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
4.0 CONSTRUCTION PHASING AND BMP IMPLEMENTATION
The BMP implementation schedule will be driven by the construction schedule. The
following provides 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: 4/1/13
• Estimate of Construction finish date: 12/1/13
• Mobilize equipment on site: 4/1/13
• Mobilize and store all ESC and soil stabilization products: 4/1/13 I
• Install ESC measures: 4/1/13 �
• Install stabilized construction entrance: 4/1/13
• Begin clearing and grubbing: 4/1/13
• Demolish existing buildings: 4/1/13—4/26/12
• Begin Site Grading: 4/8/13
• End Site Grading 9/9/13
• Begin Utility Construction 9/9/13
• End Utility Construction 9/27/13
• Begin implementing soil stabilization and
sediment control BMPs throughout the site: 4/8/13
• Final landscaping and planting begins: 9/9/13
• Permanent erosion control measures (hydroseeding): 10/1/13
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Stormwater Pollution Prevention Plan
5.0 POLLUTION PREVENTION TEAM
5.1 Roles and Responsibilities
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 IUlembers
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 TBD
Lead(CESCL)
Resident Engineer N/A
Emergency Ecology Contact NW Regional Office 425.649.7000
Emergency Owner Contact TBD
Non-Emergency Ecology Contact TBD
Monitoring Personnel TBD
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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. Th� n�mA �n�± /�nnf�r} �„f�,r,,,at;,,n f,-.
the CESCL is provided in Section 5 of this SWPPP
Site inspection will occur in all areas disturbed .
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 I
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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6.2 Stormwater Quality Monitoring �
6.2.1 Turbidity Sampling �'
Monitoring requirements for the proposed project will include either turbidity or water '
� transparency sampling to monitor site discharges for water quality compliance with the
2005 Construction Stormwater General Permit (Appendix D). Sampling will be ,
conducted at all discharge points at least once per calendar week. '��
Turbidity or transparency monitoring will follow the analytical methodologies described
in Section S4 of the 2005 Construction Stormwater General Permit (Appendix D). The 'i
, key benchmark values that require action are 25 NTU for turbidity (equivalent to 32 cm I
transparency) and 250 NTU for turbidity (equivalent to 6 cm transparency). If the 25 ',
NTU benchmark for turbidity (equivalent to 32 cm transparency) is exceeded, 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 �
revisions to the SWPPP as necessary.
3. Sample discharge location daily until the analysis results are less than 25 �i
NTU (turbidity) or greater than 32 cm (transparency). �
If the turbidity is greater than 25 NTU (or transparency is less than 32 cm) but less than
250 NTU (transparency greater than 6 cm) for more than 3 days, additional treatment
BMPs will be implemented within 24 hours of the third consecutive sample that
exceeded the benchmark value. Additional treatment BMPs to be considered will
include, but are not limited to, off-site treatment, infiltration, filtration and chemical
treatment.
If the 250 NTU benchmark for turbidity (or less than 6 cm transparency) is exceeded 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 daily sampling until the turbidity is less than 25 NTU (or
transparency is greater than 32 cm).
3. Initiate additional treatment BMPs such as off-site treatment, infiltration,
filtration and chemical treatment within 24 hours of the first 250 NTU
exceedance.
4. Implement additional treatment BMPs as soon as possible, but within 7 days
of the first 250 NTU exceedance.
5. 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.
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6.2.2 pH Sampling
Stormwater runoff wiil be monitored for pH starting on the first day of any activity that
includes more than 40 yards of poured or recycled concrete, or after the application of
"Engineered Soils" such as, Portland cement treated base, cement kiln dust, or fly ash.
This does not include fertilizers. For concrete work, pH monitoring will start the first day
concrete is poured and continue until 3 weeks after the last pour. For engineered soils,
the pH monitoring period begins when engineered soils are first exposed to precipitation
and continue until the area is fully stabilized. '
Stormwater samples will be collected daily from all points of discharge from the site and '
measured for pH using a calibrated pH meter, pH test kit, or wide range pH indicator ',
paper. If the measured pH is 8.5 or greater, the following steps will be conducted: ,
1. Prevent the high pH water from entering storm drains or surFace water. I
2. Adjust or neutralize the high pH water if necessary using appropriate �',
technology such as CO2 sparging (liquid or dry ice). '
3. Contact Ecology if chemical treatment other than CO2 sparging is planned. I
Describe inspection results and remedial actions that are taken in the site log book and I
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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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 con�enience, 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 provided to the
public when requested in writing in accordance with permit condition S5.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.
7.2 Reporting
7.2.1 Discharge Monitoring Reports
If cumulative soil disturbance is 5 acres or larger: Discharge Monitoring Reports (DMRs)
will be submitted to Ecotogy monthly. If there was no discharge during a given
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monitoring period, the Permittee shall submit the form as required, with the words "No '
discharge" entered in the place of monitoring results. The DMR due date is 15 days ',
following the end of each month. I,
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 I
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. 'I
Any time turbidity sampling indicates turbidity is 250 nephelometric turbidity units (NTU) �I
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 S5.A ;,
(see Section 5.0 of this SWPPP for contact information). j
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
APPENDIX A - SITE PLANS
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APPENDIX B - CONSTRUCTION BMPS
Preserving Natural Vegetation (BMP C101)
, High Visibility Plastic or Metal Fence (BMP C103)
Stabilized Construction Entrance (BMP C105)
�I ` Wheel Wash (BMP C106)
Construction Road/Parking Area Stabilization (BMP C107)
Silt Fence (BMP C233)
Temporary and Permanent Seeding (BMP C120)
Mulching (BMP C121)
Dust Control (BMP C140)
Storm Drain Inlet Protection (BMP C220)
Outlet Protection (BMP C209
f �
O 2013 D. R.STRONG Consuking Engineers Inc. Page 22 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
—�
4.1 Source Cootrol BMPs
BMP C101: Preserving Natural Vegetation
Purpose
The purpose of presen�ing natural vegetation is to reduce erosion and surface runoff.
Conclitions of Use
Natural vegetation should be preserved on steep slopes, near perennial and intermittent
«�atercourses or s��ales, and on building sites in ���ooded areas.
Design and Installation Specifications
Fence or clearly mark areas around trees that are to be saved. Where feasible, do not disturb
ground within the dripline of trees that are to be saved.
Do not place fill of more than six inches depth within the dripline of trees that are to be saved.
If roots of plants intended to be saved must be cut due to excavations:
• Cut as few roots as possible, and cut them cleanly.
• Paint cut root ends with a wood dressing such as asphalt base paint.
• Backfill excavations in these areas as soon as possible.
i
Maintenance Standards
Inspect flagged and/or fenced areas regularly to make sure flagging or fencing has not been
removed or damaged. If the flagging or fencing has been damaged or visibility reduced, it shall
be repaired or replaced immediately and visibility restored.
If tree roots have been exposed or injured, "prune" cleanly with an appropriate pruning saw or
loppers directly above the damaged roots and recover with native soils. Treatment of sap
flo��ing trees (fir, hemlock, pine, soft maples) is not advised as sap forms a natural healing
barrier.
September 2010 Snohomish Counfy Drainage Manua! Volume!I-Construction Stormwater Pollufion Prevenfion 23
BMP C103: High Visibility Plastic or Metal Fence
Purpose
Fencing is intended to: (1) restrict clearing to approved limits; (2)prevent disturbance of
sensitive areas, their buffers, and other areas required to be left undisturbed; (3) limit
construction traffic to designated consh-uction entrances or roads; and, (4)protect areas where
inarlcing���ith survey tape may not pcovide adequate protection.
Conditions of Use
To establish clearing limits,plastic or metal fence may be used:
• At the boundary of sensitive areas,their buffers, and other areas required to be left
uncleared.
. As necessaty to control vehicle access to and on the site.
Design and Installation Specifications
High visibility plastic fence shall be composed of a high-density polyethylene material and shall
be at least four feet in height. Posts for the fencing shall be steel or wood and placed every 6 feet
on center(maximum}or as needed to ensure rigidity. The fencing shall be f�stened to the post
every six inches with a polyethylene tie. On long continuous lengths of fencing, a tension wire
or rope shall be used as a top stringer to pt�event sagging between posts. The fence color shall be
high visibility orange. The fence tensile st�•enb h shall be 360 lbs./ft. using the ASTM D4595
testing method.
Metal fences shall be designed and installed according to the manufacturer's specifications.
Metal fences shall be at least 3 feet high and must be highly visible.
Fences shall not be «�ired or stapled to h�ees.
Maintenance Standards
If the fence has been damaged or visibility reduced, it shall be repaired or replaced immediately
and �-isibility restored.
September 2090 Snohomrsh County Drainage Manual Volume!I- Construcfion Stormwater Pollution Prevention 25
BMP C105: Stabilized Construction Entrance
Purpose
Construction entrances are stabilized to reduce the ainount of sediment transported onto paved
roads by vehicles or equipment by constructing a stabilized pad of quarry spalls at entrances to
construction sites.
Conditions of Use
Construction entrances shall be stabilized wherever traf�c will be leaving a constt�uction site aud
tcaveling on paved roads or other paved areas within 1,000 feet of the site.
On large commercial,highway,and road projects, the designer should include enough extt•a
materials in the contract to allow for additional stabilized ent��ances not shown in the initial
SWPPP. It is difficult to determine exactly where access to these projects will take place;
additional materials tivill enable the contractor to install them where needed.
Design and Installation Specifications
See Figure 4.2 for details.Note: the 100' minimum length of the entrance shall be reduced to the
maximuin practicable size when the size or configuration of the site does not allow the full
length (100').
A separation geotextile shall be placed under the spalls to prevent fine sediment from pumping
up into the rock pad. The geotextile shall meet the specifications for moderate survivability set
forth in the 2008 WSDOT Standard Specifications, Section 9-33.I Geosynthetic Material
Requirements, Table l, and shall meet the Class A AOS specification in Table 2 of that
document
Consider eacly installation of the first lift of asphalt in areas that will paved; this can be used as a
stabilized entrance. Also consider the installation of excess concrete as a stabilized entrance.
During large concrete pours, excess concrete is often available for this purpose.
Hog fuel (wood-based mulch)may be substituted for or combined with quariy spalls in areas that
will not be used for permanent roads. Hog fuel is generally less effective at stabilizing
const�uction entcances and should be used only at sites where the amount of traffic is very
limited. Hog fuel is not recommended for entrance stabilization in urban areas. The
effectiveness of hog fuel is highly variable and it generally requires more maintenance than
quarry spalls. The inspector inay at any time require the use of quai-�•y spalls if the hog fuel is not
preventing sediment from being traciced onto pavement or if the hog fuel is being carried onto
pavement. Hog fuel is prohibited in permanent roadbeds because organics in the subgrade soils
cause degradation of the sub�ade support over time.
Fencing(see BN1Ps C103 and C104) shall be installed as necessary to restrict traffic to the
construction entrance.
Whenever possible, the entcance shall be consh•ucted on a firm, compacted subgrade. This can
substantially increase the effectiveness of the pad and reduce the need for maintenance.
September 20 i 0 Snohomish Ccur,ty Drainage f✓;anual 1io;ume 11- Constructron Storm�-vater PoNutior�Prever,fion 27
BMP C106: Wheel Wash
Purpose
Wheel washes reduce the amount of sediment transported onto paved roads by motor vehicles.
Conditions of Use
When a stabilized construction entrance{see BMP C 105) is not preventing sediment from being
tracked onto pavement.
Wheel washing is generally an effective BMP when installed with careful attention to
topography. For example, a wheel wash can be detrimental if installed at the top of a slope
abutting a right-of-way where the water from the dripping truck can run unimpeded into the
street.
Pressure washing combined with an adequately sized and surfaced pad with direct drainage to a
large 10-foot x 10-foot sump can be very effective.
Design and Installation Specifications
Suggested details are shown in Figure 4.3. Snohomish County may allow other designs. A
minimum of 6 inches of asphalt treated base (ATB) over crushed base material or 8 inches over a
good subgrade is recommended to pave the wheel wash.
Use a low clearance truck to test the wheel wash before paving. Either a belly dump or lowboy
will worlc well to test clearance.
Keep the water level from 12 to 14 inches deep to avoid damage to trucic hubs and filling the ,
truck tongues with water. '
Midpoint spray nozzles are only needed in extremely inuddy conditions.
Wheel wash systems should be designed with a small grade change, 6 to I2 inches for a 10-foot-
wide pond,to allow sediment to flow to the low side of pond to help prevent re-suspension of
sediment. A dt•ainpipe with a 2-to 3-foot riser should be installed on the low side of the pond to
allow for easy cleaning and refilling. Polymers may be used to profnote coagulation and
flocculation in a ciosed-loop system. Polyacrylamide (PAM) added to the wheel wash water at a
rate of 0.25 -0.5 pounds per 1,000 gallons of water increases effecti��eness and reduces cleanup
time. If PAM is already being used for dust or erosion control and is being applied by a water
tc•uck,the same truck can be used to change the wash water.
Maintenance Standards
The wheel wash should stact out the day with fi�esh water.
The wash water should be changed a minimum of once per day. On large earthwork jobs where
more than 10-20 trucics per hour are expected, the��vash water��ill need to be changed inore
often. Wheel vvash or tire bath t��astewater shall be discharged to a sepat•ate on-site treatment
Sepfember2010 Snohomish County Drairage P"'anual Voiume Jl-Construction Stornn^�a'erPollufion Prevenfion 29
system, such as closed-loop recirculation or land application, or to the sanitary sewer with proper
local sewer district approval.
A
"Schedule 40
1 Yz'schedule 40 for sprayers
�
M
� �
2% 5:1 5:1 ( I 2%
Slope Slope Slope Slope
II
1�1
II
SIApe
Wheel Wash Plan
15 15 20' 15 50' �
� �
Elevation View
,Water level
�1g ( - 1:1 Slope
i
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�______.�.i�J
Section A-A i
N.T.S. '
Figure 4.3 Wheel Wash
Notes: I'
1. Asphalt construction entrance 6 in.aspl�alt treated base(ATB),
2. 3-inch trash pump�vitlz floats on die suction hose.
3. Midpoint spray nozzles,if needed.
4. G-inch sewer pipe with butferfly valves. Bottom one is a drain. Locate top pipe's invert 1 foot above
bottom of wheel wash.
5. 8 foot x 8 foot sump with 5 feet of catch. Build so can be cleaned with tracld�oe.
6. Asphalt curb on the low road side to direct water back to pond.
7. 6-inch sleeve under road.
8. Ball valves.
9. 15 foot.ATB apron to protect ground from splashing«rater.
September 2090 Snohomish County Drainage Manua! Volume 11-Construcfion Stormwater Pollufion Preventron 30
B�ZP C107: Construction Road/Parlcing Area Stabilization
Purpose
Stabilizing subdivision roads,parlcing areas, and other onsite vehicle transpoi-tation routes '
immediately aftec grading reduces erosion caused by construction traffic or runoff.
Conditions of Use
Roads o►�parlcing areas shall be stabilized wherever they are constructed,whether permanent or
temporary, foi•use by construction tra�c.
Fencing(see BMPs C 103 and C 104)shall be installed, if necessary,to limit the access of
vehicles to only those roads and parking areas that are stabilized.
Design and Installation Specifications
On areas that will receive asphalt as pa�-t of the project, install the first lift as soon as possible.
A 6-inch depth of 2- to 4-inch crushed rock, gravel base, or crushed surfacing base course shall
be applied immediately after grading or utility installation. A 4-inch course of asphalt treated
base (ATB)may also be used, or the road/parlcing area may be paved. It may also be possible to
use cement or calcium chloride for soil stabilization. If cement or cement kiln dust is used for
roadbase stabilization,pH monitoring and BMPs are necessary to evaluate and minimize the
effects on stormwater. If the area will not be used for permanent roads,parlcing areas, or
structures, a 6-inch depth of hog fuel may also be used, but this is lilcely to require more
inaintenance. Whenever possible, construction roads and parking areas shall be placed on a fn-m,
compacted subgrade.
Temporary road gradients shall not exceed 15 percent. Roadways shall be carefully graded to
drain. Drainage ditches shall be provided on each side of the roadway in the case of a crowned
section, oi�on one side in the case of a super-elevated section. Drainage ditches shall be directed
to a sediment control BMP.
Rather than relying on ditches, it may also be possiUle to grade the road so that runoff sheet-
flows into a heaviiy vegetated area with a well-developed topsoil. Landscaped areas are not
adequate. If this area has at least 50 feet of vegetation,then it is generally preferable to use the
vegetation to treat runoff,rather than a sediment pond or trap. The 50 feet shall not include
wetlands. If ilznoff is allowed to sheetflow through adjacent vegetated areas, it is vital to design
the roadways and parlcing areas so that no concentrated tunoff is created.
Storin drain inlets shall be protected to prevent sediment-laden water entering the storm dcain
system (see BMP C220).
11�Zaintenance Standards
Inspect stabilized areas regularly,especially after large storm events.
Crusl�ed rocic, gravel base,hog fuel, etc. shall be added as required to maintain a stable driving ,
surface and to stabilize any areas that have eroded.
September 2090 Snohornish Counfy Drainage fJanua! Volume ll-Consfruction Storm�a�ater Pol/ution Prevention 39
Fol(o��-ing construction, these are.as shall be i•estored to pre-constcuction condition or better to
prevent future ei•osion
i
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Sepfember 2o10 Snohomish County Drainage Manua! Volume U-Construcfion Stormwater Po!lution Prevention 32
BMP C233: Silt Fence
Purpose
Use of a siit fence reduces the transpoit of coarse sediinent fi•om a construction site by providing
a temporary physical barrier to sediment and reducing the runoff velocities of overland flow.
See Figure 4.19 for details on silt fence construction.
Conditions of Use
Silt fence may be used downslope of all disturbed areas.
Silt fence is not intended to treat concentrated flows, nor is it intended to treat substantial
atnounts of overland flow. Any concentrated flows must be conveyed tluough the drainage
system to a sediment pond. The only circumstance in which overland flow can be treated solely
by a silt fence, rather than by a sediment pond, is when the area draining to the fence is one acre
or less and flow rates are less than 0.� cfs.
Silt fences should not be constructed in streams or used in V-shaped ditches. They are not an
adequate method of silt control for anything deeper than sheet or overland flow.
Design and Installation Speci�cations
Drainage area of 1 acre or Iess or in combination with sediment basin in a larger site.
Maximum slope steepness (normal (pecpendicular) to fence line) 1:1.
Maximum sheet or overland flow path length to the fence of 100 feet.
No flows greater than 0.5 cfs.
The geotextile used shall meet the standards set forth in 2008 WSDOT Standard Specifications,
Section 9-33.1 Geosynthetic Matet•ial Requirements, Table 6.
Standard strength fabrics shall be suppoi�ted with wll•e mesh, chicken wire, 2-inch x 2-inch wire,
safety fence, or jute mesh to increase the strength of t1�e fabric. Silt fence materials are available
that have synthetic m.esh backing attached.
Filter fabric material shall contain ultcaviolet ray inhibitors and stabilizers to provide a minimum
of six months of expected usable construction life at a temperature range of 0°F. to 120°F.
100 percent biodegradable silt fence is available that is str•ong, long lasting, and can be left in
place after the project is completed.
Standard Notes for construction plans and specifications follow. Refer to Figure 4.19 for
standard silt fence details.
The contractor shall install and maintain temporaiy silt fences at the locations shown in the
Plans. The silt fences shall be constructed in the areas of clearing, grading, or drainage prior to
starting those activities. A silt fence shall not Ue considered temporary if the silt fence must
function beyond the life of the contract. The silt fence shall prevent soil carried by runoff water
from going beneath,through, or over the top of the silt fence, but shall allow the water to pass
tht•ough the fence.
September 2010 Snohomish County Drainage Manual Volume Il-C�nstruction Stormwater Poilution Prevention 107
��... .,,<<< i�,����< <�.:l�i:���� ��,. 1���'� �1 _��L ���,�.. .����_i � � _ ..��i <<<��, _i« �i���:�i�i.�iiL ii � _ii���i � � _.
feet above the original ground surface.
The geotextile shall be sewn together at the point of manufacture, or at an approved location as
determined by the Engineer,to form geotextile lengths as required. All sewn seams shall be
located at a support post. Alternatively,two sections of silt fence can be overlapped,provided
the overlap is long enough and that the adjacent fence sections are close enough together to
prevent silt laden water from escaping through the fence at the overlap.
The geotextile shall be attached on the up-slope side of the posts and support system with
staples,wire, or in accordance with the manufacturer's recominendations. The geotextile shall be
attached to the posts in a manner that reduces the potential for geotextile tearing at the staples,
wire, or other connection device. Silt fence back-up support for the geotextile in the forin of a
wire or plastic mesh is dependent on the propei-ties of the geotextile selected for use. If wire or
plastic bacic-up mesh is used,the mesh shall be fastened securely to the up-slope of the posts
with the geotextile being up-slope of the mesh back-up support.
The geotextile at the bottom of the fence shall be buried in a trench to a minimum depth of 4
inches below the ground surface. The trench shall be bacl�lled and the soil tamped in place
over the buried poi�tion of the geotextile, such that no flo�v can pass beneath the fence and
scouring cannot occur. When wire or polymeric bacic-up support mesh is used,the wire or
polymeric mesh shall extend into the trench a minimum of 3 inches.
The fence posts shall be placed or driven a minimum of 18 inches. A minimum depth of 12
inches is allowed if topsoil or other soft subgrade soil is not present and a minimum depth of 18
inches cannot be reached. Fence post depths shall be increased by 6 inches if the fence is located
on slopes of 3:1 or steeper and the slope is peipendicular to the fence. If required post depths
cannot be obtained, the posts shall be adequately secured by bracing or guying to prevent
overtuining of the fence due to sediment loading.
Silt fences shall be located on contour as much as possible, except at the ends of the fence,where
the fence shall be turned uphill such that the silt fence captures the runoff water and prevents
water fi•oin flowing around the end of the fence.
If the fence must cross contours,with the exception of the ends of the fence, gravel checic dams
' placed peipendicular to the back of the fence shall be used to minimize concentrated flow and
erosion along the back of the fence. The gi•avel checic dams shall be approximately 1-foot deep
' at the bacic of the fence. It shall be continued perpendicular to the fence at the same elevation
until the top of the check dam intercepts the ground siuface behind the fence. The gravel checic
dams shall consist of crushed surfacing base course, gravel backfill for walls, or shoulder ballast.
The gravel checic dams shall be located every 10 feet along the fence where the fence must cross
contours. The slope of the fence line where contours must be crossed shall not be steeper than
3:1.
Wood, steel or equivalent posts shall be used. Wood posts shall have minimum dimensions of 2
inches by 2 inches by 3 feet minimum length, and shall be fi•ee of defects such as knots, splits, or
gouges. Steel posts shall consist of either size No. b rebar or larger,ASTM A 120 steel pipe with
a minimuin diameter of 1-inch,U, T,L; ot� C shape steel posts with a minimum weiglit of 1.35
lbs./ft. or other steel posts having equivalent strength and bending resistance to the post sizes
listed. The spacing of the suppoit posts sl�all be a maximum of 6 feet.
September 2010 Snohonush County Drainage fJlanual Volume ll-Consfruciion Storrmvater Pollut�on Prevention 908
Fence back-up support, if used, shall consist of steel wire with a maximum mesh spacing of 2
inches, or a prefabricated polymeric mesh. The stcength of the wire or polymeric mesh shall be
equivalent to or greater than 180 lbs. grab tensile st�•ength. The polymeric mesh must be as
resistant to ultraviolet radiation as the geotextile it supports.
Silt fence installation using the slicing method specification details follow. Refer to Figure 4.20
� for slicing method details.
"I'he base of both end posts must be at least 2 to 4 inches above the top of the silt fence fabric on
the middle posts for ditch checics to drain properly. Use a hand level or string level, if necessary,
to mark base points before installation.
Install posts 3 to 4 feet apart in critical retention areas and 6 to 7 feet apart in standard
applications.
Install posts 24 inches deep on the downstream side of the silt fence, and as close as possible to
the fabric, enabling posts to suppoi�t the fabric from upstream water pressure.
Install posts with the nipples facing away from the silt fence fabric.
Attach the fabric to each post with three ties, all spaced within the top 8 inches of the fabric.
Attach each tie di:gonally 45 degrees through the fabric,with each puncture at least 1 inch
vet-tically apart. In addition, each tie should be positioned to hang on a post nipple when
tightening to prevent sagging.
Wrap approximately 6 inches of fabric around the end posts and secure with 3 ties.
No more than 24 inches of a 36-inch fabric is allowed above ground level.
The rope lock system must be used in all ditch check applications.
The installation should be checiced and coi�ected for any deviation before compaction. Use a
flat-bladed shovel to tuck fabric deeper into the ground if necessary.
Compaction is vitally iinportant for effective results. Compact the soil immediately next to the
silt fence fabric with the fi•ont wheel of the tcactor, slcid steer, or roller exerting at least 60 pounds
per square inch. Compact the upstream side first and then each side twice for a total of folu�
trips.
Mainte�iance Standards
If concentrated flows are evident uphill of the fence,they must be intercepted and conveyed to a I
sediment pond.
It is important to checic the uphill side of the fence for signs of the fence clogging and acting as a
ban•ier to flow and then causing channelization of flows parallel to the fence. If this occurs, �
replace the fence or remove the trapped sediment.
Sediment deposits shall either be removed when the deposit reaches approximately one-third the
height of the silt fence, or a second silt fence shall be installed.
If the filter fabric(geotextile)has deteriorated due to ultraviolet brealcdown, it shall be replaced.
September 201 D Snohomish County Orainage Manual Volume!!-Consfruction Sformwater Po!lution Preventron 109
- --- ----- — -----,i
Joints in filter fabric shall be spliced at
posts.Use staples,wire rings or 2^Xp°by 14 Ga.wire or ,
equivalent to attach fabric to posts equivalent if standard
strength fabric used
� �� � Fiiter fabric—
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7�-6'max�� � � Minimum 4"x4'trench '�J -�� E
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Backfill trench wfth native soll �
� Post spacing may be increased or 3/4"-1.5"washed gravel
to 8'if wire backing is used
2"x2"wood posls,steel fence
posts,or equivalent
Figure 4.19—Silt Fence
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September 2010 Snohomish Counfy Drainage Manual Volume Il- Consfruction Sformv✓afer Pollution Prevention 190
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` � �•F4Ay�scA II�a+�P°r�.�d U�r+�wJ'•.
Na more ihwi 24'oi a 38'tabric u�.ut�+r�tw��i�sot,r:.
is eltowed ebova ground.
Rd ot s�R fante
�..�. dppatlnn
Posl
iiad9ed
aRe1
cantpaCdOn
fakac
� . � �°�rt° Iil Fcrwv
��++�
�j�` � . � ��� � �
�i ti� \ �.4-}.,?:- :ti .., '0.-+.pj5�/ ,s ��
� ��f ��~�'t�i��i��, '���'� Z��RLRI`J, y JC• �Y��
.�� .��� . � '
� �r;l��vOE,�+��i ��i � � . i
i�t,'ir,�,c r���i'/ �if s�;o� ��,��.>: .
.�.'��T� c.•.i,�;:y ,., .. .
'
Hot�xRd shbW PdM gen�blede
[16 mm�.�2►@ (1 g tnm vdei� .
Cwnp�eced ku�eladai
ViDr�taryr pdow h na acr�ptabie bocauso oi h�Mai cs�mp�c�lon
Figure 4.20—Silt Fence Installation by Slicing Method
Sepfember 2090 Snohomrsh County Drainage Manual Vo!ume I!- Construction Stormwater Pollution Prevention 99 9
BMP C120: Temporary and Permanent Seeding ,
NOTE: Small projects permitted in accordance with SCC 30.63A.810 shall only use �'�
BMPs in this section that do not require the in��olvement of a licensed engineer. !,
Purpose I'
Seeding is intended to reduce erosion by stabilizing e�posed soils. A well-established ve�etative �
cover is one of the most effective methods of reducin� erosion. ',
Conditions of L'se !
Seeding may be used t}1i•oughout thc project on di�t�:rt�cd ��r��l� that h���c rc:�,hed final ��rade c�r i
that will remain unwot•lced for mot•e than 30 days. �
Channels that will be vegetated should be installed bct'�r� maj�r ca���h�:.��>>�I: a�ld ]l��,lru�;c�lc�i �
with a Bonded Fiber Matrix. The vegetation should be well established (i.e., 75 percent cover�
before water is allowed to flow in the ditch. With channels that will have high flows, erosion
control blankets should be installed over the hydt�oseed. If vegetation cannot be established f��;,i» !
seed before water is allowed in the ditch, sod should be installed in the bottom of the ditch o�e� '
hydromulch and blankets.
' Retention/detention ponds should be seeded as required.
� MUIC�IIST'CCjl'i� 1 �r �I� r;.,��� � ._.,i �r,�,��-�CT` �� . � . .. � � �__ � � '1�,� ..JI��:�-�i� � . �
- due to runoff. I
All disturbed ... _:� :.._.. : .,� , � ..
� 1��_ , . ,�: __ __ � � _�;��� . � , �_ '�� �,;
completed by the end of September. � �: �: � __ _ . � � �..!� , . I
provide more than average protectior
. At final site stabilization,all disturbc . .� " �� � �.I . r. , . `�..... . _.. i� i�� , _..�.i
and mulched. Final stabilization means the completion of all soil distui•bing activities at the site !
and the establishment of a permanent vegetative cover, or equivalent permanent stabilization
measures (such as pavement,riprap, gabions or geotextiles)which wi11 prevent erosion.
Design and Installation Specificatious
Seeding should be done during those seasons most conducive to growth and will vary with the
climate conditions of the region. Local experience should be used to determine the appropriate
seeding periods.
The optiinum seeding windows for western Washington are April 1 through June 30 and
September 1 through October 1. Seeding that occucs between July 1 and August 30 will require
urigation until 75 percent grass cover is established. Seeding that occuis between October 1 and
March 30 will require a mulch or plastic cover until 75 percent grass cover is established.
To prevent seed from being washed away, confirm that all required surface water cont�ol
measures have been installed.
September 201 D Snohomish County Drainage Manua! Volume I!-Construcfion Sformwater Po!lution Prevention 33
The seedbed should be firm and rough. All soil should be roughened no matter what the slope.
If compaction is required for engineering purposes, slopes must be track walked before seeding.
Bacicblading or smoothing of slopes greater than 4:1 is not allowed if they are to be seeded.
New and more effective restoration-based landscape practices i•ely on deeper incorporation than
that provided by a simple single-pass rototilling treatment. Wherever pr�actical the subgrade
should be initially ripped to improve long-term permeability, infiltration, and water inflow
qualities. At a minimum,permanent areas shall use soil amendments to achieve organic matter
and permeability performance defined in engineered soilllandscape systems. For systems that
are deeper than 8 inches the rototilling process should be done in multiple lifts, or the prepared
soil system shall be prepaf�ed properly and then placed to achieve the specified depth.
Organic matter is the most appropriate form of"fertilizei"because it provides nutrients
{including nitcogen,phosphorus,and potassium) in the least water-soluble form. A natural
system typically releases 2-10 percent of its nutrients annually. Chemical fertilizers have since
been formulated to simulate what organic matter does naturally.
In general, 10-4-6 N-P-K (nitrogen-phosphorus-potassium) fertilizer can be used at a rate of 90
pounds per acre. Slow-release fertilizers should always be used because they are more efficient
and have fewer environmental impacts. It is recommended that areas being seeded for final
landscaping conduct soil tests to determine the exact type and quantity of fertilizer needed. This '
will prevent the over-application of fertilizer. Fertilizer should not be added to the hydromulch '�
machine and agitated more than 20 minutes before it is to be used. If agitated too much, the
slow-release coating is destroyed.
There are numerous products available on the market that talce the place of chemical fertilizers. '
These include several with seaweed ext�•acts that are beneficial to soil microbes and organisms.
If 100 percent cottonseed meal is used as the mulch in hydroseed, chemical fertilizer may not be ',
necessaiy. Cottonseed meal is a good source of long-term, slow-release, available nitrogen. '
Hydroseed applications shall include a minimum of 1,500 pounds per acre of mulch with 3
percent tackifier. Mulch may be made up of 100 percent: cottonseed meal; fibers made of
wood, recycled cellulose, hemp, and Icenaf; compost; or blends of these. Tackifier shall be plant-
based, such as guar or alpha plantago,or chemical-based such as polyacrylamide or pol�in�r�, i
Any inulch or tacicifier product used shall be installed per inanufacturer's instructions. i
- Generall}�, mulches c��r��� in s�-�(1 E���und t�e��. Seed and fertilizer �i�c add�d at tiin� ��f
application.
MUlC�l1S ZIV�,��t\� I'�'�1111f'CU l;��l' .����i! IC!i��l �'..'1 ,'� �iJ`i!��� !1 I���' �il _�'�:� ,�" � , '�illl�[:lf�::C�',1��V�
by hydraseeding. �,
� On steep slopes, 13���.��i:�1 l�ih�r �i�:u��� i,!;1�`�1) �_,r `�l��ir.u.ic.�il�� 13u;��i�;( I��il�.r �I�,iria ���1L31���1) �
products should be used. BFM/MBFM products are applied at a minimum rate of 3,000 poun ' �
per acre of mulch with approximately 10 percent tacicifier. Application is made so that a �
ininimum of 95 percent soil coverage is achieved. Products shail be installed per mantif�crn,�����
_ instructions.
Areas to be permanently landscaped shall provide healthy topsoil that reduces the neeci
fertilizers, impt�oves overall topsoil quality, provides for better vegetal health and vitality,
improves hydroIogic characteristics, and reduces the need for irrigation
September 2010 Snohomish County Drarnage Manual Volume ll-Constructron Stormwater PoUution Prevention 34
Compost, if used, shall meet specifications for Grade A quality compost in Ecology Publication
94-03 8.
Areas that will be seeded only and not landscaped may need compost or meal-based mulch
included in the hydroseed in order to establish vegetation. Native topsoil should be re-installed ',
on the disturbed soil surface befoce application.
Seed that is installed as a temporary measure inay be installed by hand if it will be covered by
straw,mulch, or topsoil. Seed that is installed as a permanent measure may be installed by hand
on small areas(usuaIly less than 1 acre)that will be covered with mulch,topsoil,or erosion
blankets. The seed mixes listed below include recommended mixes for both temporaiy and
permanent seeding. These mixes,with the exception of the wetland mix, shall be applied at a
rate of 120 pounds per acre. This rate can be reduced if soi) amendments or slow-release
fertilizers are used. Locai suppliers or the local conseivation district should be consulted for
their recommendations because the appropriate mix depends on a variety of factors, including
location, exposure, soil type, slope, and expected foot traffic. Alternative seed mixes approved
by Snohomish County may be used.
Table 4.1 represents the standard mix for those areas where just a temporary vegetative cover is
required.
Table 4.1
' Temporaiy Erosion Control Seed Miat
%Weight % %Gcrmination
Puri
Chewings or annual blue grass 40 98 90
restucn rubra var. commtrtata or Poa arrna
Pere�mial rye- 50 98 90
Lolium erenne
Redtop or colonial bentgrass 5 92 85
A r•ostis alba or A �ostis tenuis
White dutch clover 5 98 90
Ti�ifo7itrn�repetas
Table 42 pro��ides just one recommended possibility foi•landscaping seed.
Table 4.2
Landscaping Seed Mix
%
%�Vei I�t Purity %Gcrmination
Perennial rye blend 70 98 90
Lolitnn erenne
Chewings and red fescue blend 30 98 90
Festuca rubra var. commutata
or Festuca rz�bra
September 2010 Snohomish County Drainage Manual Volume Il-Construcfion StormwaterPollufion Prevenfion 35
The turf seed�nix in Table 4.3 is for dry situations�vhere little�vater is requit�ed. This inix
requires very little maintenance.
Table 4.3
Low-Gro�ving Turf Seed Mix
% \Veigl�t % %Germination
Puri �
Dwarf tall fescue(several varieties) 45 98 90
Festtrca nrtrndinacea var.
Dwarf perennial rye(Barclay) 30 98 90
Loliurn erenne var. bar�cl
Red fescue 20 98 90
Festuca r�ubr•a
Colonial bentgrass 5 98 90
Agrostis tenuis
Table 4.4 presents a mix recommended for bioswales and other intermittently��et areas.
Table 4.4
Bioswale Seed Mix
%1Veight % "/o Germination
Puri �
Tall or meadow fescue 75-80 98 90
Fesh�ca ar-trndinacea or Festuca elatior
Seaside/Creeping bentgrass 10-15 92 85 i
A rostis altrstris
Redtop bentgrass 5-10 90 80
i l�rr;�i;s nlh_,or,.l���r�cr;,e.gi,';r�tti��z I
In__
, �
September 2010 Snoh�mish Counfy Drainage Manua! Volume!I-Construcfion Sformwater Pollution Prevention 36
The seed inix shown in Table 4.5 is a recommended low-growing, relatively non-invasive seed
mix appropriate for very wet areas that are not regulated wetlands. Apply this m�ture at a rate
of 60 pounds per acre.
Table 4.5
Wet Area Seed Mix*
%�'Veight % %Germination
Pw•i �
Tall or meadow fescue 60-70 98 90
Festt�ca a�nrnditaacea or
Fest2rca elatior
Seaside/Creeping bentgrass 10-IS 98 85
A rostis pahrstris
Meadow foxtail 10-15 90 80
Ale oczrrirs ratensis
Alsike clover 1-6 98 90
I Tri olitrm hybridum
Redtop bentgrass 1-6 92 85
Agrostis alba
*Modified Briargreen,Inc. Hydroseeding Guide N�etlands Seed I�lix
The meadow seed mix in Table 4.6 is recommended for areas that will be maintained
infrequently or not at all and where colonization by native plants is desirable. Lilcely
applications include rural road and utility right-of-way. Seeding should take place in September
or veiy early October in order to obtain adequate establishment prior to the winter months. The
appropriateness of clover in the mix may need to be considered,as this can be a fairly invasive
species. If the soil is amended,the addition of clover may not be necessary.
Table 4.6
Meado�v Seed Mix
%Wcight % %Germination
Pw�ity
Redtop or Oregon bentgrass 20 92 85
A r•ostis aTba or A �•ostis ore onensis
Red fescue 70 98 90
Festa�ca rtrbra
White dutch clover 14 98 90
Ti�ifolitrm repens
1blaintenance Standards I
Any seeded areas that fail to establish at least 80 percent cover (100 percent co�-er for areas that
receive sheet or concentrated flows) shall be reseeded. If reseeding is ineffective, an alternate
method, such as sodding, mulching, or nets/blankets, shall be used. If winter v��eather prevents ,
adequate grass grovvth,this time limit may be rel�ed at the discretion of Snohornish Count��
when sensitive areas would otherwise be protected. After adequate cover is achieved, any areas ,,
that experience erosion shall be reseeded and protected by mulch. If the erosion problem is ��
dcainage related, the problem shal) be fixed and the ee�oded area reseeded and protected by
�T�ulch. I
,I
_,�,�__.���,�_:w�_.__._����. �______ - --_-. ----�d�.a_.�._ _�__.v_
.�.�,�_w...� _ ��
, I
Seeded areas sIiall be supplied �vith adequate moisture, but not watered to the extent that it
causes runoff.
�
i
BMP C121: Mulching
Purpose
The purpose of mulching soils is to provide immediate temporary protection from erosion.
Mulch also enhances plant establishment by conserving moisture, holding fertilizer, seed, and
topsoil in place, and moderating soil temperatures. There is an enormous ��a►-iet}- of inulches tllat
can be used. Only the most common types are discussed in this section.
Conditions of Use
As a temporary cover measure, mulch should be used:
• On disturbed areas that require cover measures for less than 30 days.
• As a cover for seed during the wet season and during the hot summer montlis.
• During the wet season on slopes steeper than 3H:1 V with more than 10 feet of vertical
relief.
Mulch may be applied at any time of the year and must be refreshed periodically.
Design and Installation Specifications
For mulch materials, application rates, and specifications, see Table 4.7. Note: Thicknesses may
be increased for disturbed areas in or near sensitive areas or other areas highly susceptible to
erosion.
Mulch used within the ordinary high-��ater mark of surface waters should be selected to
minimize potential flotation of organic matter. Composted organic materials have higher
specific gravities (densities) than straw, wood, or chipped material.
Maintenance Standards
The thickness of the cover must be maintained.
Any areas that experience erosion shall be remulched and/or protected with a net or blanket. If
the erosion problem is drainage related,then the problem shall be fixed and the eroded area
remulched.
September 2010 Snohomish County Drainage Manua! Volume!1- Construction Stormwater Poflution Prevention 39
Table 4.7
Mulch Standards and Guidelines
ATulch Application
1�'Iaterial Qualit Standards Rates Remarks
Straw Air-dried;free from 2"-3"thick;5 Cost-effective protection when applied with adequate
undesirable seed and bales per 1000 sf thickness. Hand-application generally requires D eater
coarse material. or 2-3 tons per tliickness than blown straw.The thickness of straw may be
acre reduced by half when used in conjunction with seeding. [n
windy areas straw must be held in place by crimping,using a
tackifier,or covering with netting. Blown straw always has
to be held in place with a tackifier as even light winds�vill
blow it away.Straw,ho«�ever,has several deficiencies that
should be considered when selecting mulch materials. It
often introduces and/or encourages the propagation of weed
species and it l�as no significant long-term benefits. Straw
should be used only if mulches�vith long-term benefiu are
unavailable locally. It should also not be used within the
ordinary high-water elevation of surface��•aters(due to
flotation).
Hydromulch No grotinh Approx.25-30 Shall be applied with hydromulcher. Shall not be used
inhibiting factors. Ibs per 1000 sf without seed and tackifier unless the application rate is at
or 1500 -2000 least doubled. Fibers longer than about'/.-1 inch clog
Ibs per acre hydromulch equipment. Fibers should be kept to less than'/<
inch.
Composted No visible water or 2"thick min.; More effective control can be obtained by increasing
1�4ulch and dust during approx. 100 tons thicl:ness to 3". Excellent mulch for protecting final grades
Compost handling. Must be per acre(approx. until landscaping because it can be directly seeded or tilled
purchased from 800 lbs per yard) into soil as an amendment. Composted mulch has a coarser
supplier with Solid size gradation than compost.It is more stable and practical
�Vaste Handling to use in wet areas and during rainy weather conditions.
Permit(unless
exempt).
Chipped Site Average size shall 2"minimum This is a cost-effective way to dispose of debris from
Vegetation be several inches. thickness clearing and grubbing,and it eliminates the problems
Gradations from associated with burning. Generally,it should not be used on
fines to 6 inclies in slopes above approx. 10°/a because of its tendency to be
length for texture, transported by runoff. It is not recommended within 200
variation,and feet of surface waters. If seeding is expected shortly after
interlocking mulch,the decomposition of the chipped vegetation may tie
properties. up nutrients important to grass establishment.
V4'ood-based No visible water or 2"thick;approx. This material is often called"hoD or hogged fuel." It is
Mulch dust during 100 tons per acre usable as a material for Stabilized Construction Entrances
handling. Must be (approx.8001bs. (BMP C 105)and as a mulch. The use of mulch ultimately
purchased from a per cubic yard) improves the organic matter in the soiL Special caution is
supplier with a Solid advised re�arding the source and composition of wood-
Waste Handling based mulches. Its preparation typically does not provide
Permit or one any weed seed control,so evidence of residual vegetation in
exempt from solid its composition or known inclusion of"�eed plants or seeds
waste re�ulations. should be monitored and prevented(or minimized).
September 2010 Snohomish County Drainage Manual Volume!/-Construction Stormwater Pollution Prevention 40
BMP C140: Dust Control I
Purpose '�
Dust control prevents w�ind transport of dust from disturbed soil surfaces onto roadv�rays, �
drainage ��ays, and surface waters.
Conditions of Use
In areas (including roadways) subject to surface and air movement of dust where on-site and oft=
site impacts to roadw�ays, drainage�vays, or surface waters are likely.
Design and Installation Specifications ,
Vegetate or mulch areas that will not receive vehicle traffic. In areas where planting, mulching,
or paving is impractical, apply gravel or landscaping rock.
Limit dust generation by clearing only those areas where immediate activity will take place,
leaving the remaining area(s) in the original condition, if stable. Maintain the original ground
cover as long as practical.
Construct natural or artificial windbreaks or windscreens. These may be designed as enclosures
far small dust sources.
Sprinkle the site with water until surface is wet. Repeat as needed. To prevent carryout of mud ,
onto street, refer to Stabilized Construction Entrance (BMP C105).
Irrigation water can be used for dust control. Irrigation systems should be installed as a first step
on sites where dust control is a concern.
Spray exposed soil areas with a dust palliative, following the manufacturer's instructions and
cautions regarding handling and application. Used oil is prohibited from use as a dust
suppressant.
PAM (BMP C126) added to water at a rate of 0.� lbs. per 1,000 gallons of water per acre and
applied from a water truck is more effective than water alone. This is due to the increased
infiltration of w�ater into the soil and reduced evaporation. In addition, small soil particles are
bonded together and are not as easily transported by wind. Adding PAM may actually reduce
the quantity of water needed for dust control, especially in eastern V��ashington. Since the
wholesale cost of PAM is about$ 4.00 per pound, this is an extremely cost-effective dust control
method.
Techniques that can be used for unpaved roads and lots include:
• Lower speed limits. High vehicle speed increases the amount of dust stirred up from
uripaved roads and lots.
• Upgrade the road surface strength by improving particle size, shape, and mineral types
tliat make up the surface and base materials.
• Add surface gravel to reduce the source of dust emission. Limit the amount of fine
particles (those smaller than .075 mm) to 10 to 20 percent.
September 2010 Snohomish County Drainage Manual Volume ll- Construction Stormwater Pollution Prevention 60
• Use geotextile fabrics to increase the strength of neiv roads or roads undergoing
reconstruction.
• Encourage the use of alternate,paved routes, if available.
• Restrict use bti tracked vehicles and hea�y trucks to pre��ent damage to road surface and
base.
• Appl�' C11CI]11Cc11 C�L1St SU]J�JI'2SS3ritS 11Slll�,T T�le 3C�I1111 II7Zt�lOC1. hlellClll]a t�le pl'OC�UCt\L'lt�l Ifle
top fe�v inches of surface material. Suppressailts may also be applied as surface
treatments.
• Pave unpa��ed pei7nanent roads and other trafficked areas.
• Use vacuum street sweepers.
• Remove mud and other dirt promptly so it does not dry and tl�en turn into dust.
• Limit dust-causinQ «�ork on ��-indv davs.
Maintenance Standards
Respray area as necessar}� to keep dust to a minimum.
September 2010 Snohomish County Drainage Manual Volume !1- Construction Stormwafer Polfufion Prevention 61
BMP C220: Storm Drain Inlet Protection
Purpose
To prevent coarse sediment from entering drainage systems prior to permanent stabilization of
the disturbed area.
Conditions of Use
Where storm drain inlets are to be made operational before permanent stabilization of the
disturbed drainage area. Protection should be provided for all storm drain inlets dow-nslope and
within 500 feet of a disturbed or construction area, unless the runoff that enters the catch basin
��ill be conveyed to a sediment pond or trap. Inlet protection may be used anyw�here to protect
the drainage system. It is likely that the drainage system will still require cleaning.
Table 4.91ists several options for inlet protection. All of the methods for storm drain inlet
protection are prone to plugging and require a high frequency of maintenance. Drainage areas
should be limited to 1 acre or less. Emergency overflows may be required where stormwater
ponding��ould cause a hazard. If an emergency overflow is provided, additional end-of-pipe
treatment may be required.
Table 4.9
Storm Drain Inlet Protection
Applicable for
Emergency Paved/Earthen
T e of Inlet Protection Overflow Surfaces Conditions of Use
Dro Inlet Protection
Excavated drop inlet Yes,temporary Earthen Applicable for heavy flows. Easy to
protection flooding will maintain. Large area Requirement: 30'
occur X 30'/acre
Block and gravel drop inlet Yes Paved or Earthen Applicable for heavy concentrated
protection flows. Will not pond.
Gravel and wire drop inlet No Applicable for heavy concentrated
protection flows. Will pond.Can withstand
traffic.
Catch basin filters Yes Paved or Earthen Fre uent maintenance re uired.
Curb Inlet Protection
Curb inlet protection with a Small capacity Paved Used for sturdy,more compact
wooden weir overflow installation.
Block and gravel curb inlet Yes Paved Sturdy,but limited filtration.
protection
Culvert Inlet Protection
Cuh�ert inlet sediment trap 18 month ex ected life.
September 2010 Snohomrsh County Drainage Manual Volume !!-Construction Stormwater Pollution Prevenfion 93
_
,
i
Design and Installation Specifications
Excavated Drop Inlet Protection ��i
Excavated drop inlet protection is an excavated impoundment around the storm drain. Sediment �
settles out of the stormwater prior to entering the storm drain.
Depth 1-2 ft as measured from the crest of the inlet structure.
Side Slopes of excavation no steeper than 2:1.
Minimum volume of excavation 35 cubic yards.
Shape basin to fit site���ith longest dimension oriented toward the longest inflo���area. ,
Install provisions for draining to prevent standing water problems. I',
Clear the area of all debris.
Grade the approach to the inlet uniformly.
�'� Drill weep holes into the side of the inlet.
Protect weep holes with screen wire and washed aggregate.
Seal weep holes v�Then removing structure and stabilizing area. �
It may be necessary to build a temporary dike to the down slope side of the structure to prevent
bypass flow.
Block and Gravel Filter-
Block and gravel filter is a barrier formed around the storm drain inlet with standard concrete
blocks and gravel. See Figure 4.14.
Height 1 to 2 feet above inlet.
Recess the first row 2 inches into the ground for stability.
Support subsequent courses by placing a 2x4 through the block opening.
Do not use mortar.
Lay some blocks in the bottom row on their side for dewatering the pool.
Place hardware cloth or comparable wire mesh with '/�-inch openings over all block openings.
Place gravel just below the top of blocks on slopes of 2:1 or flatter.
An alternative design is a gravel donut.
Inlet slope of 3:1.
Outlet slope of 2:1.
1-foot wide level stone area between the structure and the inlet.
Inlet slope stones 3 inches in diameter or larger.
Outlet slope use gravel '/�- to 3/-inch at a minimum tliickness of 1-foot.
September 2090 Snohomrsh County Drarnage Manuaf Volume 1!-Construction Stormwater Pollution Prevention 94
Block and Gravel Filter
Gravel and �nrire mesh filter is a gravel barrier placed over the top of the inlet. This structui•e
does not provide an overflow.
Hardware cloth or comparable wire mesh with '/2-inch openings.
Coarse aggregate.
Height 1-foot or more; 18 inches ���ider than inlet on all sides.
Place wire mesh over the drop inlet so that the wire extends a minimum of 1-foot beyond each
side of the inlet structure.
If more than one strip of inesh is necessary, overlap the strips.
Place coarse aggregate over the wire mesh.
The depth of the aravel should be at least 12 inches over the entire inlet opening and extend at
least 18 inches on all sides.
Catchbasin filte��,
Catchbasin filters should be designed by the manufacturer for use at construction sites. The
limited sediment storage capacity increases the amount of inspection and maintenance required.
which may be daily for heavy sediment loads. The maintenance requirements can be reduced b��
combining a catchbasin filter with another type of inlet protection. This type of inlet protection
provides flow bypass without overflo��7 and therefore may be a better method for inlets located
along active rights-of-wa}�.
S cubic feet of stora�e.
Dewatering provisions.
High-flow bypass that��-i11 not clog under normal use at a construction site.
The catchbasin filter is inser-ted in the catchbasin just belo���the gratin�.
Curb Inlet Protection ���ith Wooden Weir
Curb inlet protection with wooden�veir is a barrier formed around a curb inlet��-ith a ���ooden
frame and gravel
Wire mesh with '/2-inch openings.
Extra strenb h filter cloth.
Construct a frame
Attach the wire and filter fabric to the frame.
Pile coarse washed aggregate against�vire/fabric.
Place weight on fraine anchors.
September 2010 Snohomish County Drainage Manua! Volume!!-Construction Sformwater Po!lution Prevenfion 95
Block and Gravel Curb Inlet Protection
Block and gravel curb inlet protection is a barrier formed around an inlet with concrete blocks
and gravel. See Figure 4.15.
Wire mesh with '/z-inch openings.
Place two concrete blocks on their sides abutting the curb at either side of the inlet opening.
These are spacer blocks.
Place a 2x4 stud through the outer holes of each spacer block to align the front blocks.
Place blocks on their sides across the front of the inlet and abutting the spacer blocks.
Place vvire mesh over the outside vertical face.
Pile coarse aggregate against the ���ire to the top of the barrier
Curb and �utter sediment bairier
Curb and gutter sediment banier is a sandbag or rock berm (riprap and aggregate) 3 feet high and
3 feet wide in a horseshoe shape. See Figure 4.16.
Construct a horseshoe shaped berm, faced with coarse aggregate if using riprap, 3 feet high and 3
feet wide, at least 2 feet from the inlet
Construct a horseshoe shaped sedimentation trap on the outside of the berm sized to sediment
trap standards for protecting a culvert inlet.
September 2010 Snohomish Counfy Drainage Manual Volume ll- Consfruction Stom�water Po!lution Prevention 96 ,
i '
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Notes:
1.Drop inlet sediment barriers are to be used for smail,nearly level drainage areas.(less than 5%a) �
2. Excavate a basin of sufficient size adjacent to the drop inlet. i
3.The top of the structure(ponding height)must be�+�ell below the ground elevation downslope to prevent '
runoff from bypassing the inlet. A temporary dike may be necessary on the downslope side of the structure.
Figure 4.14-Block and Gra��el Filter �',
Septeri�ber 2010 Sr�c�hornish County Drarna:�e Manu�31 VoJ�une 1l- Constructron Storrz��^,�aterPollufion Prevenfion 97
Plan View
Back of Sidewalk A Catch Basin
I
�
�.
ri ��,,
il '�i
�' II
i� �i
�� �l 2x4 Wood Stud
,�
� Back of Curb Concrete Block
Curb Inlet
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Wire Screen r �
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Section A - A 3���Drain Gravel
(20mm)
'/4'Drain Gravel
(20mm)
Ponding Height
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Overflo
r—
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4 Wood Stud /
(100x50 Timber Stud) �j�.
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NOTES:
1. Use block and gravel type sediment barrier when curb inlet is located in gentiy sloping street segment,
where water can pond and allow sediment to separate from runoff.
2. Barrier shali allow for overflow from severe storm event.
3. Inspect barriers and remove sediment after each storm event. Sediment and gravel must be removed
from the traveled way immediately.
Figure 4.1�—Block and Gravel Curb Inlet Protection
September 2010 Snohomish County Drainage Manual Volume ll-Construction Stormwater Po!lution Prevention 98
Plan View
Back of Sidewalk I'�
Burlap Sacks to Catch Basin
Overlap onto Curb
, �\ Curb Inlet
�� Back of Curb
�'� i ,,
i� '
I 1
I 1
�
RUNOFF � �
�� I
RUNOFF SPILLWAY �r/
, �!
i
/
�`, Gravel Filled Sandbags
';',\ Stacked Tightly
�
NOTES:
1.Place curb type sediment barriers on gently sloping street segments,where water can pond and allow
sediment to separate from runoff.
2.Sandbags of either burlap or woven'geotexrile'fabric,are filled with gravel,layered and packed tightly.
3.Leave a one sandbag gap in the top row to provide a spillway for overflow.
4.Inspect barriers and remove sediment after each storm event.Sediment and gravel must be removed from
the traveled way immediately.
Figure 4.16—Curb and Gutter Barrier
September 2010 Snohomish County Drainage Manua/ Volume ll- Construction Stormwater Pollution Prevention 99
��laintenance Standards
Catch basin filters should be inspected tiequently, especially after stonn events. If the insert
becomes clogged, it should be cleaned or replaced.
For systems using stone filters: If the stone filter becomes clogged with sediment, the stones
must be pulled away from the inlet and cleaned or replaced. Since cleaning of gravel at a
construction site may be difficult, an alternative approach would be to use the clogged stone as
fill and put fresh stone around the inlet.
Do not wash sediment into storm drains v��lule cleaning. Spread all excavated material evenly
over the surrounding land area or stockpile and stabilize as appropriate.
I
�
BMP C209: Outlet Protection
Purpose
Outlet protection prevents scour at conveyance outlets and minimizes the potential for i
downstream erosion by reducing the velocity of concentrated stormwater flows.
Conditions of Use �
�
Outlet protection is required at the outlets of all ponds, pipes, ditches, or other conveyances, and
where runoff is conveyed to a natural or manmade drainage feature such as a stream, «�etland,
lake, or ditch. I
Design and Installation Specifications I�
The receiving channel at the outlet of a culvert shall be protected from erosion by rock lining a
minimum of 6 feet downstream and extending up the channel sides a minimum of 1—foot above
the maximum tailwater elevation or 1-foot abo��e the crown, whichever is higher. For large pipes
(more than 18 inches in diameter), the outlet protection lining of the channel is lengthened to
four times the diameter of the culvert.
Standard wingwalls, and tapered outlets and paved channels should also be considered when
appropriate for permanent culvert outlet protection.
Organic or synthetic erosion blankets, with or without vegetation, are usually more effective than
rock, cheaper, and easier to install. Materials can be chosen using manufacturer product ;
specifications. ASTM test results are available for most products and the designer can choose
the correct material for the expected flow.
With low flows, vegetation(including sod) can be effective. I',
The following guidelines shall be used for riprap outlet protection: �
• If the discharge velocity at the outlet is less than 5 fps (pipe slope less than 1 percent),
use 2-inch to 8-inch riprap. Minimum thickness is 1-foot. ',
• For 5 to 10 fps discharge velocity at the outlet(pipe slope less than 3 percent), use 24- �
inch to 4-foot riprap. Minimum thickness is 2 feet.
• For outlets at the base of pipes sloping 10 percent or greater with a 10-foot vertical
elevation drop, an energy dissipater shall be designed and constructed in accordance with
EDDS Chapter 5-OSL, Pipe Ends and Outfall Systems.
Filter fabric or erosion control blankets should always be used under riprap to prevent scour and ,
channel erosion.
New pipe outfalls can provide an opportunity for low-cost fish habitat improvements. For
example, an alcove of lo��-velocity water can be created by constructing the pipe outfall and
associated energy dissipater back from the stream edge and digging a channel, over-widened to
the upstream side, from the outfall. Overwintering juvenile and migrating adult salmonids may
use the alcove as shelter during high flows. Bank stabilization, bioengineering, and habitat
September 2010 Snohomish County Drainage Manua! Volume!!- Construction Stormwater Po!lution Prevention 91
features may be required for disturbed areas. See Volume V for more information on outfall
system design.
Maintenance Standards
Inspect and repair as needed.
Add rock as needed to maintain the intended function.
Clean energy dissipater if sediment builds up.
il
,
Septem6er 2010 Snohomish County Drainage Manua! Volume I!- Construction Stormwater Pollution Prevention 92
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.
Stake and Wire Fence (BMP C104)
Sediment Trap (BMP C240)
� Temporary Sediment Pond (BMP C241)
Straw Bale Barrier (BMP C230)
Brush Barrier (BMP C231)
Gravel Filter Berm (BMP C232)
Vegetated Strip (BMP C234)
Straw Wattles (BMP C235)
Nets and Blankets (BMP C122)
Plastic Covering (BMP C123)
Interceptor Dike and Swale (BMP C200)
Grass-Lined Channels (BMP C201)
Check Dams (BMP C207)
Concrete Handling (BMP C151)
Sawcutting and Surface Pollution Prevention (BMP C152)
�2013 D. R. STRONG Consulting Engineers Inc. Page 23 of 39
Stormwater Pollution Prevention Plan Piper"s Bluff January 31,2012
!
1 .
BMP C104: Stake and Wire Fence
Purpose
Fencing is intended to: (1)restrict clearing to approved limits; (2) prevent disturbance of
sensitive areas, their buffers, and other areas required to be left undisturbed; (3) limit
construction traffic to designated construction entrances or roads; and, (4)protect any areas
�vhere marking with survey tape may not provide adequate protection.
Conditions of Use
To establish clearing limits, stake or wire fence may be used: I
• At the boundary of sensitive areas, their buffers, and other areas required to be left
uncleared.
• As necessary, to control vehicle access to and on the site.
Design and Installation Specifications I
See Figure 4.1 for details.
. More substantial fencing shall be used if the fence does not prevent encroachment into those
areas that are not to be disturbed. ,
Maintenance Standards
If the fence has been damaged or visibility reduced, it shall be repaired or replaced immediately
and visibility restored.
_.
Survey Flagging Baling Wire Do Not Nail or Staple
Wire to Trees
3' AIIN.
10'-20'
Metal
Fence Post
—I I I I I I—I I I—I I I—I I I—I I I 1 I—I I I—I I I-11 I— I I—I I ,;
12 MIN.
�
Figure 4.1 —Stake and VVire Fence
September 2010 Snohomish County Drainage Manua! Volume ll-Construction Stormwater Po!lution Prevention 26
,I
BMP C240: Sediment Trap
Purpose
A sediment trap is a small temporaiy ponding area with a gravel outlet used to collect and store
sediment fi�om sites cleared and/or graded during construction. Sediment traps,along with other
perimeter controls, shall be installed before any land disturbance talces place in the drainage area.
Conditions of Use
Prior to leaving a construction site, stormwater runoff must pass throttgh a sediment pond or trap
or other appropriate sediment removal best management practice. Non-engineered sediment
traps may be used on-site prior to an engineered sediment tcap or sediment pond to provide
additional sediment removal capacity.
It is intended for use on sites where the tributary drainage area is less than 3 acres, with no
unusual drainage features, and a projected build-out time of six months or less. The sediment
trap is a temporary measure(with a design life of approximately 6 months) and shall be
maintained until the site area is permanently protected against erosion by vegetation and/or
sri•uctures.
Sediment traps and ponds are only effective in removing sediment down to about the medium silt
size fraction. Runoff with sediment of finer grades(fine silt and clay) will pass through
unheated, emphasizing the need to cont��ol erosion to the maximum extent first.
Whenever possible, sediment-laden water shall be discharged into onsite,relatively level,
vegetated areas (see BMP C234—Vegetated Strip). This is the only way to effectively remove
fine particles from runoff unless chemical treatment or filtration is used. This can be particularly
useful after initial treatment in a sediment trap or pond. The areas of release must be evaluated
on a site-by-site basis in order to determine appropriate locations for and methods of releasing
runof£ Vegetated wetlands shall not be used for this purpose. Frequently, it may be possible to
pump water from the collection point at the downhill end of the site to an upslope vegetated area.
Pumping shall only augment the treatment system, not replace it, because of the possibility of
�ump failure or runoff volume in excess of pump capacity.
All projects that are constructing permanent facilities for runoff quantity control should use the
rough-graded or final-graded permanent facilities for traps and ponds. This includes combined
facilities and infilt�ation facilities. When permanent facilities are used as temporary
sedimentation facilities,the surface area requirement of a sediment trap or pond must be met. If
the surface area requirements are larger than the surface area of the permanent facility,then the �,
trap or pond shall be enlarged to comply with the surface area requirement. The permanent pond
shall also be divided into two cells as required for sediment ponds.
Either a permanent contt•ol structure or the temporary control stivcture (described in BMP C241,
Temporary Sediment Pond) can be used. If a permanent control structure is used, it may be
advisable to partially restcict the lower orifice with gravel to increase residence time while still
allowing dewatering of the pond. A shut-off valve may be added to the control structure to allo�v
complete retention of stormwater in emergency situations. In this case, an emetgency o��erflo�v
«�eir must be added.
September 2010 Snohomrsh County Drainage M,anual Volume 11-Construction Stormwater Po!lufion Prevention 196
A slcimmer may be used for the sediment trap outlet if approved by Snohomish County.
Design and Installation Specif'ications
See Figures 4.22 and 4.23 for details.
If permanent runoff control facilities are part of the project,they should be used for sediment
retention.
To determine the sediment trap geometcy, first calculate the design surface area(SA) of the trap,
measured at the invet-t of the weir. Use the following equation:
II —
SA — FS(QzIVS)
where
Q2 = Design inflow based on the peak discharge from the developed 2-year
runoff event fi•om the contributing drainage area as computed in the hydrologic analysis. The
10-year peak flow shall be used if the project size, expected timing and duration of
construction, or downstream conditions wai7ant a higher level of protection. If no hydrologic
' , analysis is required,the Rational Method may be used.
VS = The settling velocity of the soil particle of interest. The 0.02 mm (inedium
silt)particle with an assumed density of 2.65 g/cm3 has been selected as the particle of
interest and has a settling velocity{VS) of 0.00096 ft/sec.
FS = A safety factor of 2 to account for non-idea( settling.
Therefore, the equation for computing surface area becomes:
SA = 2 x QZ/0.00096 or 2080 square feet per cfs c�f itlflo���
Even if permanent facilities are used,they must still have a surface area fhat is at least as lar�e as
that derived fi•om the above formula. If they do not, the pond must be enlarged.
To aid in deterinining sediment deptli, all sediment traps shall have a staff gauge ��it11 a
prominent marlc 1-foot above the bottom of the trap.
Sediment traps may not be feasible on utility projects due to the Iimited work space or th� sl��,rt-
term nature of the t��orlc. Portabie.tanks may be used in place of sediment traps for uti I
lYlaiutenance Standay�ds I'
Sediment shall be removed fi•om the trap when it reaches 1-foot in ' �'
September 2010 Snohomish County Drainage Manual Volume!1-Construction Stormwater Po!lufion Prevention 117
i
5urface area detemtinet� 4�� M�n��
at top ofw�ir \ �
� � �`- �, 7�Mln,Dv��l�,w
�„ � _, _ ,._.. � �.. � � ..r. _.:. �, ._. -
� �' � '1``in. . ��.�'_
Gryy J , : i"��` _1'Min.
� J.d�-�� ! .4 �
�1.�'Min. �' � �`�,
�'�f-' � Flet�ottom � � � � �
'�"-1 a*" � 2'-4"Ro�k RlpRap��
ihfeaha d gravrl
Note; Trap rns�be fiormed by berm or kay GeoE�tlle ,f f
p��tial or campl�k��xcavaklori �
' Dischar�e to statail�zed
c�nv�yanc�, t�utl�t,or
levf�l spreader
Figure 4.22 Cross Section of Sediment Trap
6' Min.
1'Min. depth overFlow spillwa
–���—���—���—���—���—�� y —���—���—���—���—���—�
ii-i i i_i i i-iTi-i i i-I I I I I I I- ` , - , r� I I I�;i i i-iTi-Ti-iTi-i i i_
Native soil or ��_��� - ' ' �� � ����in. 1'depth
compacted backfill ��_� ' ` �`� —��{- 2"-4'° rock
Geotextile -���—���—���—���—���=���_���=)��—����' Min. 1'depth 314"-1.5"
_���-���,-��� ���-��� ���-���-���,-� washed gravel
Fi6i�r•e 4.23 �ecliment Tran nutic��
September 2010 Snohomish County Drainage Manual VoJume!!-Construction Stormwafer Po!lufion Prevention 918
i
BMP C241: Teinporaiy Sediment Pond
NOTE: structures having a maximum storage capacity at the top of the dam
of 10 acre-ft(435,600 ft3) or more are subject to the Washington Dam Safety
Regulations (Chapter 173-175 WAC).
Pu►•pose
Sediment ponds remove sediment fi•om runoff originating from disturbed areas of the site.
Sediment ponds are typically designed to remove sediment no smaller than medium silt(0.02
min). Consequently;the}� usl�ally reduce turbidity only slightly.
Conditions of Use
Prior to leaving a consn•uction site, stormwater runoff must pass through a sediment pond or
other appropriate sediment removal best management practice.
A sediment pond shall be used where the contributuig drainage area is 3 acres or more. Ponds
must be used in conjunction with erosion cont�ol practices to reduce the amount of sediment
flo���ing into the basin.
Design and Installation Specificatio�is
Sediment basins must be installed only on sites where failure of the structure would not cesult in
l loss of life, damage to homes or buildings, or inteiTuption of use or setvice of public roads or
utilities. If fencing of the pond is required, the type of fence and its location shall be shown on
the ESC plan.
See Figure 4.24, Figure 4.25, and Figuce 4.26 for details.
If permanent iunoff control facilities are part of the project,they should be used for sediment
retention. The surface area requirements of the sediment basin must be inet. This may require
enlarging the permanent basin to comply with the surface area requirements. If a permanent
contcol snucture is used, it inay be advisable to partially restrict the lovver orifice with gravel to
increase residence time while still allowing dewatering of the basin.
Use of infiltration facilities for sediinentation basins during construction tends to clog the soils
and reduce their capacity to infiltrate. If infiltration facilities are to be used, the sides and bottom
of the facility must only be rough excavated to a minimum of 2 feet above final grade. Final
grading of the infiltration facility shall occur only when all contributing drainage areas are fitlly
stabilized. The infiltcation pretreatment facility should be fully constructed and used with the
sedimentation basin to help prevent clogging.
Deteirnining Pond Geometry
Obtain the discharge from the hydrologic calculations of the pealc flow for the 2-year runoff
event(Q2). The 10-year pealc flow shall be used if the project size, expected timing and duration
of construction, or do��vnstceam conditions warrant a higher level of protection. If no hydrologic
analysis is required,the Rational Method may be used.
September 2010 Snohomish County Drainage Manual Volume Il- Construcfion Stormv✓afer Pollution Prevention 919
Determine the required surface area at the top of the riser pipe with the eyuation:
SA = 2 x QZ/0.00096 or 2080 square feet per cfs of inflow
See BiviP C240 for more information on the derivation of the surface area calculation.
The basic geometry of the pond can now be deterinined using the following design criteria:
Required surface area SA (fi�om Step 2 above) at top of riser.
Minimum 3.5-foot depth from top of riser to bottom of pond.
Maximuin 3:1 interior side slopes and maximum 2:1 exterior slopes. The interior slopes can be
increased to a maximum of 2:1 if fencing is provided at or above the inaximum water surface.
One foot of fi•eeboard between the top of the riser and the crest of the emergency spillway.
Flat bottom.
Minimum 1-foot deep spillway.
Length-to-width ratio between 3:1 and 6:1.
Sizing of Discharge Mechanisms.
The outlet for the basin consists of a combination of principal and emergency spillways. These
outlets must pass the pealc runoff expected fi�om the contributing drainage area for a 100-year
storm. If, due to site conditions and basin geometry, a separate emergency spill-way is not
feasible, the principal spillway must pass the entire peak runoff expected fro�n the 100-year
storm. However, an attempt to provide a separate emergency spillway should always be made.
The runoff calculations should be based on the site conditions during construction. The flow
through the dewatering orifice cannot be utilized when calculating the 100-year storm elevation
because of its potential to become clogged; therefore, available spillway storage must begin at
the principal spillway riser crest.
The principal spillway designed by the procedures contained in this standard will result in some
reduction in the pealc rate of runoff. However,the riser outlet design will not adequately control
the basin discharge to the predevelopment discharge limitations as stated in SCC 30.63A.550.
Howe��er, if the basin for a permanent stormwater detention pond is used for a temporary
sedimentation basin,the control stcucture for the permanent pond can be used to maintain
predevelopment discharge limitations. The size of the basin,the expected life of the construction
project, the anticipated downstream effects and the anticipated weather conditions during
construction, should be considered to determine the need of additional discharge control. See
Figure 4.27 for riser inflo�i-curves.
September 2010 Snohomish County Drainage Manual Volume li-Cons!rucfion Sformwater Po!lufion Prevention 920
BMP C230: Straw Bale Barrier
Purpose
To decrease the velocity of sheet flows and intercept and detain small amounts of sediment from
distui•bed areas of limited extent,preventing sediment from leaving the site. See Figure 4.17 for
details on straw bale barriers.
Conditions of Use
Below disturbed areas subject to sheet and rill erosion.
Where the size of the drainage area is no greater than 1/4 acre per 100 feet of barrier length; the
maximum slope length behind the barrier is 100 feet; and the inaximum slope gradient behind
the barrier is 2:1.
Where effectiveness is required for less than three months.
Straw bale bacriers shall not be constructed in streams, channels, or ditches.
Straw bale barrieis shall not be used where rocic or hard surfaces prevent the fulI and uniform
anchoring of the barrier.
Design and Installation Speci�cations
Bales shall be placed in a single row, ]engthwise on the contour,with ends of adjacent bales
tightly abutting one another. ,
All bales shall be either wire-bound or sh•ing-tied. Straw bales shall be installed so that bindings I
are oriented around the sides rather than along the tops and bottoms of the bales in order to
prevent deterioration of the bindings.
The barrier shall be entrenched and bacl�lled. A trencl� shall be excavated the width of a bale
and the length of the proposed barrier to a minimum depth of 4 inches. The trench must be deep
enough to remove all grass and other material that might allow underflow. After the bales are
staked and chinlced (filled by wedging),the excavated soil shall be backfilled against the barrier.
Bacicfill soil shall conform to the ground level on the downhill side and shall be built up to 4
inches against the uphill side of the barriet•.
Each bale shall be securely anchored by at least two stakes or re-bais driven through the bale.
The first stake in each bale shall be driven toward the previously Iaid bale to force the bales
together. Stakes or re-bars shall be driven deep enough into the ground to securely anchor the
bales. Stakes should not extend above the bales but instead should be driven in flush �vith the
top of the bale for safety reasons.
The gaps between the bales shall be chinl<ed (filled by���edging)with straw to prevent water
fi•om escaping between the bales. Loose straw scattered ovec the area immediately uphill fi�oni a
straw bale barrier tends to inerease barrier efficiency. Wedging must be done careful(y in order
not to separate the bales.
September 2010 Snohomish County Drainage Manua! Volume!1-Construcfion Stormwater Pollution Prevention 1 Q 9
Maintenance Standards
Straw bale barriers shall be inspected iminediately after each runoff-producing rainfall and at
least daily during prolonged rainfall
Repair damaged bales and erosion around or under bales.
Sediment deposits should be removed after each runoff-producing rainfall. They must be
removed when the level of deposition reaches approxiinately one-half the height of the barrier.
Any sediment deposits remaining in place after the straw bale barrier is no longet•required shall
be dressed to conform to the existing grade,prepared and seeded.
Straw bales used as a temporary straw bale barrier shall be removed after project completion and
stabilization to prevent sprouting of unwanted vegetation.
,
�_ .
September 2010 Snohomish Counfy Drainage Manual Volume 1!-Construction Stormwater Pollution Prevention 902
I
SC'���rt i�_�
��.g.
(1.5-1,SmJ r�
� i
Ponding Height
�A p
�1 �,� � Emlr�d Stratv Bal�
�,� \ �� .� ,� 4"{160mm}IAiri�m
� into Soil
.
Angle�ke Ta�rard
Pr�t�iaus Balato
'�BCtIQi't � -� A Pro�Cfa Tigt�Rt
�
r
t q . � . , �
A
�o�darShke
ur Ret�r Urk�
Tl�our,�ba l�. '
-- �'N�� �.� ,�� �
�
B B
xar�: � I�I
i.The x�ra��beles�hall l�e p�.�d on sl��.x conto�.
2.B al�t�t�o��l��e d"n�r�v K%ith ffee�t��tly abuttin�,
3_Kcy in hnica la pcctenl u�tm nr naw�da ba Ica
Figure 4.17 Stra�v Bale Barrier II
BMP C231: Brush Barrier
Purpose
The purpose of biush barriers is to reduce the transport of coarse sediment from a construction
site by providing a temporaty physical barrier to sediment and reducing the rvnoff velocities of
overland flo�v. ��
Conditions of Use
Brush barriers may be used do��mslope of all disturbed areas of less than one-quarter acre.
Brush barriers are not intended to treat concentrated flows,nor are they intended to treat
substantial amounts of overland flow. Any concentrated flows must be conveyed through the
drainage system to a sediment pond. The only circumstance in which overland flow can be
treated solely by a barrier, rather than by a sediment pond, is when the area draining to the
barrier is small.
Brush bart•iers should only be installed on contours.
Design and Installation Specifications
Height 2 feet(minimum) to 5 feet(maximum).
Width 5 feet at base (minimum)to 15 feet(maximum�.
Filter fabric(geotextile) may be anchored over the br�� ,
the barrier. Ten-ounce burlap is an adequate alternative to tilter fabri�
Chipped site vegetatior ' ' ' ' ' , ' ' '
construct brush barriei�
A 100 percent biodegr�.. _. . . _ _ . _
by��looden stal.es. Figure �.18 depicts a typical brush barrier.
Maintenance Standards
There shall be no signs of erosion or concentrated runoff under or around the barrier. If
concentrated flows are bypassing the bairier, it must be expanded or augmented by toed-in filter
fabric.
The dimensions of the barrier must be maintained.
September 2010 Snohomish County Drainage Manual Volume ll-Construction Stormv✓ater Po!lution Prevention 104
If required,drape filter fabric
over brush and secure in 4'k4" �
min.trench with compacted -
backfill. �\; �
�\\1 � � �
C � ,•:-;.. , ' p����
�� - ����
� ��_�1
\ ��
�� " �Anchor downhill edge of
�-- filter fabric with stakes,
��'` � ��� � sandbags,or equivalent.
��� ��i�p,j< � �s
i�.����1-. I;F� ��„'^-.��
�,�i��
' 4�r �"�=11--�`�2'Min.Height
Min.5'wide brush barrier with '
max.6"diameter woody debris.
Alternatively topsoil strippings
may be used to form the barrier.
Figure 4.18—Brush Barrier
Sepfember 2010 Snohomish County Drainage Manua! Volume Il-Consfruction Stormti^✓ater Pollution Prevenfion 905
BMP C232: Gravet Filter Berm
Purpose
A gravel filter berm is constcucted on rights-of-way or traffic areas within a construction site to
retain sediment by using a filter berin of gravel or crushed roelc.
Conditions of Use
Where a temporary measure is needed to retain sediment fi�om rights-of-way or in traffic areas on
constr�uction sites.
Design and Installation Specifications
Berm material shall be 3/o to 3 inches in size,washed well-graded gravel or crushed rock with
less than 5 percent fines.
Spacing of berms:
• Every 300 feet on slopes less than 5 percent
• Every 200 feet on slopes between 5 percent and 10 percent
• Eveiy 100 feet on slopes greater than 10 percent
Berm dimensions:
• 1 foot high with 3:1 side slopes
0 8 linear feet per 1 cfs runoff based on the 10-year, 24-hour design storm
Maintenance Standards
Regular inspection is required. Sediment shall be removed and filter material replaced as
needed.
September 2090 Snohomish County Drainage Manua! Volume Il- Construcfion Stormwater Po!lution Prevention 106
BMP C234: Vegetated Strip
Purpose
Vegetated strips reduce the transport of coarse sediment from a construction site by providing a
temporary physical barrier to sediment and reducing the runoff velocities of overland flow.
Conditions of Use
Vegetated strips may be used downslope of all disturbed areas.
Vegetated strips are not intended to treat concentrated flows,nor ai•e they intended to treat
substantial amounts of overland flow. Any concentrated flows must be conveyed through the
drainage system to a sediment pond unless the criteria in table 4.11 are met.
TaUle 411
Vegetated Strips
AveraQe Slo e Slo e Percent Flow ath Len h
1.SH:1 V or less 67%or less 100 feet
2H:1 V or less 50%or less 115 feet
4H:1 V or less 25%or less 150 feet
6H:1 V or less 16.7%or less 200 feet
l OH:l V or less 10%or less 250 feet
llesign and Installation Specifications
The vegetated strip shall consist of a minimum of a 25-foot wide continuous strip of dense ,
vegetation with a permeable topsoil. Grass-covered, landscaped aceas are generally not adequate
because the volume of sediment ove�•whelms the grass. Ideally,vegetated strips shall consist of
undisturbed native growth with a well-developed soil that allows for infiltration of runoff
The slope within the strip shall not exceed 4H:1 V.
The uphill boundary of the vegetated strip shall be delineated with clearing limits.
Maintenance Standards
Any areas damaged by erosion or construction activity shall be seeded immediately and
protected by mulch.
If more than 5 feet of the ariginal vegetated strip width has had vegetation removed or is being
eroded, sod must be installed.
If there are indications that concentrated flows are traveling across the buffer, surface u�ater
controls must be installed to reduce the flows entering the buffer, or additional perimeter
protection must be installed.
September 2090 Snohomish County Drainage Manua! Volume I!-Construction Stormwater Polluflon Prevention 112
BMP C235: Straw Wattles
Purpose
Straw wattles are temporary erosion and sediment control barriers consisting of straw that is
wrapped in biodegradable tubular plastic or similar encasing material. They r•educe the velocity
and can spread the flow of rill and sheet runoff, and can capture and retain sediment. Straw
wattles are typically 8 to 10 inches in diameter and 25 to 30 feet in length. The wattles are
placed in shallow trenches and staked along the contour of disturbed or newly consti-ucted
slopes. See Figure 4.21 for typical const�-uction details.
Conditious of Use
Disttu�bed areas that require immediate erosion protection.
Exposed soils during tl�e period of short construction delays, or over winter months.
On slopes requiring stabilization until permanent vegetation can be established.
Straw wattles are effective for one to tv�,�o seasons.
If conditions are appropriate,wattles can be staiced to the ground using willow cuttings for added
revegetation.
Rilling can occur beneath wattles if not properly entcenched and water can pass between wattles
if not tightly abutted together.
Design and Installation Specifications I
It is critical that wattles are installed perpendicular to the flow direction and parallel to the slope
contour. !,
Narrow trenches should be dug across the slope on contour to a depth of 3 to 5 inches on clay
soils and soils with gradual slopes. On loose soils, steep slopes, and areas with high rainfall, the
trenches should be dug to a depth of 5 to 7 inches, or 1/2 to 2/3 of the thickness of the wattle.
Stai�t building tcenches and installing wattles from the base of the slope and work up. Excavated
material should be spread evenly along the uphill slope and compacted using hand tamping or
other methods.
Construct trenches at contour intervals of 3 to 30 feet apart depending on the steepness of the
slope, soil type, and rainfall. The steeper the slope the closer together the trenches.
Install the wattles snugly into the trenches and abut tightly end to end. D�not overlap the ends.
Install stalces at each end of the wattle,and at 4-foot centers along entire length of wattle.
If required, install pilot holes for the stalces using a straight bar to drive holes through the wattle
and into the soil.
At a minimum, wooden stalces should be approximately 3/4 x 3/4 x 24 inches. Willow cuttings
ot�3/8-inch rebar can also be used foc stakes.
September 2010 Snohomish County Drainage Manua! Volume I!-Construcfion Stormwater Po!lution Prevention 113
Maintenance Standards
Stalces should be driven through the middle of the wattle, leaving 2 to 3 inches of the stalce
protruding above the wattle.
Wattles may require maintenance to ensure they are in contact with soil and thoroughly
entrenched,especially after significant rainfall on steep sandy soils.
Inspect the slope after significant storms and repair any areas where wattles are not tightly
abutted or water has scoured beneath the wattles.
September 2010 Snohomish County Drainage Manua! Volume ll-Construction Stormwater Pollution Prevention 194
3-4' ��
� l � ` (1.2m) �"
�Ny
� � � � � �
Straw Rolls Must �\��� � � �
Be Placed Along �j�\
Slope Conlours j�� � pdJacent rolls shall
y ` � tighUy abut�
/ \ �
//� �✓�
\/\\���`�- �°�Y
% `
' \� � � �
��`\',� 10'-25'(3-8m) r �
.�\� \ �y �
���/�� �
�i�,/�� \//\
.
�j/
Spacing Depends �
on Soll Type and � ,(��� Sedfinent,organlc matter,
Slope Steepness % and natNe seeds are
�''���� �aptured behind the rolis.
%\
�����
\
/, /��i�
3"-5"(75-125mm) I
} %�
\ � �/�\�� 8"-10"DIA.
%� , � '�//�� � (200-250mm) �
\i�\ • � \/
. '�
Live Stake �
� /���
�\� I'
_�Y �� �/.
' ��� 1" X 1" Stake
� not to scale (25 x 25mm)
l 1�
A�
NOTE: �
1.Straw roll installation requires the placement and secure staking of the roll in a trencb,3"-5"(75-125mm)
deep,dug on contour. runoff must not be allowed to ran under or aro�md roll.
Figure 4.21 —Straw Wattles
September 2010 Snohomish County Drainage Manua! Volume I!-Consfrucfion Sformwafer Pollution Prevention 115
BMP C122: Nets and Blankets
Purpose
Erosion control nets and blanlcets are intended to prevent erosion and hold seed and mulch in
place on steep slopes and in channels so that vegetation can become weli established. In
addition, some nets and blanicets can be used to permanently reinforce turf to protect drainage
���ays during high flows. Nets (commonly called matting) are stc•ands of material woven into an
open, but high-tensile strength net(for example, coconut fiber matting). Blankets are strands of
material that are not tightly woven,but instead form a layer of interlocicing fibers,typically held
together by a biodegradable or photodegradable netting (for example, excelsior oi�straw
blankets). They generally have lower tensile strength than nets, but cover the ground more
completel}�. Coir(coconut fiber)fabric comes as both nets and blankets.
Conditions of Use
Erosion control nets and blankets should be used:
• To aid permanent vegetated stabilization of slopes 2H:1 V or greater and with more than
10 feet of vertical relief.
• For drainage ditches and swales (highly recommended). The application of appropriate
netting or blanlcet to drainage ditches and swales can protect bare soil fi•om channelized
runoff while vegetation is established. Nets and blanlcets also can capture a great deal of
sediment due to their open,porous structure. Synthetic nets and blanlcets can be used to
permanently stabilize channels and may provide a cost-effective, environmentally
preferable alternative to riprap. 100 percent synthetic blanlcets manufactured for use in
ditches may be easily reused as temporary ditch liners.
Disadvantages of blanlcets include:
• Surface preparation required;
• On slopes steeper than 2.5:1, bIanket installers may need to be roped and harnessed for
safety;
• They cost at least$4,000-6,000 per acre installed.
Advantages of blankets include:
• Installation does not require special equipment or extensive training
• Blanlcets can be installed in stages or phases as the project progresses; I
• Seed and fertilizer can be hand-placed by the installers as they progress do���n the slope; I
� Blankets can be installed in any weathe�: �
• There are numerous types ofblankets tl�at can l�c �i��i���ied ���ith ��:u i�,us j�.lramctcr; in
mind. Those parametei•s include: fibei• blend, lnesll stre.ngtll, longevity, biode�radabilit��. �
cost, and availability. I
September 2010 Snohomish County Drainage Manual Volume ll- Construction Storm�a�ater Pollution Prevenfion 41
Design and Installation Specifications
See Figure 4.4 and Figure 4.5 for typical orientation and installation of blankets used in channels
and as slope protection.Note: these are typical only; all blankets must be installed per
manufacturer's installation instructions.
Installation is critical to the effectiveness of these products. If good ground contact is not
achieved, runoff can concentrate under the product,resulting in significant erosion.
Blanlcets on slopes shall be installed according to manufacturer's instructions. Further guidance
may be obtained from the 2005 Ecology Stormwater Management Manual for Western
Washington.
Jute matting must be used in conjunction with mulch (BMP C121). Excelsior,woven straw
blankets and coir(coconut fiber)blanlcets may be installed without mulch.
In general, most nets (e.g.,jute matting)require mulch in order to prevent erosion because they
have a fairly open structure. Blankets typically do not require mulch because they usually
provide complete protection of the surface.
Extremely steep, unstable,wet, or rocky slopes are often appropriate candidates for use of
synthetic blanlcets, as are riverbanlcs,beaches and other Iligh-energy environments. If synthetic
blankets are used, the soil should be hydromulched first.
Maintenance Standards
Good contact with the ground must be maintained, and erosion must not occur beneath the net or
blanket.
Any areas of the net or blanlcet that are damaged or not in close contact with the ground shall be I
repaired and stapled. ;
If erosion occurs due to poorly controlled drainage,the problem shall be fixed and the eroded �
area protected.
�
September 2010 Snohomish County Drainage Manual Volume!I-Construction Stormwater Pollution Prevention 42
� � �
�G
�� '� Cr'
� /��/j��/ � � . . .. �
,�t2•, • .
�/\��\��// /�/��/\�/ \��\m� � o ��/�//��//��
� � � �.
�/��/��/�� � /�/��/��/ �/��, .�/i�/i�/���,
� � {750 m) � � �6'Ii50rtvn) :
Longitudinal AnchorTrench Terminal Slope and Channel Anchor Trench
� ��
I � ,1s � �F iF � �,\i�.
�
P �.,�
� � �
� � � � Stake at 3'-5' �� '
� � (1-1.5m)Intervais. �
� P ,
G' P J"�,.
�� �
P G��a�o,� �'
I P (� 0� P
,
P �
����\/��\/�\/� ,.
(�' ! �\�������\//,;
/��/� Chedc slot at 25'(7.6m)fntero_
P ������'� Isometric Vie�
�
P �/ /�/
��\\i\�i�
P ��
�
� P s•(150mm)
, • /.i,� \\ \ �.
///\�//\�//\�// a �,� (JOOmmJ . �//\\//\� ' •o� • /\///\�//\�
//����\��\��\�\o; �/��' \�\��\ � � �\�j\�j\
�� ��/��/��/��/ ��\� �\��\ (150mm} /�\��\��\
Initial Channel Anchor Trench Intermittent Check Slot
NOTES:
1.Check slots to be constructed per manufacturecs specifications,
2.Staking or stapling layout per manufacturers specifications.
Figure 4.4—Channel Installation
September 2010 Snohomish County Drainage Manua! Volume 1!-Construction Stormwater Pollution Prevention 43
Slope surface shail be smooth 6efore
piacement for proper soii contact. If there is a berm at the
Sta lin attem as er .� top of slope,anchor
P 9 P P upslope af the berm.
manufacturer'srecommendatio�s. �� •'�•'•:�`.'";,,t,i•;,'•',:•;•.
� �� �
Min.2" i i ��': .•:.::�, I I�
Overlap � �
� � _��i!—�Anchor in 6"x6"min.Trench
� i —„—. and staple at 12" intervals.
' �`'�;� � _ li�� Min.6"overfap.
,� � �i `'I'_�.
-I I - -- ^�, .�_ � - I�
'��=1 I I_�f�_���__-��_� '':�::'.': � Staple overlaps
'_i I I—���_�����i�������i��r����� �- max.5"spaang.
Bring material down to a level area,tum
Do not stretch blankets/mattings tight- the end under 4"and staple at 12"intervals.
allow the rolls to mold to any irregularities.
For sbpes less than 3H:1 V,rolls Lime,fertilize,and seed before installation.
may be placed in horizontal strips. Planting of shrubs,trees,etc.Should occur
after installation.
� €'i��t�rc -R.�— Sf�z��c tnctallnti��ii
�
� !�
� �
' � 1
Sepfember 2010 Snohomish County Drainage Manua! Volume!1-Consfruction Stormwater Po!lution Prevention 44
BMP C123: Plastic Covering
Pur ose
P
Plastic covering provides immediate, shoi�t-teim erosion protection to slopes and disturbed areas.
Conditions of Use
Plastic covering may be used on disturbed areas that require cover measures for less than 30
days, except as stated below:
• Plastic is particularly useful for protecting cut and fill slopes and stockpiles. Note: The
relatively rapid breakdown of most polyethylene sheeting malces it unsuitable for long-term
(greater than six months)applications.
• Cleae plastic sheeting can be used over newly-seeded areas to create a greenhouse effect
� and encourage grass growth if the hydroseed was installed too late in the season to establish 75
� percent grass cover, or if the wet season stacted earlier than normal. Clear plastic should not be
used for this puipose during the summer months because the resulting high temperatures can kill
the grass.
• Due to rapid iunoff caused by plastic sheeting, this method shall not be used upslope of
areas that might be adversely impacted by concentrated runoff. Such areas include steep and/or
unstable slopes.
• Whenever plastic is used to protect slopes, water collection measures must be installed at
the base of the slope. These measures include plastic-covered berms, chatuiels, and pipes used to
covey clean rainwater away from bare soil and disturbed areas. At no time is clean runoff from a
plastic covered slope to be mixed with dii-ty ivnoff from a project.
Plastic covering may also be used foi:
• Temporary ditch liner;
• Pond liner in temporary sediment pond;
e Liner for bermed temporary fuef storage area if plastic is not reactive to the type of fuel I��
being stored; ',
• Emergency slope protection during heavy rains; and, ;
• Temporary drainpipe ("elephant trunlc"}used to direct«�ater. I
�
September 2010 Snohomish County Drainage Manua! Vo/ume I!-Construction Stormwater Pollufion Prevention 45
Design and Installation Specifications
Plastic sheeting shall have a minimum thickness of 6 mils (0.006 inches, or 0.15 mm).
Plastic slope cover must be installed as follows:
• Run plastic up and down slope,not across slope;
• Plastic may be installed perpendicular to a slope if the slope length is less than 10 feet;
. Minimum of 8-inch overlap at seams;
• On long or wide stopes, or slopes subject to wind, all seams should be taped;
• Place plastic into a small(12-inch wide by b-inch deep) slot t�•ench at the top of the slope
and bacl�ll with soil to lceep water fi•om flowing underneath;
e Place sand filled burlap or geotextile bags every 3 to 6 feet along seams and pound a
wooden stake tht•ough each to hold them in place;
. Inspect plastic for rips,tears, and open seams regularly and repair immediately. This
prevents high velocity runoff fi•om contacting bare soil which causes extreme erosion;
• Sandbags may be lowered into place tied to ropes. However, all sandbags must be stalced
in place.
• If erosion at the toe of a slope is likely, a gravel berm, riprap, or other suitable protection
shall be installed at the toe of the slope in order to reduce the velocity of i�unoff
Maintenance 5tandards
• Torn sheets must be replaced and open seams repaired.
• If the plastic begins to deteriorate due to ultraviolet radiation, it inust he completely
removed and replaced.
• When the plastic is no longer needed, it shall be completely removed.
Septen�ber 2090 Snohomrsh County Drainage Manual Vo!ume!1-Construction Sform�rvater Pollution Prevenfion 46
4.2 Runoff Conveyance and Treatment BMPs
BMP C200: Interceptor Dilce and S���ale
Purpose
Provide a ridge of compacted soil,or a ridge with an upslope swale, at the top or base of a
disturbed slope or along the perimeter of a disturbed construction area to convey stormwater.
Use the dilce and/or swale to intercept the runoff from unprotected areas and direct it to areas
where erosion can be controlled. This can prevent storm runoff from entering the worlc area or
sediment-laden runoff fi•om leaving the construction site.
Conditions of Use
Where the iunoff fi•om an exposed site or disturbed slope must be conveyed to an erosion control
facility which can safely convey the stormwater.
Locate upslope of a constcuction site to prevent runoff from entering disiurbed area. �
� When placed horizontally act•oss a disturbed slope, it reduces the amount and velocity of runoff
flowing down the slope.
Locate downslope to collect runoff from a disturbed area and direct it to a sediment basin.
Design and Installation Specifications
Dilce and/or swale and channel must be stabilized with temporary or permanent vegetation or other ,
channel protection during construction. .
Channel requires a positive grade for drainage; steeper grades require channel protection and
check dams.
Review construction for areas where overtopping may occur.
Can be used at top of new fill before vegetation is established. j
May be used as a pei7nanent diversion channel to carry the iunoff. I
Sub-basin tributary area should be one acre or less.
Design capacity for the pealc flow fi•om a 10-year, 24-hour storm, assuming a Type lA rainfall
distribution, for temporary facilities. Alternatively, use 1.6 times the 10-year, 1-hour flow
indicated by an approved continuous runoff model. Facilities that will also seive on a permanent
basis must be designed and consti�ucted in accordance with Chapters 30.63A and 30.63B SCC,
and Snohomish County EDDS.
September 201 D Snohomish County Drainage Manua! Volume!!-Construction Stormwater Pollufion Prevention 67
Dike material compacted
90°/a modified proctor
CPEP or equivalent pipe
.:«Y�
: �—�� (� � �
��=��WT Interceptor Dike'
�� - �(�I-�_ ��\ �.. 12' AIIN..:
� . �-)��- .. � � �
,� � �� — Provide riprap pad
� �=-�� or equivalent energy �
- dissipafion
Discharge to a stabilized Standard flared
watercourse,sediment retention end section
facility,or stabilized outlet
Inlet and all sections must be
securely fastened together
with gasketed tivatertighifittings
Figure 4.10 -Pipe Slope Drain
September 2010 Snohomish County Drainage N,anual Volume 11-Construction Stormwater Pollution Prevention 80
( u
I
BMP C201: Grass-Lined Channels
Purpose
To provide a channel with a vegetative lining for conveyance of runoff. See Figure 4.8 for
typical grass-lined channels.
Conditions of Use
This practice applies to construction sites where concentrated runoff needs to be contained to
prevent erosion or flooding.
When a vegetative lining can provide sufficient stability for the channel cross section and at
lower velocities of water(normally dependent on grade). This ineans that the channel slopes are
generally less than 5 percent and space is available for a relatively large cross section.
Typical uses include roadside ditches,channels at property boundaries,outlets for diversions,
and other channels and drainage ditches in low areas.
Channels that will be vegetated should be installed before major earthworlc and hydroseeded
with a bonded fiber matrix{BFNI}, The vegetation should be well established(i.e., 75 percent
cover)before water is allowed to flow in the ditch. With channels that will have high flows,
erosion contcol blankets should be installed over the hydt•oseed. If vegetation cannot be
established from seed before v�later is allowed in the ditch, sod should be installed in the bottom
of the ditch in lieu of hydromulch and blankets.
Design and Installation Speci�cations
Locate the channel where it can conform to the topography and other features such as roads.
Locate them to use natural drainage systems to the greatest extent possible.
Avoid sharp changes in alignment or bends and changes in grade.
Do not reshape the Iandscape to fit the drainage channel.
The maximum design velocity shall be based on soil conditions,type of vegetation, and method
of revegetation,but at no times shall velocity exceed 5 feet/second. The channel shall not be
ovei�topped by the peak runoff from a 10-year, 24-hour storm, assuming a Type lA rainfall
distributian." Alternatively,use 1.6 times the 10-year, 1-hour flow indicated by an approved
continuous runoff model to determine a flow rate which the channel must contain.
Grass-lined channels that will also function as pet•manent stormwater conveyance facilities must
be designed and constructed in accordance with Chapters 30.63A and 30.63B SCC, and
Snohomish County EDDS.
An established grass or vegetated lining is required before the channel can be used to convey
stormwater,unless stabilized with nets or blankets.
If design velocity of a channel to be vegetated by seeding exceeds 2 ft/sec, a temporary channel
liner is required. Geotextile or special mulch protection such as fiberglass roving or straw and
netting provide stability until the vegetation is fully established. See Figure 4.9.
September 2090 Snohomish County Drainage Manual Volume Il-Consfruction Stormwater PoNution Prevention 70
Check dams shall be removed when the grass has matured sufficiently to protect the ditch or
- swale unless the slope of the swale is greater than 4 percent. The area beneath the check dams
shall be seeded and mulched immediately after dam removal.
If vegetation is established by sodding,the pennissible velocity for established vegetation may
be used and no temporary liner is needed.
Do not subject grass-lined channel to sedimentation from disturbed areas. Use sediment-
trapping BMPs upstream of the channel.
V-shaped grass channels generally apply where tlie quantity of water is small, such as in short
reaches along roadsides. The V-shaped cross section is least desirable because it is difficult to
� stabilize the bottom where velocities may be high. '�
Trapezoidal grass channels are used where runoff volumes are large and slope is low so that
velocities are nonerosive to vegetated linings. (Note: it is difficult to construct small parabolic
� shaped channels.)
Subsurface drainage, or riprap channel bottoms, may be necessary on sites that are subject to
prolonged wet conditions due to long duration flows or a high water table.
Provide outlet protection at culvert ends and at channel intersections.
Grass channels, at a minimum, should cai-�y peak ivnoff for temporary construction drainage
facilities fiom the 10-year,24-hour storm without eroding. Where flood hazard exists, increase
the capacity according to the potential damage.
Grassed channel side slopes aene►•ally are c.onsti•ucted 3:1 oi-flatter to aid in t}le establishnle►lt of
vegetation and for maintenancc.
COI1StCUCtC�l8C1C101Sa1211T11i11U1I1 Ot��.� tOOI 1;11'�_�'f ;iI'��UIl.! I'1C [�:C�F`�1�:�V� I�=) ;1����'.1� l��l' ����I� ��LI���lll_
C�U''1[lt� >Z�C�f�c'Cj l�t'C���t'3tl(1!1C :l!l�j ��i�� �".I;�i{Li�� �
Jlaiutcna�icc �taut�tar�l•�
During the establishmeut periuc�; cil��i: brass-lined ciiailn�l� ait�r e���ry rainTai�
After grass is established,periodically check the channel; checic it after every heavy rain[
event. Immediately malce repairs.
It is particularly important to check the channel ovtlet and all road ci�ossings for banlc stab i I i i�
and evidence of piping or scouc holes.
Remove all significant sediment accumulations to maintain the designed can•ying capacity.
Keep the grass in a healthy, vigorous condition at all times, since it is the primary erosion
protection for the channel.
September 2090 Snohomish County Drainage Manua/ Volume!I-Construction Sformwater Po!lufion Prevention 71
Typical V-Shaped Channel Cross-section
��� ���� +i �, ����
� ����1 ��1���, /� �'��/ri \��,1
�i\\\j\��///� 11`�^\\\\ .�\/\�//� t\�\ \\//�/
,��V
i �
i��/��l/��.,y �����"����\��'/ /
% � M
�\j���//� \��, / ���� �6 -9
Filter � /\�/ (�50-225mm)
Fabric ���i�/�� Key in Fabric
Grass-Lined � With Rock Center
Typical Parabolic Channel Cross-Section
�li li�v, 1�'�i���� til�i,\��li I a\,�1��h�\I..�h�l ,a
r�l�f�G;� �, ' h���lG,
��\ ,� ����' �1.� �1�����'��� �/i��/ ��i�. ��'� �r „�� /�//
:�/. „ .
� ���'���Iii,�V- � / g^-g��� ,\� ��
��\� \ \ •�\, ' (150-225mm) \ \ \, /��Filter
�i��/��i�� Key In Fabric ��// //,/
Fabric
With Channel Liner With Rock Center
f�r Base Flow
Typical Trapezoidal Channel Cross-Section
I.���ii�v, I� �ti��v1Vl� f �
�, ` v,� Design Depth �ia��
�//�//� ��,���f ����' // �/��//\.
�\�/\ /,�� , ' / /
\�� � �//�,
�, .
��\.•I�G '��IVIi1„7 U�r�,�tilvJ,v�l� �J Idl��1��5b�i����V���^ �/��\/
vercut channel 2^(6omm� / / / / / / /
to allow bulking during .��,���,.��j���j ��,�\��\���
seedbed preparation ,�/���
and growth of vegetation. Filter� With Rock Center For Base Flow
Fabric
Figure 4.8—Typical Grass-Lined Channels
Sepfember 2010 Snohomish County Drainage Manual Volume!!-Consfrucfron Stormwater Pollution Prevention 72 I'
�'�iG,; Overlap 6"(150mm) minimum i��
� '�7 y�� �
�\ \� '�� ,� Excavate Channel to Design ��,�� / /
�,\ \�///, \� �� �i Grade and Cross Section \��� � /\�///
' ���//� ,./���i
,� �T��, �,�.
� �� �i,� Design Depth �
���
OVERCUTCHANNEL �=G�, ' Longitudinal
2'(50mm)TOALLOW ''-� �V� anchor trench
BULK/NGDUA/NGSEEDBED �/ ��'�� i41r/, .l�l .V� �d�
PHEPAHAT/ON �
�//�/�.//��///�/i
�'
� P e•(tsomm) TYPICAL/NSTALLAT/ON
W/THEROS/ONCONTROL �/��/
/��/�� '� � �/� /� /� BLANKETS OR TURF ��� �� ���j���
�/\�/\�':° � �\\/\\ HE/NfORCEMENT MATS ��/\/\�/ /\�/\�/\�
�/��//�� �s• ,� � /��/��/ ��\\��\\�� ���\\��\\��
�\ �\ (150mm) /�� ��j� /��/��/\n5oinm) \�\��
Intermittent Check Slot Longitudinal Anchor Trench
Shingle-lap spliced ends or begin new
roll in an intermittent check slot
� -�� w�-
Prepare soi!and apply seed before � O � ,
installing blankets,mats or other � LL ��
temporary channel liner system (7 � W
V '�
��� �� �U ��
. � v� � . .
�
� �v�� ,� v� ��-- ;
�'`�'� � � ��,
��. X� . .
,�i '��r�!�
� �
',�\��;�j\\//,i,,�j�
NOTES:
����
1.Design velocities exceeding 2 ft/sec(O.Sm/sec)require temporary blankets,mats or similar
liners to protect seed and soil until vegetation becomes established.
2.Grass-lined channels with design velocities exceeding 6 ft/sec(2m/sec)should include
turf reinforcement mats,
Figure 4.9—Temporary Channel Liners
Sepfember 201 D Snohomisl�County Drainage Manual Volume 11- Consfruction Stormwafer Po!lution Prevenfion 73
BMP C207: Check Dams
Purpose
Construction of small dams across a swale or ditch reduces the velocity of concentrated flow and
dissipates energy at the checic dam.
Conditions of Use
Where temporary channels or permanent channels are not yet vegetated, channel lining is
infeasible, and velocity checks are required.
NOTE: use of check dams in receiving waters may require approval from Washington State
Department of Fish and Wildlife or other state or federal regulatory agencies.
Design and Installation Speci�cations
Whatever material is used,the dam should form a triangle when viewed fi•om the side. This
prevents undercutting as water flows over the face of the dam rather than falling directly onto the
ditch bottom.
Check dams in association with sumps work more effectively at slowing flow and retaining
sediment than just a checic dam alone. A deep sump should be provided immediately upstream
of the checic dam
In some cases, if carefully located and designed, check dams can remain as permanent
installations with very minor regrading. They may be left as either spillways, in which case
accumulated sediment would be graded and seeded, or as check dams to prevent further sediment
from leaving the site.
Check dams can be constructed of either rock or pea-gravel filled bags. Numerous new products '
are also available for this purpose. They tend to be re-usable, quick and easy to install, effective, �
and cost efficient. '
Check dams should be placed perpendicular to the flow of water. I
The maximum spacing between the dams shall be such that the toe of the upstream dam is at the
same elevation as the top of the downstream dam. ;
Keep the maximum height at 2 feet at the center of the dam. I
Keep the center of the checic dam at least 12 inches lower than the outer edges at natural ground
elevation.
ICeep the side slopes of the checic dam at 2:1 or flatter.
Key the stone into the ditch banks and extend it beyond the abutments a minimum of 18 inches
to avoid washouts from overflow around the dam.
Use filter fabric foundation under a rock or sand bag check dam. If a blanlcet ditch liner is used,
this is not necessary. A piece of organic ar synthetic blanket cut to fit will also work for this
purpose.
September 2090 Snohomish County Drainage Manual Volume!!-Construction Stormwater Pollution Prevention 86
Rocic checic dams shall be constructed of appropriately sized rock. The rocic must be placed by
hand or by mechanical ineans (no dumping of rocic to form dam)to achieve complete coverage
of the ditch or swale and to ensure that the center of the dam is lower than the edges. The rocic
used must be large enough to stay in place given the expected design flow through the channel.
In the case of grass-lined ditches and swales, all check dams and accumulated sediment shall be
removed when the grass has matured sufficiently to protect the ditch or swale -unless the slope
of the swale is greater than 4 percent. The area beneath the checic dams shall be seeded and
mulched immediately after dam removal.
Ensure that channel appurtenances, such as culvert entrances below check dams, are not subject
to damage or blockage from displaced stones. Figure 4.13 depicts a rypical rock check dam.
Maintenance Standards
Check dams shall be monitored for performance and sediment accumulation during and after
each runoff producing rainfall. Sediment shall be removed when it reaches one half the sump
depth.
Anticipate submergence and deposition above the checic dam and erosion fi•om high flows
around the edges of the dam.
If significant erosion occurs behueen dams, install a protective riprap liner in that portion of the
channel.
i
�
September 2010 Snohomish County Drainage Nanua! Volume I!-Construction Sformwater Pollufion Prevention 87
View Looking Up�tream 1s��a.5m)
A
12"{15amm)
�
�\\�\\�� �\ ��o: �o��"c� • o (� ����� /\ /.' %.//,.///.
�/.�/��� �' e��aQa���`-'o� �����"o��� °��� 24"{Q.�fTI}
NOTE: \ �� e-�',�o�"�����O°p ��g00;� ° �i, �j\ j
e 2:b4Y�'�'��o° r
extend It beyond the abuiments� �\� ������i\��//
minim�un of 18"(O.�m}io prevent A
flow around dam.
Section A - A
�zow �
~`-� 24"(0.6m) d
I ooe
�o
� �e o �
','\//\\\//\\\// / g �\ oe �Q�oo e,00�a
.//,,/i• '� i��/ \ ��\��\f�\�\�\' \i
� ,�\��\��\/���/ti�l��i���j/�\�/ /�\�/�
�/\\.,/ ���
8'{2.4m}
� Spacing Between Check Dams ;,
'L'=1he distanoe such ihat paints'A'and
'B'are of equal elevation.
'L'
a
0
g , a °�.��.�°�4 �� PoiNr�A, Poinrr�e�
�����\/j�\/��\j�\/�\/�\/�j�j ��, . .
r,��i.�/i./�. /..//�\��\��\��\�\�\ \ �. a ���jo,..o
\\/�\�/��\����\\/��\\���\�%\�/\���%��'��/ �/ / /
�.�\,��j���\��\��
/�,./i,
NOT 70 SCALE
Figure 4.13—Check Dams
� i
��
September 2010 Snohomish Counfy Drainage Manual Volume ll-Constructron Stormwater Pollution Prevention 88
BMP C151: Concrete Handling
Purpose
Concrete work can generate process water and slurry that contain fine particles and high pH,
both of which can violate water quality standards in the receiving water. This BMP is intended
to minimize and eliminate concrete process water and slurry from entering waters of the state.
Conditions of Use
Any time concrete is used,these management practices shall be utilized. Concrete construction
projects include, but a��e not limited to,the following:
• Curbs
• Sidewalks
• Roads
• Bridges
• Foundations
• Floors
. Runways
Design and Installation Speci�ications
Concrete truck chutes,pumps, and internals shall be washed out only into formed areas awaiting
installation of concrete or asphalt.
Unused concrete remaining in the truck and pump shall be returned to the originating batch plant
for recycling.
Hand tools including,but not limited to, screeds, shovels, rakes, floats, and trowels shall be
washed off only into formed areas awaiting installation of concrete or asphalt.
Equipment that cannot be easily moved, such as concrete pavers, shall only be washed in areas
that do not directly drain to natural or constructed stormwater conveyances.
Washdown from areas such as concrete aggregate driveways shall not drain directly to natural or ,
constructed stormwater conveyances. �'
When no formed areas are available,washwater and leftover product shall be contained in a lined !
container. Contained concrete shall be disposed of in a manner that does not violate groundwater '
or surface water quality standards. �I
Maintenance Standards
Containeis shall be checked for holes in the liner daily during concrete pours and repaired the ,
same day. ��
��
I
September 2090 Snohomish Counry Drainage Manua! Volume I!-Construction Stormwater Pollution Prevention 63 �I
BMP C152: Sawcutting and Surfacing Pollution Prevention
Purpose
Sawcutting and surfacing operations generate slurry and process water that conta.ins fine particles
and high pH (concrete cutting),both of which can violate the water yuality standards in the
receiving water. This BMP is intended to minimize and eliminate process water and sluriy from
entering waters of the State.
Conditions of Use
Anytime sawcutting or surfacing operations talce place,these management practices shall be
utilized. Sawcutting and sut�facing operations include, but are not limited to, the following:
• Sawing
. Coring
• Grinding
. Roughening
• Hydro-demolition
. Bridge and road surfacing
Design and Installation Specifications
Slurry and cuttings shall be vacuumed during cutting and surfacing operations.
Slurry and cuttings shall not remain on permanent concrete or asphalt pavement overnight.
Slurry and cuttings shall not drain to any natural or constructed drainage conveyance.
Collected slurry and cuttings shall be disposed of in a inanner that does not violate groundwater
or surface water quality standards. I
Process water that is generated during hydro-demolition, surface roughening or similar
o erations shall not drain to an natural or constructed draina e conve ance and shall be I
P Y g Y
disposed of in a manner that does not violate groundwater or surface water quality standards. I
Cleaning waste material and demolition debris shall be handled and disposed of in a manner that
does not cause contamination of water. If the area is sv��ept with a pick-up sweeper,the material �
must be hauled out of the area to an appropriate disposal site. �
Maintenance Standards ;
Continually monitor operations to determine whether slurry, cuttings, or process water could
enter waters of the state. If inspections show that a violation of water quality standards could
occur, stop operations and irrunediately implement preventive measures such as berms, barriers,
secondary containment, and vacuum trucks.
September 2010 Snohomish County Drainage Manua! Volume!I-Consfruction Stormwater Pollufion Prevention 64
• Use geotextile fabrics to increase the strength of new roads or roads undergoing
reconstruction.
• Encourage the use of alternate,paved routes, if available.
• Restrict use by tracked vehicles and heavy trucics to prevent damage to road surface and
base.
. Apply chemical dust suppressants using the admix method, blending the product with the
top few inches of surface material. Suppressants may also be appIied as surface
t►•eatments.
• Pave unpaved permanent roads and other trafficked areas.
• Use vacuum sh•eet sweepers. .
• Remove mud and other dirt promptly so it does not diy and then turn into dust.
• Limit dust-causing«�orlc on windy days.
Maintenance Standards
Respray at•ea as necessary to keep dust to a miniinum.
Sepfember 2090 Snohomish County Drainage f✓lanua! Volume !1- Constrcrction Stormwater Pol(ution Prevenfion 61
APPENDIX D - GENERAL PERMIT
�s�2013 D. R. STRONG Consulting Engineers Inc. Page 24 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
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
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,
iv. 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, tu�bid 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. I
g. General comments and notes, including a brief description of any BMP I
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".
��2013 D. R.STRONG Consulting Engineers Inc. Page 25 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31, 2013
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 heafth or the environment, the Permittee shall
comply with the Noncompliance Notification requirements in Special Condition S5.F of
the permit.
�;2013 D. R. STRONG Consulting Engineers Inc. Page 26 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
SITE INSPECTION FORM
General Information
Project Name:
Inspector Name: Title:
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 Ac`.ion
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Co�rective Action
�I
I
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 Rates
� BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
�_ � _ .� F; ST��":G C ��_„�. F �r � �,_ P 3 " :f��
S'��rr;�a`:r Pol�.f���� Prcven:n�� Pla�� P��par s E�.f' Ja�oary �1 2��13
�
_ _ .
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
Element 4: InstaU 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:
Location Inspected Functioning Problem/Corrective Action
Y N Y � N NIP
BMP: __
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
Element 5: Sfabilize Soils
BMP: _
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Location Inspected Functioning Problem/Corrective Action
Y N Y N NIP
:�2013 D. R. STRONG Consulting Engineers Inc. Page 28 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31, 2013 ,
�
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 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
E/ement 7: Protect Drain Inlets
BM P: .
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP: I
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
O 2013 D. R. STRONG Consulting Engineers Inc. Page 29 of 39 I
Stormwater Pollution Prevention Plan Piper's Bluff January 31, 2013 �
Element 8: Stabilize Channels and Outlets
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 9: Control Po!lutants
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 10: Control Dewatering _ .
BMP: -
inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
BMP:
Inspected Functioning
Location Y N Y N NIP Problem/Corrective Action
O 2013 D.R.STRONG Consulting Engineers Inc. Page 30 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
�
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:
. anspare, _ or le:
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 o No
If photos taken, describe photos below:
O 2013 D.R.STRONG Consulting Engineers Inc. Page 31 of 39
Stormwater Pollution Prevention Plan PipePs Bluff January 31,2013
APPENDIX F - ENGINEERING CALCULATIONS
PRE-DEVELOPED HOURLY TIME STEP MODELING INPUT:
.� . w�t.x - ..
� Land llse Summary , F �`�-�` , ��`'�'' �
�r ,`� �+ �.� Y �.�
�Area 7
Till Forest 4•98 acres
Till Pasture U.00 acres
Till Grass U.00 acres
Outwash Forest U.00 acres
Outwash Pasture 0.00 acres
Ouiwash Grass 0.00 acres
Wetland O.OU acres
Impervious 0.00 acres
Total
� 4.98 acres
Scale Factor : 1.U0 Hourly Reduced
Time Series: predev >?
Compute Time Series I
Modify User Input �
File for computed Time Series [.TSFJ ` `
;� .
PRE-DEVELOPED HOURLY TIMF STFp M�nFi �ti�� ^� !Tp! �T
Flow Frequency Analysis
Time Series File:predev.ts
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Pro'.
(CFS) (CFS) Period
0.314 2 2/09/Ol 18:00 0.402 1 100.00 O. G
0.085 7 1/06/02 3: 00 0.314 2 25.00 0. 9
0.233 4 2/28/03 3: 00 0.241 3 10.00 0. 9�
0.008 8 3/24/04 20:00 0.233 4 5.00 0.8
0.139 6 1/05/05 8:00 0.204 5 3.00 0. 6�
0.241 3 1/18/06 21:00 0. 139 6 2.00 0.5.
0.204 5 11/24/06 4:00 0. 085 7 1.30 0.2
0.402 1 1/09/08 9:00 0.008 8 1. 10 0. 0'
(` -,m•-•.-� `� �,�=1.� . �^'" �!l ^(` !�
_ __ __ _ __
il
DEVELOPED HOURLY TIME STEP MODELING INPUT: '
r� -�- ,, �� � ,�
- � ���,= ..
� Land Use Summary - ��,� .� -
� �:
_. � Area � �
- Till Forest 0.00 acres
Till Pasture 0.00 acres
Till Grass 7•87 acres
Ouiwash Forest 0.00 acres I
Outwash Pasture 0.00 acres
Ouiwash Grass 0.00 acres �i
Wetland 0.00 acres '
Impervious 3.17 acres i
Total
4.98 acres
Scale Factor : 1.00 Hourly Reduced
Time Series: DEV »
Compute Time Series I
Modi User In ut
�Y P
File for computed Time Series [.TSFJ
_ �
DEVELOPED HOURLY TIME STEP MODELING OUTPUT:
Flow Frequency Analysis
Time Series File:dev.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
0.928 6 2/09/O1 2:00 1.88 1 100.00 0. 990
0.757 8 1/05/02 16:00 1. 19 2 25.00 0. 960
1. 12 3 2/27/03 7:00 1. 12 3 10. 00 0.900
0.820 7 8/26/04 2:00 0. 987 4 5. 00 0.800
0. 987 4 10/28/04 16:00 0. 985 5 3.00 0. 667
0. 985 5 1/18/06 16:00 0. 928 6 2.00 0.500
1. 19 2 10/26/06 0:00 0.820 7 1.30 0.231
1.88 1 1/09/08 6:00 0.757 8 1. 10 0.091
Computed Peaks 1.65 50.00 0. 980
G 2013 D.R.STRONG Consuking Engineers Inc. Page 33 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
�
FLOW CONTROL FACILITY DESIGN OUTPUT
Retention/Detention =ac�-lity
Type of Facility: Detention Pond
Side Slope: 3.00 H: 1�T
Pond Bottom Length: 33.00 ft
Pond Bottom Width: 16.00 =t
Pond Bottom Area: 528. sq. ft
Top Area at 1 ft. FB: 13038. sq. ft
0.299 acres
Effective Storage Depth: 14.00 ft
Stage 0 Elevation: 410.00 ft
Storage Volume: 69132. cu. ft
1.587 ac-ft
Riser Head: 14 .00 ft
Riser Diameter: 18.00 inches
Number of orifices: 3
Full Head Pipe
Orifice # Height Diameter Discharge Diameter
(ft) (in) (CFS) (in)
1 0.00 0.88 0.079
2 10.00 1.50 0.122 4.0
3 10.70 1.40 0.097 4.0
Top Notch Weir: None
Outflow Rating Curve: None
�tage Elevation Storage Discharge Percolation-- Surf Area
;-t) (ft) (cu. ft) (ac-ft) (cfs) (cfs) (sq. ft)
' �. GO 410.00 0. 0.000 0.000 0. 00 528.
�. Ol 410.01 5. 0.000 0.002 0. 00 531.
0. 02 410.02 11. 0.000 0.003 0.00 534 .
0.03 410.03 16. 0.000 0.003 0.00 537.
0.04 410.04 21. 0.000 0.004 0.00 540.
0.05 410.05 27 . 0.001 0.005 0.00 543.
0.06 410.06 32. 0.001 0.005 0.00 546.
0.07 410.07 38. 0.001 0.006 0.00 549.
0.35 410.35 203. 0.005 0.012 0.00 635.
0. 62 410.62 387. 0.009 0.017 0.00 724.
0.90 410.90 603. 0.014 0.020 0.00 822.
1.17 411.17 838. 0.019 0.023 0.00 921.
1.45 411.45 1111. 0.026 0.025 0.00 1030.
1.72 411.72 1404. 0.032 0.028 0.00 1140.
1. 99 411.99 1727. 0.040 0.030 0.00 1256.
2.27 412.27 2096. 0.048 0.032 0.00 1381.
2.54 412.54 2486. 0.057 0.033 0.00 1507 .
2.82 412.82 2927 . 0.067 0.035 0.00 1643.
3.09 413.09 3389. 0.078 0. 037 0.00 1780.
3.37 413.37 3908. 0.090 0. 039 0.00 1928 .
3. 64 413.69 4448. 0.102 0.040 0.00 2075.
3. 92 413.92 5052. 0.116 0.042 0.00 2234 .
4. 19 414.19 5676. 0.130 0.043 0.00 2392.
4.47 414 .47 6369. 0.146 0.044 0.00 2561.
4.74 414 .74 7083. 0.163 0.046 0.00 2730.
5.01 415.01 7844. 0.180 0.047 0.00 2905.
O 2013 D.R. STRONG Consufting Engineers Inc. Page 34 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
5.29 415.29 �683. 0. 199 0.048 O. 00 3091.
5.56 415.56 9543. 0.219 0.050 0.00 3276.
5.84 415.84 10487 . 0.241 0.051 0.00 3473.
6.11 416.11 11451. 0.263 0.052 0.00 3668.
6.39 416.39 12507. 0.287 0.053 0.00 3877 .
6.66 416.66 13582. 0.312 0.054 0.00 4083.
6. 94 416.94 14755. 0.339 0. 055 0.00 4302.
7.21 417.21 15946. 0.366 0.056 0.00 4519.
7.49 417.49 17249. 0.396 0.057 0.00 4750.
7.76 417.76 18557. 0.426 0.058 0.00 4977.
8.03 418.03 19932. 0.458 0.060 0. 00 5210.
8.31 418.31 21425. 0.492 0.061 0. 00 5457 .
8.58 418.58 22931. 0.526 0.062 0.00 570-.
8.86 418.86 24564 . 0.564 0.063 0.00 5959.
9.13 419.13 26207. 0. 602 0.063 0.00 6213.
9.41 419.41 27984. 0. 642 0.064 0.00 6482 .
9.68 419. 68 29770. 0.683 0.065 0.00 6747 .
9. 96 419. 96 31698. 0.728 0.066 0.00 7027.
10.00 420.00 31980. 0.734 0.066 0.00 7068.
10.02 420.02 32122. 0.737 0.067 0.00 7088.
10.03 420.03 32192. 0.739 0.068 0.00 7098.
10.05 420.05 32335. 0.742 0.071 0.00 7119.
10.06 420.06 32406. 0.744 0.074 0.00 7129.
10.08 420.08 32549. 0.747 0.078 0.00 7149.
10.09 420.09 32620. 0.749 0.083 0.00 7160 .
10. 11 420.11 32764. 0.752 0.087 0.00 7180.
10. 12 420.12 32835. 0.754 0.088 0.00 7190.
10.40 420.40 34889. 0.801 0.106 0.00 7479.
10. 67 420. 67 36947. 0.848 0. 119 0. 00 7764 .
10.70 420.70 37180. 0.854 0.120 0. 00 7795.
10.71 420.71 37258. 0.855 0.121 0.00 7806.
10.73 420.73 37414. 0.859 0.122 0.00 7827 .
10.74 420.74 37493. 0. 861 0.125 0.00 7838.
10.76 420.76 37650. 0.864 0.128 0.00 7859.
10.77 420.77 37728. 0.866 0. 133 0.00 7870.
10.79 420.79 37886. 0.870 0.138 0.00 7892.
10.80 420.80 37965. 0.872 0.141 0.00 7902.
10.82 420.82 38123. 0.875 0.142 0.00 7924 .
11.09 421.09 40302. 0. 925 0.167 0.00 8216.
11.37 421.37 42646. 0. 979 0.185 0.00 8525.
11. 64 421.64 44988. 1.033 0.201 0.00 8828.
11. 91 421. 91 47413. 1.088 0.216 0.00 9136.
12. 19 422.19 50017. 1.148 0.228 0.00 9461.
12. 46 422.46 52614. 1.208 0.241 0.00 9780.
12.74 422.74 55400. 1.272 0.252 0.00 10117 .
13.01 423.01 58175. 1.336 0.263 0.00 10446.
13.29 423.29 61149. 1.404 0.273 0.00 10794 .
13.56 423.56 64109. 1.472 0.282 0.00 11134 .
13.84 423.84 67277. 1.544 0.292 0.00 11493.
14 . 00 424.00 69132. 1.587 0.297 0.00 1170'
14 . 10 424 .10 70309. 1. 614 0.762 0.00 1183"
14 .20 424 .20 71498. 1. 641 1. 610 0.00 1196.
14.30 424 .30 72701. 1. 669 2.710 0.00 120G ": .
14.40 424 .40 73917. 1. 697 4.010 0.00 1222� .
14 .50 424 .50 75146. 1.725 5.480 0.00 12360 .
�4 . 6C 424 .60 76309. 1.754 6. 910 0.00 1249� .
14 .;� 429 .7C 7?6�5. l.?�2 7 . 4'-_� �.00 12629.
O 2013 D. R.STRONG Consulting Engineers Inc. Page 35 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
14.80 424.80 78915. 1.812 7. 930 0.00 12765.
14.90 424.90 80198. 1.841 8.400 0.00 12901.
15.00 425.00 81495. 1.871 8.840 0.00 13038.
15.10 425.10 82806. 1. 901 9.260 0.00 13176.
15.20 425.20 84130. 1. 931 9.660 0.00 13314 .
15.30 425.30 85969. 1. 962 10.040 0.00 13953.
15.40 425.40 86821. 1. 993 10.410 0.00 13593.
15.50 425.50 88187. 2.025 10.760 0.00 13734.
15.60 425.60 89568. 2.056 11.110 0.00 13875.
15.70 425.70 90962. 2.088 11.440 0.00 14017.
15.80 425.80 92371. 2.121 11.770 0.00 14160.
Hyd Inflow Outflow Peak Storage
Target Calc Stage Elev (Cu-Ft) (Ac-Ft)
1 1.88 ******* 0.28 13.49 423.49 63386. 1.455
2 0. 93 0.31 0.25 12.72 422.72 55199. 1.267
3 1.12 ******* 0.22 11.94 421. 94 47731. 1.096
� 0. 93 ******* 0.22 11.94 421.94 47716. 1.095
5 0. 99 ******* 0.16 11.05 421.05 39968. 0. 918
5 0.58 ******* 0.10 10.23 420.23 33669. 0.773
? 0.76 ******* 0.06 9.39 419.39 27883. 0.640
8 0.82 ******* 0.06 8.21 418.21 20902. 0.480
----------------------------------
R.cute Time Series through Facility
Inflow Time Series File:dev.tsf
Ostflow Time Series File:rdout
Tnflow/Outflow Analysis
Peak Inflow Discharge: 1.88 CFS at 6:00 on Jan 9 in Year 8
?eak Outflow Discharge: 0.280 CFS at 14:00 on Jan 9 in Year 8
?eak Reservoir Stage: 13.49 Ft
Peak Reservoir Elev: 423.49 Ft
Peak Reseraoir S�oraae: 63386. Cu-Ft
. 1.455 Ac-Ft
Flow Frequency Anaiysis
Time Series File:rdout.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) (ft) Period
0.251 2 2/09/O1 21:00 0.280 13.49 1 100.00 0. 990
0.064 7 1/07/02 4:00 0.251 12.72 2 25.00 0. 960
0.217 3 3/06/03 22:00 0.217 11. 94 3 10.00 0. 900
0.061 8 8/26/04 7:00 0.217 11.94 4 5.00 0.800
0.095 6 1/08/05 3:00 0.163 11.05 5 3.00 0. 667
0.163 5 1/19/06 0:00 0.095 10.23 6 2.00 0.500
0.217 4 11/24/06 8:00 0.064 9.42 7 1.30 0.231
0.280 1 1/09/08 14:00 0.061 8.21 8 1. 10 0.091
Ccmputed Peaks 0.270 13.2i 50. 00 0. 9�0
Flo:�� ��ura�io� frcm ,_rr.� Ser_�s F=_=e:r���Lt.tsf
C 2013 D. R. STRONG Consulting Engineers Inc. Page 36 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31, 2013
Cutoff Count Frequency CDF Exceedence Probability
CFS � a $
0.004 37253 60.752 60.752 39.248 0.392E+00
0.011 2181 3.557 64.309 35. 691 0.357E+00
0.018 2049 3.341 67.650 32.350 0.323E+00
0.025 2774 4.524 72.174 27.826 0.278E+00
0.032 2761 4.503 76. 676 23.324 0.233E+00
0.039 3214 5.241 81. 918 18.082 0. 181E+00
0.046 3815 6.221 88. 139 11.861 0.119E+00
0.053 2842 4.635 92.774 7.226 0.723E-01 ,
0.060 1950 3.180 95.954 4.046 0. 405E-01
0. 067 1952 3.183 99.137 0.863 0.863E-02
0. 074 34 0.055 99.193 0.807 0.807E-02
0.081 20 0.033 99.225 0.775 0.775E-02
0.088 43 0.070 99.296 0.705 0.705E-02
0.095 57 0.093 99.388 0. 612 0. 612E-02
0.102 44 0.072 99.460 0.540 0.540E-02
0.109 51 0.083 99.543 0.457 0.457E-02
0.116 51 0.083 99. 627 0.373 0.373E-02
0.123 34 0.055 99.682 0.318 0.318E-02
0.130 9 0.015 99. 697 0.303 0.303E-02
0. 137 6 0.010 99.706 0.294 0.294E-02
0.145 10 0.016 99.723 0.277 0.277E-02
0. 152 12 0.020 99.742 0.258 0.258E-02
0. 159 19 0. 031 99.773 0.227 0.227E-02
0. 166 19 0. 031 99.804 0.196 0.196E-02
0.173 15 0.024 99.829 0.171 0. 171E-02
0.180 14 0.023 99.852 0. 148 0. 148E-02
0.187 7 0.011 99.863 0. 137 0.137E-02
0.194 12 0.020 99.883 0. 117 0.117E-02
0.201 9 0.015 99.897 0.103 0.103E-02
0.208 10 0.016 99.914 0.086 0.864E-03
0.215 10 0.016 99.930 0.070 0.701E-03
0.222 16 0.026 99.956 0.044 0.440E-03
0.229 10 0.016 99.972 0.028 0.277E-03
0.236 4 0.007 99.979 0.021 0.212E-03
0.243 4 0. 007 99.985 0.015 0.147E-03
0.250 6 0.010 99.995 0.005 0.989E-04
Duration Comparison Anaylsis
Base File: predev.tsf
New File: rdout.tsf
Cutoff Un�ts: Discharge in CFS
-----Fraction of Time----- ---------Check of Tolerance-------
Cutoff Base New oChange Probability Base New °Change
0.069 I 0. 94E-02 0.83E-02 -11. 6 I 0.94E-02 0.069 0.066 -4 . 5
0.088 I 0.62E-02 0.70E-02 13. 1 � 0.62E-02 0.088 0.095 7 . 4
0.107 I 0. 49E-02 0.48�-02 -1.3 � 0.49E-02 0.107 0.107 -0.3
0.126 I 0. 37E-02 0.31E-02 -16.4 I 0.37E-02 0.126 0.117 -7. 0
0. 145 � 0.28E-02 0.28E-02 -2.3 � 0.28E-02 0. 145 0.142 -1. 6
0. 163 I 0.22E-02 0.21E-02 -7.4 I 0.22E-02 0. 163 0.160 -1.8
0. 182 � 0.15E-02 0.15E-02 -1.1 � 0.15E-02 0.182 0.182 -0.3
0.201 I O.10E-02 O.10E-02 1.6 I O.10E-02 0.201 0.202 0. 6
0.220 I 0. 62E-03 0.49E-03 -21.1 I 0.62E-03 0.220 0.217 -1. 5
0.239 � 0.34E-03 0.18E-03 -47.6 I 0.34E-03 0.239 0.226 -5.2
0.257 I 0.21E-03 O.00E+00 -100.0 I 0.21E-03 0.257 0.238 -7. 5
0.275 � 0.16E-03 O. OGE+OC -"�_00. 0 � 0. 16�-03 0.276 0.243 -12. i
v 2013 D. R. STR�NG Consulting Engineers Inc. Page 37 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31, 2013
0.295 I 0. 11E-G3 C. 00�+CO -1�0.0 ' 0. "_lE-�3 0.295 G.246 -16. 5
0. 314 � 0. 16E-04 O.00E+00 -100.0 I 0.16E-04 0. 314 0.25i -19. 9
Maximum positive excursion = 0.007 cfs ( 8. 6%)
occurring at 0.081 cfs on the Base Data:predev.tsf
and at 0.088 cfs on the New Data:rdout.tsf
Maximum negative excursion = 0.063 cfs (-19. 9%)
occurring at 0.314 cfs on the Base Data:predev.tsf
and at 0.251 cfs on the New Data:rdout.tsf
----------------------------------
Route Time Series through Facility
Inflow Time Series File:dev.ts{
Outflow Time Series F_le:rdoi�
Inflow/Outflow Analysis
Peak Inflow Discharge: 1.88 CFS �t 6:00 on Jan 9 in Year 8
Peak Outflow Discharge: 0.280 CFS at 14 :0� o� Jan 9 ir_ Y�ar 8
Peak Reservoir Stage: 13.49 Ft
Peak Reservoir Elev: 423.49 Ft
Peak Reservoir Storage: 63386. Cu-=t
. 1. 455 rc-F�
Flow Frequency Analys_s
Time Series File:rdout.tsf
Project Location:Sea-Tac
' ---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) (ft) Period
0.251 2 2/09/Ol 21:00 0.280 13.49 1 100.00 0. 990
0.064 7 1/07/02 4:00 0.251 12.72 2 25.00 0. 960
0.217 3 3/06/03 22:00 0.217 11. 94 3 10.00 0.900
0.061 8 8/26/04 7:00 0.217 11. 94 4 5.00 0.800
0.095 6 1/08/05 3:00 0.163 11.05 5 3.00 0.66�
0.163 5 1/19/06 0:00 0.095 10.23 6 2.00 0.500
0.217 4 11/24/06 8:00 0.064 9.42 7 1.30 0.231
0.280 1 1/09/08 14:00 0.061 8.21 8 1.10 0.091
Computed Peaks 0.270 13.21 50. 00 0.980
Flow Duration from Time Series File:rdout.tsf
Cutoff Count Frequency CDF Exceedence Probability
CFS a °s %
0.004 37253 60.752 60.752 39.248 0.392E+00
0.011 2181 3.557 64.309 35. 691 0.357E+00
0.018 2099 3.341 67.650 32.350 0.323E+00
0.025 2774 4 .524 72.174 27.826 0.278E+00
0.032 2761 4.503 76.676 23.324 0.233E+00
0.039 3214 5.241 81.918 18.082 0.181E+00
0.046 3815 6.221 88.139 11.861 0. 119E+00
0.053 2842 9 . 635 92.774 7.226 0.723E-01
0.060 1950 3. 180 95.954 4.046 0.405E-01
0.067 1952 3.183 99.137 0.863 0.863E-02
0.074 34 0.055 99.193 0.807 0.807E-02
0.081 20 0.033 99.225 0.775 0.775E-02
0.088 43 0.070 99.296 0.705 0.705E-02
O 2013 D.R.STRONG Consufting Engineers Inc. Page 38 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
---,
0.095 57 0.093 99.388 0. 612 0. 612E-02
0.102 44 0.072 99.460 0.540 0.540E-02
0. 109 51 0.083 99.543 0.457 0.457E-02
0.116 51 0.083 99.627 0.373 0.373E-02
0.123 34 0.055 99.682 0.318 0.318E-02
0.130 9 0.015 99.697 0.303 0.303E-02
0.137 6 0.010 99.706 0.294 0.294E-02
0.145 10 0.016 99.723 0.277 0.277E-02
0.152 12 0.020 99.742 0.258 0.258E-02
0.159 19 0.031 99.773 0.227 0.227E-02
0.166 19 0. 031 99.804 0.196 0.196E-02
0.173 15 0.024 99.829 0.171 0.171E-02
0.180 14 0.023 99.852 0.148 0.148E-02
0.187 7 0.011 99.863 0.137 0.137E-02
0.194 12 0.020 99.883 0. 117 0.117E-02
0.201 9 0.015 99.897 0. 103 0.103E-02
0.208 10 0.016 99.914 0.086 0.864E-03
0.215 10 0.016 99. 930 0.070 0.701E-03
0.222 16 0.026 99. 956 0.044 0.440E-03
0.229 10 0.016 99. 972 0.028 0.277E-03
0.236 9 0.007 99. 979 0.021 0.212E-03
0.243 4 0.007 99. 985 0.015 0. 147E-03
0.2�0 0 �.0"'-0 99.
DURATION ANALYSIS
N
� fdOULduf O
R targetdur •
m
0
v
d
0
�
0
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l0 5 � � ��0-0 � 10 3 10 2 '10 � 10�
Probab�:ity F�ccer'ence
G 2013 D. R.STRONG Consulting Engineers Inc. Page 39 of 39
Stormwater Pollution Prevention Plan Piper's Bluff January 31,2013
� y �
1
PUBLIC WORKS DEPARTMENT p �� •�f�O� ��
M E M O R A N D U M
DATE: September 25, 2013
TO: Jan 111ian, Plan Reviewer
Dan Thompson, Construction Inspector
FROM: G2�on Straka, Surface Water Utility Supervisor, x7248
STAFF CONTACT: Hebe C. Bernardo, Surface Water Utility Engineer,x7264
SU6IECT: Piper's Bluff—Bay SaverT'"Adjustment 2013-04
The Surface Water Utility has completed review of the adjustment request from
WestPac Development LLC for the Piper's Bluff Subdivision 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 engineer 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 applicant engineer on October 16, 2012,
provides the following findings:
1. The projed went through drainage review in 2012-2013. Plans were approved
for construction in May 2013. The projed is currently under construdion. The
construction permit number is U13000618.
2. The projed was originally approved using Contech Cartridge system for basic
water quality treatment mitigation, per City adopted standards. WestPac
Development is requesting a substitution of cartridge systems(from Contech
Cartridge System to Bay Saver'" Cartridge System) due to Contech's inability to
meet the production schedule.
The adjustment request proposes to use the Bay Saver'"' Cartridge System for Basic
Water Quality treatment. The Washington State Department of Eco(ogy has approved
the Bay SaverT"" Cartridge System'"'for General Use Level Designation for Basic Water
Quality treatment.
Based on the information provided in the adjustment request,the Bay Saver"" Cartridge
System for Basic Water Quality Treatment is approved with the following conditions:
. � .
<
Ms.Illian
Page 2 of 3
September 25,2013
1. The as-built.construction plans that are prepared following the completion of the
project construction are to be updated to include the details and information
associated with Bay SaverT"' Cartridge System that is being installed instead of
the Contech Cartridge System that was shown on the approved construction
plans.
2. The water quality design flow shall be as listed in the General Use Level
Designation for Bay SaverT"" Cartridge System.
3. The Storm Filter system shall be sized as described in the Bay SaverTM' Cartridge
System '"'Technical and Desiqn Manual, and the designer shall select the result
yielding the larger number of cartridges.
4. Pre-settling shall be provided per Section 6.5.1 of the 2009 KCSWDM, General
Requirements for Media Fi(tration Facilities.
5. The Bay Saver�"" Cartridge System must be instalfed in an area that is accessible
to maintenance equipment. The maintenance of a Bay SaverT" Cartridge System
requires a vacuum truck as well as the removal and replacement of the filter
cartridges. The manhole covers, and/or access openings of the Say SaverT""
Cartridge System must be placed in locations that can be easily reached by such
a vehicle.
6. Facility shall be constructed in accordance with the plan (attached}with the 36-
inch and 30-inch manhole access opening with ladders in both access openings.
10. Installation of a eay Saver'" Cartridge System shall follow the manufacturer's
recommended procedures.
11.The Bay Saver'"" Cartridge System shall be inspected every six(6) months during
the two-year maintenance and defect bond period following completion of
construction and plat recording. The owner is responsible for the maintenance
of the Bay SaverT" Cartridge System during the two-year maintenance and defect
bond period.
12. All Bay SaverTM' Cartridge System cartridges will need to be repfaced before the
end of the two-year maintenance and defect period, prior to release of the of
the two-year maintenance and defect bond. The City will maintain the facility
after the two-year maintenance and defed bond is released at the end of the
two-year maintenance and defect bond period.
13. The Bay Saver"" Cartridge System shall be maintained in accordance with
manufacturer recammendations.
H:\File Sys\SWP-Surface Water Projetts\SWP-27-Surface Water Projects{CIP}\273129 Rentan 5tormwater
Manual\ADJUSTMENTS\2013\2013-4-Pipers Bluff-Bay Fi(ter.doc\HCBtp
Ms.11lian ,
Page3of3
September 25,2013
14.The Bay Saver'"" Cartridge System shall be installed in accordance with the
approved construction plans at the same location of the previously approved
Contech Cartridge System was proposed to be installed.
15.The approval of this adjustment to use the Bay Saver'"" Cartridge System for the
Pipers Bluff Plat does not authorize the use of the Bay Saver'" Cartridge System
on future projects without prior approval from the City of Renton.
16. Please note that the approval of this adjustment does not relieve the applicant
from other city, state, or federa[ requirements.
If you have any questions about this adjustment, please contact Hebe C. Bernardo or
me.
Attachments
tt: Lys Hornsby,P.E.,Utiiity Systems Director
Neil Watts,Development Services Director
Richard Marshall,Surface Water and Water Maintenance Manager
file
H:\Flle Sys\SWP-Surface Water Projects\SWP-27-SurFace Water Projects(CIP)\27-3129 Renton Stormwater
ManuaI�ADJUSTMENTS\2013\2013-4-Pipers Bluff-Bay Filter.doc\HCBtp
BAYSAVER
� TECHNOLOGIES°
Piper's Bluff
City of Renton, WA
Stormwater Management
BayFilter System
BayFilter
Sizing Report
Prepared by: BaySaver Technologies, LLC
Paola Rodriguez (301) 829-6470
prodriguez@BaySaver.com
1030 Deer Hollow Drive
Mt. Airy, Maryland 21771
r
Table of Contents
1.) Overall System Design
2.) BayFilter Design Computations
3.) Bayfilter System Details
,
i.) Overall System Design:
This is a proposed design to the SWM Plan for the Piper's Bluff project. The current
design employs an underground Contech Stormfilter system for treatment of the WQV
flow rate of 0.101 cfs generated by the site. This system utilizes a 96" diameter manhole
with 13 stormfitter cartridges.
We are proposing a treatment solution as an alternate to the aforementioned system with
a Bayfilter Filtration system. The BayFilter system wil) consist of an 84" diameter
manhole with 3 Ba�lter cartridges to treat the required WQV flow rate. Each BFC has a
design capacity of 15 gpm, as approved by Washington DOE.
2.)BayFilter Design Computations
Flow Based Sizin Calculator Ba Filter
Re uired Treatment Flow cfs 0.101 �
Flow Rate Per Cartrid e m 15 I
Number of Cartrid es Re uired 3 ��
Treatment Flow Provided cfs 0.10 '
Precast Structure Re uired 84"-MH I�I
Flow Based Sizing Calculator 1
Computed Treatment Flow(cis) 0.101 36' FRAME ao' FRAME
Flow Rate Per Cartridge(gpm) 15 � a2s oo a2s oo ER
Number of Cartridges Required 3
Number of Dreindown Modules Required 3 ' ,
Treatment Flow Provided 0.10 N��
Vault Required 84-rnh '
.�
IAYFILTER STORMVATER F0.TRATIOI STSTEM PROTECTED!Y US.PATENT M 6,869,328 e � -
S� e
�..
'1. o 0
18' OUTLET '`� � �
� o
18' OVER��OW
STANDPIPE
30' FRAME � �
6 COVER
e e
;� -----84•----- ;�.
�84` �':
o �
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t8' OVERFLOW
'� STANDPIPE
36' FRAME ��� � �
6 COVER
� ` ` � � 18' INLET
�, O O 410.00'
18' OUTLET
407.70'
- =.:•'...�. ': :�;j ::;.
'.� �� ' .�::: ,i:�.
18' INLET
PLAN VIEW SECTION VIEW
REv DESCRIPTION a►rE ra�s: �I3AYSAVER
ILGINOLOGIES
o� Pe� c��y oi Ranton, odd.a seoa,d y/»��3 h00-829-7283 '
monhole acceea. `r ,v'AWtlAVSAVERCOM gAYFILTER MANHOLE
DESIGNED: TEP DATE: 9/17/13 MODEL MHF-84-3
DRAVrh PR SCALE: N.T.S,
CHECKED: EKH DWG Na HF-103
BayFilter Installation Instructions
P[PER'S BLUFF—RENTON, WA ',
MANIFOLD AND STAND P�E PICTURE I�
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SEE ATTACHED DETAIL DRAWING FOR ASSEMBLY
HAYFILTER STORMVATER FILTRRTION SYSTEM PROTECTED HY U.S.P�TENT � 6,B69,S2B
18" �UTLET 1
18" �VERFL❑W
STANDPIPE � BAYFILTER MANIFOLD ASSEMBLY �
, e� . 1. One (1 ) 18" overflow standpipe.
� � � ��.:: , . 3 2. One (1) 4" fernco. ' �
3. One (1) 4" pvc pipe 6" long. '
� 4 4. One (1) 4" pvc cross fitting.
. 5. Two (2) 4" pvc pipe 15" long.
. �� 6. One (1) 4" pvc pipe 20" long.
7 .~' 7 7. Three (3) 4" Filter Tee fitting.
8. Three (3) Flow disks 1.14" orifice.
:. 9. Three (3) 4" insert caps.
1 Q 10. Three (3) Draindown Modules.
g � 11. Three (3) Bayfilter BFC cartridges.
.
9
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9
:�
' �� , � 10
.
a. .
3 "
�84" 11
7 36"
18" INLET 18" OVERFLOW
STANDPIPE
R�v o�scRiwr�on� o�� P NOTES: � 13AYSAVER
rr•cHNoi.ocirs ,
f. BFC carM�Edges a�.d �r R00-829-7283 PIPER S BLUFF
wwwpAYSAVLN.COM BAYFILTER MANHOLE
DD1!'s shti�ped j'ram ADS pEc.�GNED: TEP ��n: 9/ll/13 MODEL MHF-84-3
warehouse. DRavrx PR scn�: N,r.s. MANIFOLD DETAIL
CHECKED: EKH DVG ND� HP--103
BayFilter Installation Instructions
Installation of a BayFilterTM System
1. Contact utility locator to mark any nearby underground utilities and make sure it is safe
to excavate.
2. Reference the site plan and stake out the location of the BayFilterTM manhole/vault.
3. Excavate the hole,providing any sheeting and shoring necessary to comply with all
federal,state and local safety regulations.
4. Level the subgrade to the proper elevation. Verify the elevation against the
manhole/vault dimensions,the invert elevations, and the site plans. Adjust the base
ag8regate, if necessary.
5. Have the soil bearing capacity verified by a licensed engineer for the required load
bearing capacity. On solid subgrade,set the first section of the BayFilterT^t
manhole/vault.
6. Check the level and elevatian of the first section to ensure it is correct before adding any
riser sections.
?. If additional section(s}are required,add a watertight seal to the first section of the
BayFilterTM manhole/vault. Set additional section(s)of the manhole/vault,adding a
watertight seal to each joint.
8. Install the trolley system(if applicable). See separate instruction sheet.
9. Install the PVC outlet manifold. Glue all PVC joints with the exception of the BayFilter
cartridge coupling. See separate insuuction sheet.
10. Install the PVC outlet pipe in BayFilterTM manhole/vault.
11. Install the inlet pipe to the BayFiiterT"'manhole/vault.
12. After the site has stabilized,remove any accumulated sediment or debris from the vault
and install the Ba�lter Drain Down Modules(DDM}with red mark aligned to the top of
the manifold system.
13. Install the flo�v disks and the BayFilterT""car[ridges.
TOOL LIST:
� • PVC GLUE AND PRIMER
• CRANE/LIFTING MECHANISM TO LOWER THE CARTRIDGES IN THE VAULT(EACH
CARTRIDGE WEIGHS 350 LB)
• SCREWDRIVER OR NUT DRIVER FOR FERNCO COUPLERS
• SOFT BLOW HAM1v�R
• SAW(IN CASE PVC SCH 40 PIPING LENGTH NEEDS TO BE ADNSTED).
GRANITE PRECAST Up To Center/Up Calculatlo
Job: 7101 Customer. BAYSAVER 7ECHNOLOGIES,INC. 5trvcture Code:84' Type: Storm ' I
Job Name: PIPER'S BLUFF Statlon:REVISED Descriphion: 84"General Storm R Unit
Structure Product Detail Inside Area View
kem_ Product a�Product Deser�gtion Yards Waight �{m to Invert 17.30' Preqst Height 17.25' Wall 8.00"
CR-06X3 1 8'X 30'GRADE RING 0.00 300 Less CasU�g 18.97' Floor 7.00" Sum 0
CR-04X3 1 4'X 30'GRADE RING 0.00 220 p I
C.CUST 1 4'x30•CI RING AND CI COVER o.00 o Invert to Floor 0. Plus RoOr 17.83'
LOCKWG'DRANI" AdJustrnent(Brick/Mort) 0.14
C.CUST 1 45c38'CI RING AND CI COVER 0.00 0 •
LOCKWG'DRAIN" �,�, ._.._.___._.._.._.._.._.._, g�
Too 2 CR-04X3 1 4"X 38'ORADE RING 0.00 82 T�q 1.42 84"CUST�OM FLA�T�TOP/
Too 4 084TS2R 1 84"CUSTOM FLATTOP/TW O ROUND 2.18 8.700
HOLES �
Tou 3 CR-08X3 1 6"X 38"GRADE RING 0.00 400
ttem 2 084XQ7R 1 84'X T RISER 4.20 18.800 ��2 T.00 84"X T RISER
kem 1 OB4X08R 1 84"X B'RISER W/HOLE 4.84 18.580
Base 0849S 1 94"BASE SLAB x O.SB' 1.88 7.340
Acces 084RG 3 84"GASKET 0.00 0
SVucture Totals 12.90 52,602
' Hem 1. 2 8.00 84'X 8'PoSER W/HOLE
�
1
Elevations 3so 2m �eo � � so 0�,0°
Ekv Angb Plpe Hde Mole' Hole' Up' Ilem
Im _1.�_ --- TYVe Nei9M Width .
I(Il �? L� e Pv ___� _S�Q� _ 1�.1 _ll�r�t I
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(5)____: _ _ 0_ _. ______. _ o_ . _ 0 ,._ o NEEDS CUSTOM 2 HOLE TOP SLNB.SEE AITACHED.
le)_ .: �_ o__ ._ _._..�_._. --, o-- 9. . 9_...
�_ _.` � o 0
(eL__. ..- -�---- '- -- o 0 0
DexAptlon: 84"X 8'RISER W/HOLE
Product ID: 064XOCRWC
Nem: Item t Slep Location: D011
(1�ORED M I
, UP:14.1" / �JO }k�l.{�
135 I
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APPROVQL OF DRAWING
THIS DRqWING�9 FURWARDHD FOR YOURAPPROVAL. '
�G'��^��, PLEASECHECNTHEDRAWINGAMDRETURNITAPPROVED 'i
�� OR WiTH CWINGES NOTED,IFANY.
S�pb ARODUGTlpN W►LL NOT START UNTlL
APPROVEp DRAW/NCSARE RETURNED.
(2�ORED COMPANY
Up:41.7" !Mg
315
�
Meets or Exceeds WSDOT Std Plan B-15.60-01
iB 4" Typ e 3 Ma nhole Manhdes Canstructed in Aaordance Wlth ASfM C-478
Rubber Gasket Canforms to ASTM C�43
Polyprapylene MH Steps Conform to PSTM C-478
�1�in
, , �4��I.o. CUSTOM ER: BAYSAVER
i� � PROJECT: PIPERS BLUFF
. .
•- ��� �� .� DATE:9/16/13
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a� ��
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Grade Rinp Q��LL�Z
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o i a��S�Q a � DETAIL E
� �' I �F��4 Q � � k SCALE 1 / 24
.�,,,� I r to 8' ------�_� c�
I I �� WEI6HT5:
J.,.a TOP SLAB: 12"- 8,700 Ibs
� I RISER: 1'- 2,400 Ibs
; I� 2'• 4,800 Ibs
�—————��T 3'- 7,200 Ibs I
4'- 9,600 Ibs
———— 5'- 12,000 Ibs
�`` ' � E 6'- 14,400 Ibs
7'- 16,800 Ibs
� o I 8'- 19,200 Ibs
� I BASE SLAB: lY- 7,540 Ibs
COIVCRETE:
�,,, f Fr-4,000 psl�28 Days
1,��, REINFORCING STEEL:
.d... � ��� Wekled Wire Fabrk:ASTM M97
� I Rebar.ASTM A615 Grade 60
Top Slab:0.75 Sq In,/R.e,w.min.
Riser:6.215q In./R e.w.min.
8� I Base 9ab;0.34 Sq In./tt e.w.min.
PIPE PENETRATIONS:
�.� —�L�� 1'Base Slab Ma�dmum Hole Size:72"
Minlm�an Dis�nce Hole to Hole:12°
Hdes Cored to Plan Spedf�tlons
8" 7' 8° Kor-N-Seal ConneGlons AvaNabie
8���� SITE PENEfRATIONS;
Cor#ract�to Estadsh Level Grade
ELEVATION VIEW Prlor to Setting ease Plece at a
Talerar►ce of 1/4"Oo 3/8'
�2013 Granite Precasting&Concrete,lnc,
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. Operations and Maintenance �
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BAYSAVER TECHNOLOGIES� INC.
- [�LET W ATE
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Stormwatex runoff enters the manhole or concrete sttvcture via an inlet pipe
and begins to 6ll the structure. An energy dissipator at the vault inlet slows the influent '
water and allows coaise sediments to settle tvithin the structure. ��Ihen the water '
surface elevation in the vault/manhole reaches operating level,water flows thxough the ''
BFC driven by a hydrostatic head. Within the BFC, the water flows through a
proprietary filter media and drains via a vertical pipe. The vertical drain is connected to
the underdrain system which conveys 6ltered water to the outfall.
During a rypical storm eeent,the BayFilterT`�system has Four cvcles:
1. Vault fill and aiz release;
2 Uniform bed load hydrodynainic 6ltrarion;
3. Uniform bed load siphon filtraaon;and
3
BAYFILTERT"s SPECIFICATIONS
PART 1.00 GENERAL
1.1 DESCRIPTION
A. The BayFilterTM system's internal components manufacturer selected by
the Contractor and approved by the Engineer, shall furnish all labor, I
materials, equipment and incidentats required to manufacture the
BayFilter system components(s) specified herein in accordance with the
attached drawing(s)and these specifications.
B. Concrete structures and any appurtenances that form an integrai part of the
BayFilterTM system shall be described in Part 2.00 of these specifications.
1.2 OUALITY CONTROL INSPECTION
A. The quality of materials, the process of manufacture, and the finished
sections shall be subject to inspection by the Engineer. Such inspection
may be made at the place of manufacture, or on the worksite after
delivery, or at both places, and shall be subject to rejection at any time if
material conditions fail to meet any of the specification requirements. If a
BayFilter system component(s) is rejected after delivery to the site, it shall
be mazked for identification and removed from the site. Any BayFilter
system component{s) which have been damaged beyond repair during
delivery will be rejected.
1.3 SUBMITTALS
A. Plan, elevation, and profile dimensional drawings shall be submitted to the
Engineer for review and approval. The Contractor shall be provided with
the approved plan, elevation, and profile dimensional drawings.
PART 2.00 PRODUCTS
2.1 INTERNAL COMPONENTS
All components including concrete structure(s), PVC manifold piping and filter
cartridges, shall be provided by BaySaver Technologies Inc., 1030 Deer Hollow
Drive,Mount Airy, MD(800.229.7283).
A. PVC Manifold Piping: All internal PVC pipe and fittings shall meet
ASTM D1785. Manifold piping shall be provided to the contractor
partially pre-cut and pre assembled.
BaySaver Technologies,Inc. 1 9/7/12-Yersion 1.0
B. Filter Cartridges: Extemal shell of the filter cartridges shall be
substantially conshucted of polyethylene or equivalent material acceptable
to the manufacturer. Filtration media shall be arranged in a layered fashion
to maximize available filtration area. An orifice plate shall be supplied
with each cartridge to restrict the flow rate.
a. Maximum flow rate for the BFC cartridge shall be 30 gpm at 0.7 gpm
per sq-ft. of filter media.
b. Maximum flow rate for the EMC cartridge shall be 45 gpm at 0.5 gpm
per sq-ft. of filter media.
C. Filter Media: Filter media shall be by BaySaver Technologies Inc. or
approved alternate.
a. Filter media for the BFC cartridge sball consist of 43 square feet of the
following mix: sand media shall have an effective particle size of not
more than 0.50 mm; it shall have an angular grain shape, be 99%
silica, and not leach nutrients. The media shall also include a blend of
Perlite and Activated Alumina.
b. Filter media for the EMC cartridge shall consist of 90 square feet of
the following mix: a blend of Zeolite, Perlite and Activated Alumina.
22 PERFORMANCE
A. The stormwater filter system shall be capable of treating 100% of the
required treahnent flow at full sediment load conditions.
B. The stormwater filter system's cartridges shall have no moving parts.
C. The stormwater treatment unit shall be designed to remove at least 80% of
the suspended solids load. Said removal shall be based on full-scale testing
using SIL-CO-SIL 106 media gradation with a dso of 23 microns
(manufactured by US Silica) or equivalent. Said full scale testing shall
have included sediment capture based on actual total mass collected by the
stormwater filtration system.
D. The stormwater filtration system shall reduce incoming turbidity
(measured as NTUs) by 50% or more and shall not have any components
that leach nitrates or phosphates.
E. The stormwater filtration cartridge shall be equipped with a hydrodynamic
backwash mechanism to extend the filter's life and optimize its
performance. Inlet flow shall be upflow.
F. The stormwater filtration system shall be designed to remove a minimum
of 50%of the incoming Total Phosphorus(TP) load.
G. The stormwater filtration system's cartridges shall have the following
minimum flow and sediment load capacities:
BaySaver Technologies,lnc. 2 9/7/12-Versian 1.0
I�
Design Flow per Treated Sediment Load
cartridge-(gpm) (lbs)
Nominat
45 EMC 350
30 BFC 150
23 BFC 200
20 BFC 250
15 BFC 300
2.3 PRECAST CONCRETE VAULT COMPONENTS
A. Concrete structures shall be designed for H-20 traffic loading and
applicable soil loads or as otherwise determined by a Licensed Professional
Engineer. The materials and structural design of the devices shall be per
ASTM C857 and ASTM C858.
B. The minimum compressive strength of the concrete shall be 4000 psi.
C. Cement shall conform to the requirements for Portland cement of
Specification C150.
D. Aggregates shail conform to Specification C33, except that the requirement
for gradation shall not apply.
E. Reinforcement shall consist of wire confornung to Specification A82 or
Specification A496, of wire fabric confornung to Specification A185 or
Specification A497, or of bars of Grade 40 steel conforming to
Specification Ab15/A615M.
F. The access cover shall be designed for HS20-44 traffic loading and shall
provide a minimum 30 inch clear opening.
G. All joints shall be waterproof with wrapped gaskets or sealed with a mastic
treatment.
H. Any grout used within the system shall meet the ASTM C 1107 "Standard
Specification for Packaged Dry, Hydraulic-Cement Grout (Non-Shrink)".
Grades A, B and C at a pourable and plastic consistency at 70°F. CRD C
621 "Corps of Engineers Specification For Non-Shrink Grout."
2.4 CONTRACTOR PROVIDED COMPONENTS
Specifications for all contractor-provided components are minimum requirements.
If a higher standard is shown on the plans or described in another section of the '
technical specifications, then the higher standard shall govern ,
BaySaverTechnologies,I�c. 3 9/7i12-�ersion 1.0 I�il
A. Sub-Base: Sub-base shall be six-inch minimum of 3/-inch minus rock,
95% compaction. Compact undisturbed sub-grade materials to 95% of
maximum density at +/-2% of optimum moisture content. Unsuitable
material below sub-grade shall be replaced to engineer's approval.
B. The minimum compressive strength of the concrete for cast in place
structures shall be 4Q40 psi.
C. Silicone Sealant: Shall be pure RTV silicone conforming to Federal
Specification Number TT 5001543A or TT 500230C or Engineer
approved.
D. Grout: Shall be non-shrink grout meeting the requirements of Corps of
Engineers CR.D-0588. Specimens molded,cured and tested in accordance
with ASTM C-109 shall have minimum compressive strength of 6,200 psi.
Grout shall not exhibit visible bleeding.
E. Backfill: Backfill shall be %-inch minus rock at 95%compaction.
PART 3.00 EXECUTION
3.1 PRECAST CONCRETE VAULT
A. Vault top finish grade shall be even with surrounding finish grade surface
unless otherwise noted on plans.
B. Contractor shall grout all inlet and oudet pipes flush with vault interior
wall.
C. Sanded PVC fittings shall be used on all PVC inlet and outlet pipes.
3.2 ANTI-FLOTATION BALLAST(Where Required)
A. Ballast shall be to the dimensions specified by the engineer and noted on
the data block. Ballast shall run the entire length of the long side of the
vault on both sides. Ballast shall nat encase the inlet and/or outlet piping.
Provide 12" clearance from outside diameter of pipe.
3.3 CLEAN UP
A. Remove all excess materials, rocks, roots, or foreign debris, leaving the
site in a clean, complete condition approved by the engineer. All filter
components shall be free of any foreign materials including concrete.
BaySaver Techriologies, Inc. 4 9/7/12-Version 1.0
3.4 FILTER CARTRIDGES
A. Filter cartridges shall not be installed until the project site is clean and
stabilized or if the inlet and outlet pipes are temporarily blocked off. The
project site includes any surface that contributes stormwater runoff to the
BayFilter system. All impermeable surfaces shall be clean and free of dirt
and debris. All catch basins, manholes and pipes shall be free of dirt and
sediments.
3.5 INSTALLATION NOTES
A. Contractor to strictiy follow the approved design and construction
specifications. Any substitutions are to be pre-approved by the inspector
and design engineer in writing prior to placement of materials.
B. The stormwater filtration system(s) may not be activated until all
contributing drainage areas to each facility are stabilized. Construction of
the facility shall not proceed without prior authorization of the inspector.
C. No "rock dust" can be used for sand.
D. Contact "Miss Utility" at 1-800-257-7777 at least 48 hours prior to the
start of construction.
PART 4.00 EXECUTION
4.1 INSTALLATION
A. Installation of the BayFilter System(s) shall be performed per
manufacturer's Installation Instructions. Such instructions can be obtained
by calling BaySaver Technologies, Inc. at 1.800.229.7283 or by login to
www.BavSaver.com.
I
BaySaver Technologies,Inc. 5 9/7/11-Version 1.0
i �V�
NlSE146'79 � � �
OEP � BiY; Mi L�
ECOLOGY
December 2012
GENERAL USE LEVEL DESIGNATON FOR BASIC TREATMENT
CONDITIONAL USE LEVEL DESIGNATION FOR ENHANCED,AND
PHOSPHORUS TREATMENT
For
BaySaver Technologies, Inc.BayFilterTM
Ecologv's Decision:
1. Based on BaySaver Technologies' application subtnissions,Ecology hereby issues a
GeneraE Use Level Designation (GULD)for the BayFilterTM.
• As a stormwater treahnent device for Basic treatment(TSS) removal.
• The Basic Treatment GLTLD is for both the BayFilter Cartridge(BFC) and
Enhanced Media Cartridge(EMC)and limited to the following maximum flow
rates:
a. BFC Cartridge maximum flow rate of 0.7 gpm/sf
0 30 gpm(0.067 cfs) per cartridge(43 sf filter area)
0 26-inches in diameter and approximately 28.75-inches tall.
b. EMC Cartridge magimum flow rate of 0.5 gpm/sf __`_
0 45 gpm(0.1 cfs) per cartridge(30-inch diameter)(�0 sf filter area)
0 75 gpm(0.17 cfs)per cartridge(39-inch diameter) (150 sf filter area)
c. Media combinations for the BayFilter cartridges are limited to Silica Sand,
Perlite, Zeolite,and Activated Alumina. (All filters are limited to 19-inch vertical
component to the spiral filter layers)
2. Based on BaySaver Technologies' application submissions,Ecology hereby issues a
conditional use level designation (CULD)for the BayFilterTM cartridges.
• As a stormwater treatment device for Enhanced treatment(dissolved Cu and
dissolved Zn removal)and Phosphorus treatment.
• Sized at a design rates no greater than those listed above(GiTLD (Basic) Flow
rates).
3. Ecology approves use of BayFilterTM Cartridges using the Silica Sand,Perlite, Zeolite,
and Activated Alumina for treatmeot at the above flow rates per cartridge. Designers
shall calculate the water quality design flow rates using the following procedures:
• Western Wsshington: For treatment installed upstream of detention or retention,
the water qua(ity design flow rate is the peak 15-minute flow rate as calculated using
the latest version of the Western Washington Hydrology Model or other Ecology-
approved coatinuous runoff model.
• Eastern Washington: For treatment installed upstream of detention or retention,
the water quality design flow rate is the peak 15-minute flow rate as calculated using
one of the three methods described in Chapter 2.2.5 of the Stormwater Management
Manual for Eastern Washington{SWMIVIER� or local manual.
• Entire State: For treatment installed downstream of detention,the water quality
� design flow rate is the fu112-year release rate of the detention facility.
4. The CITLDs expire on December 1,2013 unless extended by Ecology, and are subject to
the conditions specified below.
5. The GULD has no expiration date,but it may be amended or revoked by Ecotogy, and '
is subject to the conditions specified betow.
Ecologv's Condi�ions of Use:
BayFilterTM units shall comply with these conditions:
1. Design, assemble,install,operate,and maintain BayFilterTM units in accordance with
BaySaver Technologies' applicable manuals and documents and the Ecology Decision.
2. Maintenance: The required maintenance interval for stormwater treatment devices is
often dependent upon the degree of pollutant loading fram a particular drainage basin.
Therefore,Ecology does not endorse or recommend a"one size fits all" maintenance
cycle for a particular modeUsize of manufactured filter treatment device.
• Typically,BaySaver designs BayFilter Cartridge systems for a target filter media
replacement interval of 12 months.
• Testing results provided to Ecolog,y for the Basic GULD approval indicate that the
treatment system required maintenance after four months of operation. Ecology
used the effluent flow rate decreasing to below the design flow rate as the indicator
of the need for maintenance. Ecology determined this from the continuous flow
monitoring data. This interval does not necessarily determine the maintenance
frequency for all Bay�lter systems.
• Owners/o erators must ins ect Ba Filter s stems for a minimum of twelve months II
P P Y Y
from the start of post-construction operation to determine site-specific maintenance
schedules and requirements. Owners/operators must conduct inspections monthly
during the wet season,aud every other month duriag the dry season. (According to
the S�V1I�IlVIWW,the wet season in western Washington is October 1 to Apri130.
According to SWMMEW,the wet season in eastern Washington is October 1 to
June 30.)After the first year of operation,owners/operators must conduct
inspections based on the fmdings during the first year of inspections.
� Conduct inspections by qualified personnel,follow manufacturer's guidelines, and
must use methods capable of determining either a decrease in treated effluent
flowrate andlor a decrease in pollutant removal ability.
3. When inspections are performed,the following findings typically serve as maintenance
triggers:
• Accumulated vault sediment depths exceed an average of 2 inches, or
� Accumulated sediment depths oo the tops of the cartridges exceed an average of 0.5
inches,or
� Standing water remains in t6e vault between rain events.
• Bypass during starms smaller than the design storm.
• Note: If excessive floatables (trash and debris} are present,perform minor
maintenance consisting of gross solids removal,not cartridge replacement
4. The filter fabric used in the BayFilter is highly oleophilic(oil absorptive); therefore,
hydrocarbon accumulation on the filter may cause premature failure. Oil control
BMP's should be installed upstream of BayFilter installations if warranted, and/or the
BaySaver should be inspected after any known oil spill or release.
5. BaySaver Technologies Inc. commits to submitting a QAPP for Ecology approval by
June 1,2012 that meets the TAPE requirements for attaining a GITLD for enhanced
and phosphorus treatment. The monitoring site(s)c6osen should be reflective of the
product's treatment intent. Baysaver shall monitor sites prior to installation of the
canister to ensure concentrations of the monitored constituents are within TAPE
guidelines.
6. BaySaver Technologies Inc. shall complete all required testing and submit a TER for
enhanced and phosphorus treatment for Ecology review by Apri130,2013.
7. BaySaver Tec6nologies Inc. may request Ecology to grant deadline or expiration date
eztensions, upon showing cause for such egtensions.
S. Discharges from the BayFilterTM units shall not cause or contribute to water quality
standards violations in receiving waters.
Applicant: BaySaver Tech.nologies Inc.
Applicant's Address: 1030 Deer Hollow Drive
Mount Airy,MD,21771
Application Documents:
• Technical Evalteation Report BayFilter System, Grandview Place Apartments,Vancouver,
Washington and Appendices A through O (May I8, 2011)
� Washington State Department of Ecology Technolog�Assessment Protocal—
Envirorrmental BayFilterTMCondttional Use Desigrration Application(March 2007)
� BaySaver Technologies,Inc.BayFilterTM System Washington State Technical and Design
Mamral, Version 1.1 (December 2006)
• Eff ciency Assessment ojBaySeparator and Bay frlter Systems in the Richard Montgomery
High School January 6.2009.
• Eval:ration of MASWRC Sample Collection, Sample Analysis, and Data Analysis,
December 27,2008
• Letter from Mid-Atlantic Stormwater Research Center to BaySaver Technologies, In.
dated October 22,2009.
• Letter from Mid-Atlantic Stormwater Research Center to BaySaver Technologies, In.
dated November 5,2009.
� Maryland Department of the Environment letter to BaySaver Technologies dated Jan. 13,
2008 regarding approval of BayFilter as a standalone BMP for Stormwater treatment.
• NJCAT letter to BaySaver Technologies dated June 18, 2009 regarding Interim �
Certification.
Applicant's Use Level Request:
• General use level designation as a basic, enhanced, and phosphorus treatment device in
accordance with Ecology's Stormwater Management Manua( for Western Washington.
Applicant's Performance Claims:
• Removes and retains 80%of TSS based on laboratory testing using Sil-Co-Sil 106 as a
laboratory stimulant.
• Removes 42%of dissolved Copper and 38%of dissolved Zinc.
• Expected to remove 50% of the influent phosphorus load.
Ecology's Recommendations:
Ecology finds that:
• Ecology should provide BaySaver Technologies, Inc. with the opportunity to demonstrate,
through additional laboratory and field-testing,whether the BayFilterTM system(as a
single treatrnent facility) can attain Ecology's Enhanced Treatment and Phosphorus
removal g�als.
Findings of Fact:
• Based on field testing in Vancouver, WA, at a flow rate less than or equal to 30 gpm per
canister, the BayFilterTM system demonstrated a total suspended solids removal efficiency
of greater than 80% for influent concentrations between 100 and 200 mg/l and an effluent
concentration<20 mg/1 for influent concentration< 100 mg/1.
• Based on laboratory testing,at a flowrate of 30 GPM per filter,the BayFilterT"' system
demonstrated a total suspended solids removal efficiency of 8I.5°/a using Sil-Co-Sil 106
with an average influent concentration of 268 mg/L and zero initial sediment loading.
• Based on laboratory testing, at a flowrate of 30 GPM per filter, the BayFilterTM system
demonstrated a dissolved phosphorus removal efficiency of 55%using data from the
Richard Montgomery High School field-testing. The average influent concentration was
0.31 mg/L phosphorus and zero initial sediment loading.
• Based on data from field-testing at Richard Montgomery High School in Rockville, MD
the BayFilter system demonstrated a Cu removal efficiency of 51% and 41% for total and
dissolved Cu respectively. Average influent concentrations are 41.6 µg/1 total and 17.5
�g/1 dissolved.
• Based on data from field-testing at Richard Montgomery High School in Rockville,MD
the BayFilter system demonstrated a Zn removal e�ciency of 45% and 38% for total and
dissolved Cu, respectively. Average influent concentrations are 354 µg/1 total and 251
µg/1 dissolved,respectively.
Other BayFilterTM Related Issues to be Addressed By the Company:
1. The Washington State field test results submitted in the TER do not yet show whether the
BayFilterTM system can reliably attain 30%removal of dissolved Cu, 60%removal of
dissolved Zn, or 50% removal of Total Phosphorus found on local highways,parking lots,
and other high-use areas at the design operating rate.
2. BaySaver Technologies, Inc. should test a variety of operating rates to establish conservative
design flow rates.
3. The system should continue to be monitored to measure bypass and to calculate if the system
treats 9I%of the volume of the total annual runoff volume.
4. The system should be tested under normal operating conditions, such that the settling basin is
partially filled with pollutants. Results obtained for"clean"systems may not be
representative of typical performance.
5. Conduct field-testing at sites that are indicative of the treatment goals.
b. BaySaver should continue monitoring the system for a longer period to help establish a
maintenance period and to obtain data from additional qualified storms. Conduct testing to
obtain information about maintenance requirements in order to come up with a maintenance
cycle.
7. Conduct loading tests on the filter to determine maximum treatment life of the system.
8. Conduct testing to determine if oils and grease affect the treatment ability of the fitter. This
should include a determination of how oil and grease may affect the ion-exchange capacity of
the system if claims are to be made for phosphorus removal.
9. BaySaver should develop easy-to-implement methods of determining when a BayFilter system
requires maintenance(cleaning and filter replacement).
10. BaySaver must update their O&M documents to include information and instructions on the
"24-hour draw-down" method to determine if cartridges need replacing.
Technology Description: Download at www.BaySaver,com
Contact Informallon:
Applicant: Tom Pank
BaySaver Technologies, Inc.
1030 Deer Hollow Drive
Mount Airy, MD, 21771
(301) 829-6470
t��ci�baysaver.com
Applicant website: www.BavSaver.com
Ecology web link: httn:liwww.ecv.wa.Qov/programs/wq,�stormwater/newtech/index.html
Ecology: Douglas C. Howie, P.E.
Department of Ecology
Water Quality Program
(360)407-6444
douglas.howie'a,ecv.wa.gov
Revision Histor
Date Revision
A ri12008 Ori inal use-level-desi ation document
February 2010 Revision
Au st 2011 GULD awarded for Basic Treatment
Apri12012 Maintenance r uirements u dated.
Au st 2012 Revised desi storm criteria
December 2012 Revised contact information and document formattin
BAYSAVER TECMNOLOGIES, INC. �
Insta�atic�n o� a 11�anhaie Bay�i����
1. Contact utility locamr to mazk anjT nearb}' underground udlioes and
mal:e sure it is safe to excavate.
2. Reference the site plan and stake out the location of the BayFilterTM
manhole.
3. Excavate the hole, pro�riding any sheeting and shoring necessari� to
comply with all federal,state and local safety regutaaons.
4. Level the subgrade to the proper elevation. Verif�r the ele��ation
against the manhole dimensions, the invert ele��ations, and the site
plans. Adjust the base aggregate,if necessary.
5. Have the soil bearing capacity��erified bj� a licensed engineer for the
xequired load bearing capacity. On solid subgrade, set the base of the
BayFilterTM manhole.
6. Check the lei�el and elevadon of the base unit to ensure it is conect
before adding any riser sections.
7. Add watertight seal (either masric rope or rubber gasket) to the base
unit of the BaS�FilterTM manhole. Set riser section(s}on the base unit
8. Install the PVC watertight oudet manifold �vithin the BayFilterrn1
manhole.
9. Install the inlet pipe to the BayFiiterTM manhole.
10. Install the energy dissipatorJlevel spreader at the system inlet locarion.
11. After the site is scabilized,remove anj�accumulated sediment or debris
fcom the manhole and install the BayFilterTM carnidges.
2s
B A Y S A V E R T E C N N O L O G 1 E S, 1 N C.
Installaticm af Precast Vau�t BayF�terTM
1. Contact utility locator to mark any nearbj• underground utilities and
ma1:e sure it is safe to excavate.
2. Reference the site plan and stake out the location of the BayFilterT�`1
vault.
3. Exca��ate the hole, providing any sheeting and shoring necessaz}� to
comply with all federal,state and local safety reguladons.
4. Level the subgrade m the proper elevation. Verify the elevadon
against the manhole dimensions, the inverc elevations, and the site
plans. Adjust the base aggregate,if necessary.
5. Have the soil bearing capadty��erified bp a licensed engineer for the
required load bearing capacity. On solid subgrade, set the fust secdon
of the BayFilterTM precast vault
6. Check the level and elevation of the first section to ensure it is correct '
before adding any riser secuons. ',
7. If addiaonal section(s) are required, add a watertight seal to the first
section of the Ba}'FilterTM vault. Set additional section(s) of the vault, ',
adding a watertight seal to each joint.
8. Insta2l the PVC oudet manifold and oudet chamber s}'stem.
9. Install the PVC oudet pipe in BayFilterTM vault.
10. Install the inlet i e to the Ba FilterTM vault.
pP Y
11. Install the energS�dissipator/level spreader at the inlet pipe.
12. AEter the site is stabilized,remove an}'accumulated sediment or debris
from the vault and inst�ll the BayFilterTM camidges.
�
� I!
BayFilter '
M ai n t en an ce Gu i d e
Phone (301)829-6470 Toll Free 800-229-7283 Fax (301} 829-3747
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m2009 BaySaver Technologies, Inc.
www.BaySavet.com
1302 R3sing Ridge Rd. Unit 1 • Mount Airy, Niaryland 21771
(301) 829-G470 Toll Free 800-229-7283 Fax (301)829-3747
` �
BayFilterTM Maintenance and Operations Overview
The BayFilteiTM system tequices periodic 111Sp�lOf1�f11811tEf17102t0 OOf1tiCllJ@OpEf�lll��thBdPS�'1
effidency.
WFt�718 BayFllterT"� system is first installed,it is recommended that it be inspected every six {6) months.
During the sy5tems first mantenanoe cyd� inspedion is required � edery sx months and �ter m�or
storm eventsto determineratesof sediment and pollution aoamufation.When thefilter system achibits
flows beJow desic,�n levds, the system shauld be maintaned. The mo�t effiaent wa�r of d�ermining
whether thesystem isoper�ing bdow desc,�flow-r�es cai be pe-Formed by visral ins�ections
The mantell7toe pfocess comprises the removal and replacement of each BayFilterTM cartridge and the
cleaning of the vault or manhole�vith a�racuum truck.BayFilterTM maintenance should be performed by
a Bay�er Technoio�es, Inc. oertified mantenaioe oontractor, or other paty traned by Bay93ver
Techr�olajes, l nc.
Bay3�✓er Technolcx,�es, I nc. offers three different options to owners of a system in regads to
mantena-i�outlined bdow.
• Bay�ver Technologes offas education aid traning services to owners of, or muniapalities
mantaning their BayFilter systems
• If the st�owner or muniapality would preFer to outsource manteianoe oper�ions to a third
party, Bay�+er Tedinologes mantans a list of oertified oontradors in the geogr�hic region
needed.
• lf the st�owner or muniapality would prefer that B�yRaver Technolajes, Inc. mantan the
sy5tgns, a contract can be reached between Ba�ver and the owner, in which Bay�ver will
outsouroetheservicesto aoe�tified mantenanoecontractor.
If the s�stem being instailed is a pilot test projed for the Washington St�te Depatrr�ent of Ewlogy, I'
Bay�er will maintan thesystem until testing h�completed.
Thae as two oore wmponasfs of maintenanoe on a Ba�Filter system. The first component is the
required seni-ainual in�ionsof thesystem,theseoond isthemanta�aioein which thefiltersrequire
rq�laoen�ent.
General I nspection Procedure
D uring a storm�ver�t
• I n�ions c�n be performed during both dry a1d wet se�on, e�en during a storm-evait. I n
Washin�on, the filter systems ae deagned in ai off-line configur�ion. After lifting the acoess
wver from the top of the va�lt or ma�hol� w�a will c�ident within the system. If water is
spilling over the bypa�swer d�ing a storm,thefilters ae probably operating below desgi-flow
rates The only acoe�tion to this is in the ca9e where the spifl-over is observed during a peek
storit�rent, in which some of the flow will bypa�s the system. lf flows ae observed spilling
over the bypass during a storm ewent, a seoond inspec�ion should be scheduled duing a dry-
period to verifythefiltersaeoperatingbelowthedesgi eFfiaency.
—�
i
• I f no water ca�be observed bypa�i ng the system during a storm event,it c�be conduded that �
the BayFilt� system is oper�ing as desg�ed. Continue regular inspections at the sx-month
interval until an average lif��y+de has been determined for the particula�stem.
• I n addition,the BayFilter system still needs to be inspeded a�ter major storm ev�ts !,
D uring a dr�� �
� An inspec�ion during a dr�period is prefared over an inspection d�xing a storm Event, because i
in addition to indicating to the inspedor whether or not the system is 0cpired, lifecyde
estimates ca� be determined by the amount of sediment aocumul�ed at the bottom of the
housing structure
• During a dry period, the insde of the va�lt or ma�hole should only carry a modest ano�t of
�vater (<_1'�. If more rhan one inch of water is obsaved � the floor of the vault, the system
needs to be mantaned.
� Assuming water le�-els within the housing structure indicate the system isn't espired, sediment
�ould be measured to d�ermine the rate of aocumulation. BayFilta systerns �ould be
mantaned when four indies of sedimait have aocumutated on the floor of the vaultl manhole
to ensure proper opa�ion of thedran-down modules
General Mairrtenance Proc�dure
Mantenanoeof the BayFilter sys#an requirestheremoval a�d re�lacement of the BayFilter catridges,
vaouuming of the bottom of the housng structur�and r�a�rnbly of the drain-down manifold.
1. R�rnov�e the ma�hole oov�s aid open�I acoess hatches
2. BeFore enteri ng the system make sre the ar is saFe per 09-I A Sta�dads or use a bre�hing apparatus.
Use low 02, hi�CO,or other applicablewaning devioes per regulatory requiranents
3.Usng avacuum trudc renove any liquid and sadimentsth�can be removed prior to entry.
4. Usng asmall lift or the boom of thevacuum trudc,ranovethe used catridg�s by lifting thefn out.
Usethetrolleysystem to removecartridgeswhen applic�le.
5.When all ratridgesae removed, rgnovethebala�oeof thesolidsaxf water;then loosen theunder
dran manifold and removethedran pipesaswell. Carefullycapthema�ifdd and rhe Fern�o's and r;,�se
thefloor,remo�ingthebalanoeof thecollec�ed s�lids.
6.Cleai themanifold pipes,insped,and reinstall.
7. i nstal I the exchange c�rtridges atid dran-down modules,then dose all oovas
i � D. R. STRONG
CON5ULTIIVG ENGINEERS
May 22, 2013
Project No. 12029
Jan Illian
Development Services
City of Renton /
1055 S. Grady Way, 6'h FI. � �i'�
Renton, WA 98057 �3 G�
Re: Project File No. LUA12-076, ECF, PP ����
Piper's Bluff �
Dear Ms. Iliian:
Thank you for your coordination and review of this project. We have carefully considered each
of the comments in your letter dated April 3, 2013. Additional information has been provided
and revisions have been made, as appropriate. The following is a summary of the actions taken I
in response to each comment. '
Storm Drainaqe Comments:
1. See pages 8 and 9 of attached wetland report.
2. See pages 8 and 9 of attached wetland report.
3. See pages 8 and 9 of attached wetland report.
� a. Spill control measures will be achieved in the control structure with FROP tee. See �
sheet C13.
�b. Spill control maintenance and operation manual have been included in Section X of
the drainage report.
4. A note has been included on sheet C8 which will allow the City to access the Site for the
inspection of flow control BMPs to be constructed on the lots. The note shall also be
���� included on the final plat map.
(,a�c���'�,.-5. The HOA shall be responsible for the maintenance of landscaping within Tract "A". The City
P�`f� � shall be responsible for maintenance of the drainage facilities constructed within Tract "A".
A storm drainage easement to benefit City of Renton shall encompass all of Tract "A". �
�6. A fence has been placed around the perimeter of the pond. II
7. Outfalls have been sized according to 2009 KCSWDM. See Section V of the Drainage I
Repart. ,
8. The outlet of the stormwater facility is proposed within the wetland buffer, which is an ',
exempt activity per RMC Chapter 4-3-050.C. However, any area disturbed during �,
installation of the outfall will be restored with native trees and shrubs. ��
9. Additional notes (a, b and c) have been added to the ESC Plan. � �
10. Within the drainage plan, the additional comments have been noted, two catch basins have
been provided on Hoquiam Ave NE, and catch basin 1 has been altered to a dual directional
vaned grate. According to Chapter 4.2.1 in KCSWDM 2009 under pipe clearances, a
minimum of 3 feet horizontal clearance shall be provided between storm drain pipes and
other utilities. This is provided.
Sewer Comments:
1C.,_-.N E - ^I�r�
Sui'e�.._
1 a. All DI pipes have been changed to C900. "�rPno eV(25)827-3CS3
1b. Sanitary Sewer Manhole 2 now has a 90 degree connection with Sanitary Sewer Manhol��l�4zs�sv-�a^�
Toll Free:(800)962-1a�_
vrnw.drstrong cc�-
Engineers � Surveyors I Landscape Architects
. Jan Illian Ii
hlav 22.2013 I
+ Page 2 of 2 ',
1 c. A typical side sewer callout is shown on the Sanitary Sewer Plan as weil as all the invert
elevations of the stubs.
Street Comments:
1a. A transition ramp is shown in the NE corner for pedestrian use.
1 b. See 1 a. �
1 c. Clear space has been limited to one location in the middle of every block for fire trucks and I,
minimized to 20 feet with the 5 additional feet included in the planter.
1d. No parking signs have been added within the fire truck clear area space and also on one
side of street.
1 e. The paving note has been added to the plan sheet.
1f. The cross section has been adjusted to match what is shown on the plan sheet.
Detail Comments:
1. All current storm and sewer details are included on the detail sheet. I'
If you have any questions regarding the revisions, please do not hesitate to contact me.
Sincerely yours, ;,
D. R. STRONG Consulting Engineers Inc. I
; '�
, , I
Nadeem . Khan
Senior Design Engineer
NAK/qhh
R:',2012'.0�]20?9�3 iDoctmreia�s lLetters'�L 130-116 lllinn.cloc
. ,
__ _ _---
,--�` ;� Sewall Wetland Consulting, Inc.
- -_ 27641 Co��ngtpn 1 ti'ay SE#2 Phone:25_'i-8.59-0615
----- Covmgton WA 9�2 Fax:25.�852-4732
April 15, 2013
Peter O'Kane �
WestPac Homes, LLC
7449 West Mercer Way
Mercer Island, Washington 98040
RE: Pipers Bluff Plat—Rei�ised City of Renton Critical Areas Report
& Supplemental Stream Study
SVVC Job#12-135
1.0 INTRODUCTION
�
This report describes jurisdictional wetlands and streams on the 5 acre proposed Pipers
Bluff Plat, located on the east side of Hoquiam Avenue NE in the City of Renton,
Washington (the"site"). Specifically,the site consists of a rectangular shaped group of
four(4) abutting parcels in a portion of the NE '/4 of Section 10,Township 23 North, '
Range 5 East of the Willamette Meridian in King County, Washington.
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Aipers Bluff'�12-13_S
Sewall i1'etland Consulti��g, Irrc.
Apri!I5, 2013
Page 2
The site consists of four Parcels including#1023059002, #9367, #9312 & #9144. Single
family homes are present on two of the parcels along Hoquiam Avenue, and the
remaining property besides the associated lawns and landscaping is undeveloped forested
area.
The site is proposed to be subdivided into 30 single-family residential Lots���ith
associated roads, and infrastructure.
2.0 METHODOLOGY
Ed Se���all of Se���all Wetland Consulting, Inc. inspected the site on June 6, 2012.The site
«�as reviewed using methodology described in the Washington State Wetlunds
Identifrcation Manual(WADOE,March 1997). This is the methodology currently
recognized by the City of Renton and the State of Washington for wetland determinations
and delineations. The site���as also inspected using the methodology described in the
Corps of E�igineers Wetlujzds Delineution Ma�icral (Environmental Laboratory, 1987),
and the Western Mou►�tains, Vulleys und Coast region Supplement(Version 2.0) dated
June 24, 2010, as required by the US Army Corps of Engineers. Soil colors�vere
identified using the 1990 Edited and Revised Edition of the Mu�tsell Soi/Color Charts
(Kollmorgen Instruments Corp. 1990).
The T�'ashin ton State Wetlancls Identi rcation ar�d Delineation Mar�ual and the Cof• s o
g .f P .�
Engineers Wetlands Deli�eatios�Mar�a�al/Regional Si�pplenzent all require the use of the
three-parameter approach in identifying and delineating wetlands. A���etland should
support a predominance of hydrophyrtic vegetation, have hydric soils and display wetland
hydrology. To be considered hydrophy�tic vegetation, over 50%of the dominant species
in an area must have an indicator status of facultative (FAC), facultative wetland
(FACW), or obligate wetland (OBL), according to the National List of Plant Species That
Occur in Wetlands:Northwest (Region 9) (Reed, 1988). A hydric soil is "a soil that is
saturated, flooded, or ponded long enough during the growing season to develop
anaerobic conditions in the upper part". Anaerobic conditions are indicated in the field
by soils���ith lo�v chromas(2 or less), as determined by using the Munsell Soil Color
Charts; iron oxide mottles; hydrogen sulfide odor and other indicatars. Generally,
���etland hydrology is defined by inundation or saturation to the surface for a consecutive
period of 12.5% or greater of the growing season. Areas that contain indicators of
wetland hydrology beriveen 5%-12.�%of the growing season may or may not be
wetlands depending up�n other indicators. Field indicators include visual observation of
soil inundation, saturation, oxidized rhizospheres, water marks on trees or other fixed
objects, drift lines, etc. Under normal circumstances, indicators of all three parameters
���ill be present in «-etland areas.
Piper.c t3ltrff���'12-13�
Sewall li"etland Consulting, I�7c.
April 15, 2013
Pu�e 3
Follo«-ing delineation ofthe wetland and stream on the site,the flags were surveyed by
D.R. Strong Consulting Engineers (see attached survey).
3.0 OBSERVATIONS
3.I E_risting Site Documentation
Prior to visiting the site a revie�v of several natural resource inventory maps ��as
conducted. Resources reviewed included the NRCS Soil Surve��, National \�'etlands
Inventory, and the City of Renton's �'�'ater Class map.
3.I.1 Soil Survey
According to the Soil Surve}, King County Area, Washin�on (Sntider et al 1973),the
entire site is mapped as containing Alderwood gravelly loam soils (Map Units AgC &
AgD). Alderwood soils are moderately-well drained soils formed in glacial till under
conifers. Alder�vood soils are not listed as a "hydric" soil according to the publication
Hvdric Soils of the United States (USDA NTCHS Pub No.1491, 1991). Ho���ever,
Alder���ood soils can contain small inclusions of poorly drained hyric soils such Norma.
Bellinaham, Seattle, Tuk��-ila and Shalcar soil series.
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Pi ers Blu i�12-135 ��
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Sex-all 1�'et/and Consulting,Inc. ,
.4p�•il I5, 2013
Page 4
3.1.2 Nutional Wetlands Inventory
According to the National Vl'etlands Im�entor} there are no wetlands or streams located
on or near the site.
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3.1.4 Cit,y- of Renton Water Class Map
According to the City of Renton Draft Water Class Map, the upper reach of Honey Creek
is located on the northeast corner ofthe site. This stream is mapped as a Class 4 stream
b}-the City(bro�o�n stream shading).
Pi/�cr.e Rltrlj'r:l?-13i
Setiral! li'e�lurid Coas�rlti�ig, l��c.
Apri! 1�, 2013
Page S
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_Abnt�e: Citv orRentof7's i�'ater Tt�e hfap
3.2 Field Obser��ations
3.21 Upla��ds
The site is located near the crest of a hill ��ith the property sloping dow n to the east
towards Honey Creek. As previously mentioned, several structures as�vell as associated
la�vn, driveway and landscaped area is located along the west side of the site.
The area along the west side of the site includes immature red alder, big-leaf maple, old
apple trees, cottonwood, dense thickets of blackberry, hazelnut, salmonberry and sword
fern. The �vestern end of the site appears to have been cleared at one time but has been
re-vegetated ���ithin the last 20+years. The majority of the site is covered��-ith a mixed
forest�vith conifers as the main component in the overstory. Douglas fir�vith several 4'-
5' dbh specimens are the dominant species in the overstory with scattered big leaf maple
and red alder. Understory species include hazelnut, indian plum. elderberry. s�vord fern.
salmonberry, and stinging nettle.
Soil pits excavated within the upland area of the site revealed soils«ith proliles similar
to the mapped Alder�vood series.
i
Pipers Blt ff'�12-135
Setivall l�'etlai�d Consarlting, Ii�c.
April 1�, 2013
Page 6
3.2.2 Wetlands I
A single scrub-shrub, riparian�;retland was identified and delineated along the northeast
corner of the site. The�vestern edge of the�vetland��ras flagged with orange/black
flagging labeled AA 1-AA2-A 1-A7, and the east side with B 1-B4. This narrow band of
���etland borders Honey Creek���hich passes through its center flo�i-ing in a northerly
direction.
Vegetation in this�vetland consists of small pacific w�illo�v, salmonberry, lady fern, skunk
cabbage and manna grass.
Soil pits excavated �vithin the���etland revealed a sapric muck soil with a color of lOYR
2/1 ��-hich��-as saturated���ithin 12"of the surface.
�'etland A«�ould be classified as PSS1C (palustrine, scrub-shrub, broad leaved
deciduous, seasonally flooded) according to the US Fish and Wildlife Wetland
Classification methodology(Cowardin et al. 1979). �
According to the criteria in City of Renton Municipal Code (RMC) Chapter 4-3-O�O.M.1,
Wetland A��-ould be classified as Category 2 wetland. Category 2 ��-etlands are defined
in the Code as follo��s;
11. Cutegorp 2: Category 2 wetlar�ds are ivetlands tivhich meet one of-ntof-e
of the folloiving criteria:
(aj l�'etlands that are �rot Catego�y 1 or 3 tivetla�rds; and/or
(bj j�'etlands thaJ have heron rookeries or osprey nests, but are not
Categofy 1 wetlancls; anc�/or• ,
(c) i�etlands of any si.ze located at the headtia�aters of a lvatercourse, ',
i.e., a tivetland u�ith a pes•ennial or seasonal ou�ow channel, but ivith no defined inflatent ' '
char�nel, but are not Category 1 wetlands; a�rd/or ,
(d) i��etlancls having rsiinir�ium existing evic�enee of hirnxar�-relazed ',
physical c�ltef•ation sa�ch as dikis�g, ditchi»g or cl�armelization; arzd�or '
According to Renton Municipal Code (RMC) Chapter 4-3-OSO.M.I,"Wetland A"best
meets this rating as a���etland with minimum evidence of human related physical
alteration, but not meeting the criteria of a Category 1 or Category 3 wetland. Typically,
Category 2��etlands have a 50' buffer measured from the wetland edge.
3.2.3 Streums
As previously mentioned, Honey Creek passes through Wetland A and the northeast
corner of the site. As required by Code, the ordinary high water mark(OHWM) of the '
creek as I7agged with �vhite/blue dot flagging labeled Wl-W8 on the ���est side and E1-E4
Pipers Bliiff��12-135
Seivall I�'etland Consultir�g, Irac.
April I5, 2013
Page '
on the east side. This is depicted on the attached D.R. Strong Consulting Engineers Plat
map.
Honey Creek is a slo�v flo�i�ing mud and sand bottom stream as it flows northerly through
the site. Trash, pallets and tires line the edge� of the creek in this area, although �
other��•ise, the stream appears relatively healthy with about 6" of flo«�ing water across its �
channel. The stream is strongly influenced by storm�vater outfalls upstream as flow in I
the channel �i-as noted to quickly increase follo«�ing a rain event. I,
The stream buffer on the project site is very healthy and includes large deciduous and ��i
coniferous tree species��-ith a dense native understory. To the east and off-site,this '
buffer has been impacted by clearing and use of the areas as la���n for single family homes
to the east.
Honey Creek is mapped as a Class 4 stream by the City of Renton. Class 4 streams are
"non-salmonid bearing«�aters during years of normal rainfall and/or mapped on Figure 4,
Renton Water Class Map, as Class 4".
According to RMC Title IV Chapter 4.03.OSO.L.S.a, Class 4 streams have a 3�' buffer I,
measured from the OHWT�I of the creek. '
Although Honey Creek is a non-fish bearing�vater in this reach, appro�imately'/4 mile
do��rnstream of the site this creek does become fish bearing. As a result this portion of
the creek (and associated���etland)has an important function in providing a hydrologic
source and attenuating lo��� flo���periods of year for the do���nstream fish bearing section.
Wildlife use of the creek is limited to ti�pical urban tolerant«rildlife including deer,
raccoon, coyote,
4.0 FUNCTIONS AND VALUES
The ���etland on-site was analyzed for function using the Washington State Department of
Ecology Wetlands rating System for�h'estern Vl'ashington. This system is typically
utilized to classify wetlands, but the classification is function-based, scoring three main
functions, 1,)water quality,2) hydrologic function, and 3)habitat functions.
Li'etlar7d A-Vl�etland A was rated as a riparian wetland and scored a total of 52 points
indicating a Category 2 wetland under this system which indicates inoderate-high overall ��
functional value. Its highest scoring function�tiras for water quality«-hich scared 20
points, and its hydrologic fimction�vas moderate at 18 points. Habitat value«ras
generally low at 15 points due to the lack of unique habitat features, lack of a variety of
plant communities, and the close proaimit}� of de�velopment to its boundaries. ��
_ �
Prpers Bl�r f'�12-13J
Seia�nll {i�'etlai�d Cons��rlting,Inc.
April 1�, 2013
Page 8
5.0 REGULATIONS I
In addition to the�vetland regulations previously described for���etlands and streams,
certain activities(filling and dredging)���ithin "waters ofthe United States" may fall
under the jurisdiction of the US Army Corps of Engineers (ACOE). The ACOE regulates
all discharges into "���aters ofthe United States" (wetlands) under Section 404(b) ofthe
Clean VVater Act.
Due to the increasing emphasis on Endanaered Species Act compliance for all fills of
�'�'aters of the United State and V6'aters of the State, both the Corps of Engineers and
W'ashington Department of Ecology should be contacted regarding permit conditions,
compliance, and processing prior to commitment to any fill of�vetlands or streams for
this project.
6.0 PROPOSED PROJECT
The proposed project is the construction of a 28 lot subdivision with associated access
road, and storm water facility.
The outlet of the stormwater facility will also pass through the���etland buffer. This is an
exempt activity«-ithin the wetland buffer according to RMC Chapter 4-3-OSO.C.
Ho��rever, any area disturbed during installation of the outfall«-i11 be restored with native
trees and shrubs.
7.0 HYDROLOGIC ASSESSMENT
The proposed project has been designed to avoid the wetland, stream and its associated
buffer. However, the proposed storm��-ater outfall�vill disperse���ater from the site to the
buffer area and the associated wetland and stream. Wetland A is a narro�i�band of
riparian��retland«�hich is strongly influenced by Honey Creek flo��•s as well as outflo«�s
of storm�vater facilities located south of the site. The creek and water entering the site '
from the south are the main sources of hydrology to the��-etland. Other hydrologic
inputs to the creek include direct precipitation as���ell as potentially some minor surficial
ground«later outflo����from the site.
The amount of«�ater flo�ving from the sites surface to the��-etland and creek appears
minimal, with no evidence of sheet flow and only a potential minor contribution from
infiltrating precipitation. The project proposes to discharge���ater from the stormwater
facilit}'to the edge of the wetland in a rock lined dispersal pad. This should insure water
that currentiv makes it��av from the site to the�vetland and creek continues to do so.
;
Pipers Bluff�'�12-135 ��
Setivall l{�etland Co�zsulting,Inc. ,
�pril 1 S, 2013
Page 9
Based upon the calculations in the Revised DR Strong Drainage Report for Pipers Bluff
(dated January 31, 2013-see table belo«�),there is a minor increase in the flowJ rates off
the site from pre-developed rates. This should insure the project will not dry out the
�vetland, and that adequate hydrology enters the���etland to maintain its viability.
DESIGN INFORMATION INDIVIDUAL BASIN
Water Qualit desi n flow
Water Qualit treated volume
Draina e basin(s
Onsite area inlcudes fronta e 4.98
Offsite area 0
T ot Stora e Faali Pond
Live Stora e Volume re uired) 69,132 �
Predev Runoff Rate 2- ear 0.139
10- ear 0.241
100- ear 0.402
Develo ed Runoff Rate 2- ear 0.928
10- ear 1.12
100- ear 1.88
T pe of Restrictor Fro -Tee
Size of orifice(restriction No. 1 0.88
No.2 1.50 �
No.3 1.40
Above: Table f3�om DR Str•ong Drainage Report
If you have any questions regarding this report, please call us at (253) 8�9-051� or at
ese��rall@se���all���c.com .
Sincerelv.
Se���all I�Y'etlarrd Cof��sultirr�, Is�ac.
.......r��-'-��,.�,--'
Ed Se�vall
Senior Wetlands Ecologist PVl'S #?12
Attached: Data Sheets
IVADDE Rc�ting Forrn
Site Plan/survey
Pipers Bluff/#12-135
Se�vall Wetland Consulting, Inc.
April 15,2013
Page ]0
REFERENCES
Co�;�ardin, L., V. Carter, F. Golet, and E. LaRoe. 1979. Classification of Wetlands and
Deep«rater Habitats ofthe United States. U.S. Fish and Wildlife Service,
FWS/OBS-79-31, �'ashington, D. C.
Daubenmire, R. 1959. A canopy-coverage method of vegetational analysis. Northwest
Science 33:43-64.
Diers, R. and J.L. Anderson. 1984. Development of Soil Mottling. Soil Survey Horizons,
Winter 1984, pg 9-15.
Environmental Laboratory. 1987. Corps of Engineers Wetlands Delineation Manual,
Technical Report Y-87-1. U. S. Army Corps of Engineers Watervvays Elperiment
Station, Vicksburg, Mississippi.
City of Renton Municipal Code
Hitchcock, C. and A. Cronquist. 1976. Flora of the Pacific North���est. University of
Washington Press, Seattle, Washington.
Munsell Color. 1988. Munsell Soil Color Charts. Kollmorgen Instruments Corp.,
Baltimore, Mary(and. ,
National Technical Committee for Hydric Soils. 1991. Hydric Soils of the United States.
USDA Misc. Publ. No. 1491.
Reed, P., Jr. 1988. National List of Plant Species that Occur in Wetlands: Northwest
(Region 9). 1988. U. S. Fish and Vl'ildlife Service, Inland Fresh��-ater Ecology Section, St. �
Petersburg, Florida.
Reed, P.B. Jr. 1993. 1993 Supplement to the list of plant species that occur in �vetlands:
North��lest(Region 9). USFWS supplement to Biol. Rpt. 88(26.9) May 1988.
WETLAND DETERMiNATION DATA FORM—Western Mountains,Yalteys,and Coast Region
Praject/Site ��7.�.J ��``� CitylCounty: ��"`"��"`� Sampling Date: G�� � �Z
Appkcant/Owner: State: Sampiing Point: ��
fnvestigator{s): �� ��� SecGon,Towtrship,Ranae.
�andform(hu+sbpe.terrace,etc.): LQcai reiief(concave,convex,none): S�ope(°�):
Subregion{LRR): Lat: Long: Datum:
Soil Map Unit Name: NWI cEassificaiion:
Are dimaGc 1 hydrobgic conditions an the site typicai for thfs time of year? Yes No_f� (If no,explain in Remarks.)
Are Vegetation .Soil ,or Hydrology significantly disturbed? Are'Normal Circumstances'present? Yes � No I
Are Vegelation ,Soil ,or HydrWogy naturally problematic9 (if needed,explain any answers in Remarks.y �
SUMMARY OF FINDiNGS— Attach site map showing sampiing point locations,transects,impartant features,etc.
Hydrophytic VegeW6on Present? Yes Mo �
la the Sampled Area
Hydric So+l Present? Yes No '� ,�
wilhinaWatland7 Yes No
Wetland Hydrofogy Present? Yes No
Remadcs: �gb�w- /3��yt. �a�..�•°•/1
VEGETATION—Use scientific names ot plants.
Absnlute Dominamt Indicator Dnminartce Test worksheet:
Tree Stratum (Plof size: ) °�Cover Soecies? Status �mber of Dominant Species
t. I�S����� n.�G+i'�J�Q•� G G ��✓ That Rre OBL,FACW,w FAC: � (A)
2.
Total Number of DominaM
3 Species Across All SbaW: � (B)
4.
Percent ai Domina�t Sgecies
=Totai Cover That Are OBL,FACW,or FAC: �� (NBj
Sao�innlShrub Stretum (PEot size� 1
t. l���%S ��S�c���— � F�v prevalence index wo►ksheer
Z. /Z;.5�s ��,���� �.� 3 v Fif-C Total 95 Cover of Muitiolv bv.
3. OBl species x t=
4. FACW speties x 2=
5, FAC species x 3=
=Total Cover FACU species x d=
H�b Stratum (Plot size: 1 UPL species x 5=
1. }i'lv, ti1'c w,.n. r,�—��--'� _� _L_ Coiumn Totals: (A) fg)
2.
g Prevalence Index =B/A=
q. Hydrophytic Vegetataon indicators:
5. Dominance Test is>50°h
g_ Prevalence�ndex is s3.0'
�_ Morptroiogical Adaptations'(Provide supporting
8 data in Remarks or on a separate sheet}
9 _ WeUand Non-Vasc�ar Plants'
�� _ Problematic Hydrophytic Vegetation'(Explain)
�� `Indicalors of hydric soit and wetland hydrofogy must
be present,unless distwbed or probiematic.
=Total Cover
Woodv Vine Stra3um (Plot size >
1 Hydrophytic
z vegetatiw, ✓.
Present? Yes No
=To:al Cover
°/a Bare Ground in tierb Stratum
Remarks:
US Army Corps of Engineers Westem M ountains,Va'Ieys,and Coasl-Interim Version
SOIL Sampling Pant: ��z
Profife Description: {Describe to the depth needed to dceument the indicator or confirm the absence of indicators.)
Depth btahix Redox Features � I
(inches} Color(moistl % Cobr(mast) 96 Type Loc Texture Remarks
3 "' d��
� io`in 3/3 _ � ,S L- II
'T G-Concentration,D=De tion,RM=Reduced Matrix,CS=Covered w Coated Sarxl Grains. 'Location: PL=Pore linin ,M=Matrix.
Hydrfc Sofi lndicators: (Applicahle to ali LRRs,unless otF�erwise noted.� Indicators for Problematic Hydric Soils':
Histosol(At) _ Sandy Redox(SS) _ 2 cm Muck(A10)
His6c Epipedon(A2) _ Stnpped Matrix{S6) _ Red PareM Material(fF2}
B�adc Histic(A3) _ Loamy Mudry Minera!(F1)(ezcept MLRA 7) _ Other(Explain in Remairks)
� Hydrogen SulCde(A4) � Loamy Gleyed Matrix(F2}
Depieted Beiow Dark Surface(A11} _ Oepleted Matrix{F3)
Thick Dark Surface(At2} _ Redox Dark Surface(F6) 'indicators ot hydrophytic vegebfion and
Sandy Mucky I�Aineral(S1) _ Depkted Dar1c Surface(F7) wetland hydrology must be present.
Sandy Gleyed Matrix(S4) Redox Depressions(F8) uniess disturhed or problemattc.
Restricdve Layer(if preaenq:
Type�
DepUt(inches): fiydric Soil PresentT Yes No �
Remarks:
Nu ,.,./, ��1`.i
HYDROLOGY
Wetiand Hydro{ogy Indicatota:
Primarv Indicators(minimum of one required check aU that aooWS Seco�darv Indicators(2 or more reauiredS
S�+iace Water(At) _ Water-Stained leaves(B9)(except MLRA _ Waier-Stained Leaves(B9)(MLRA!,2,
HigA Water Table(A2) 1,2.4A,and 48} 4A,and 48)
Saturation(A3) _ Salt Crust(B11) _ Drainage Pariems(B10)
Water Marks(61) _ Aquatic Invertebrates(B13} _ Dry-Season Water Table(C2}
Sediment Deposits(B2) _ Hydrogen Suffi�Odor(C1) _ Saturation VisiWe on Aerial Imagery(C9)
DriB Deposits(63) _ Oxidized Rhizospheres alorg Living Roots(C3) _ Geomorphic Position(D2)
Algal Mat or Crust(B4) _ Presence of Reduced Fron(C4) _ ShaHow Aquitard(03}
� Iron Deposits(BS) _ Recent Iron Reduction in Tilled Soils(C6) _ FAC-Neutral Test(D5)
SuAace Soil Cradcs(B6) _ Stunied or Stressed Plants(D1)(LRR A) _ Raised Mt Mounds(D6;(LRR A)
Inundation Visible on Aerial Imagery(87) _ Other(Explain in Remarks) _ Frost-Heave Hummocks{07)
_ Sparsely Vegetated Coneave Surface(B8)
�ie Observations: ,//�
Surface Water Present? Yes No " Deplh(mches)�
Water Table Present? Yes No��pth(inches):
Saiuration Present? Yes_ No_ Depth(inches): Wetland Hydrology PreseM? Yes No�
(indudes ca ifla ftin e)
Describe Recorded Data(stream gauge,monitonng well.aenal photos,previous inspections},ff available:
Remarks / /
,/t�o ir d'+ C a /v f
US Army Ccrps of Engmeers Westem Ma�ntains Valleys and Coast-Interim Vers�on
WETLAND QETERMINATION DATA FORM-Western Mountains,Valleys,and Coast Region
Project/Site �"?�^� Ciry�County� � �"� Sampling Date: �' y � ��-
AppliqnUOwner. State: Sampling Pant bQ Z �����
Investigator(s): �� ��'�/ Section,Townshg�,Range:
Landform(hilislope,terrace,etc.): Local relief(concave,cornex,rane): Slope(°.6►:
Subregion{LRR): Lat: Long: Datum
Soil Map Unit Name: NWI dassfication
Are ciimatic!hydrdogic conditions on Ne site typical for this tirne of year? Yes No � {If no,explain in Remarks.)
Are Vegetatior: .SaI or Hydrobgy significantly disturbed? Are'Normal C�wmstances'present? Yes � No
Are Vegetation ,Soif or Hydr�ogy naturally problematic? (tf rreeded,explain any answers in Remarks.)
SUMMARY OF FINDINGS- Attach site map showing sampling point locations,transects,important features,etc.
HydrophyGc Vegetation Present? Yes �No la U»Sampled Area
Hydric Soil Present? Yes� No W�thin a Wetland7 Yes �No
Wetland Hydrology Present? Yes No
Remarks: �,�ovc. Nr r h ti � � �
r.,,,, �
VEGETATION-Use scientific names of plants.
Absolufe Dominant Indicator pominance Test worksheet:
Tree Stratum {Plot size: ) 96 Cover Soecies? Status
Number of Domfnant Species �
t. That Are OBI,FACW,or FAC: (A)
2' Total Number o1 Oominant
3 Species Across AII Strata: �' (B)
4. i
=Total Cover Peroent of Dominsrtt Species / U J
SadmylShrub Stratum (Plot size_� That Are OBL,FACW,or FAC: (A!B)
t. /���"� Sta� •?.S � �'4� Prev�encel�dexworksheet
2. Total%Cower of MulUolv bv:
3. OBL spedes x t=
4. FACW species x 2=
5. FAC spec.ies x 3=
=Total Cover FACU spec�es x 4= '
Herb S[ratum (Pbt size: 1 I
/ ��„` �'' UPL species x 5=
t —����" F •y � F�� Colum�7otals:
�A1 (B)
2.
3_ Prevalencelndex =BtA= �
q, Hydrophytic Vegetation Indicators: '
3. Dominance Test is>5096 �
g, Prevalence Index is 53.0'
�. Morphological Adaplations'(Pro�ide supporting �
8.
data in Remarks or on a separete sheet}
9 _ Wetland Non-Vascular Ptants' '
Prob►emaGc Hydrophyuc Vegetation`(Explain) '
70. — '
'Indicators of hydnc soil and weUand hydro4ogy must I
�� be present.untess�sturbed or problematic- i
=Total Cover i
Woodv Vine Stratum (Plot size ) '
i
1. Hydrophytie �
2 vegetation
PresentT Yes No I
=Total Cover
%Bare Ground in lierb S[ratum
Remarks:
US Army Corps of Er.gineers Western Mountains.Valleys.and Coast-lnterim Version
SOIL Sampling Pant:_�Z ��
Profile Description: (Describe to the depth needed to doeument ths indicator or confirm the absence of indicators.►
Depth Mahix Redox FeaNres
finchesl , Cdor(moistS 96 Cobr fmasU % Tvoe� Loc� 7exture Remarks
__� �Q��� Z�f {.�,�,L�,..��l
1G foyh z!/ �
'T : C=Concenhation,D=De tion,RM=Reduced Matrix,CS=Covered m Coated Sancf Grains. 'Location: PL=Pore Lini ,M=Mavix.
Hydric Soil Indicators: (Appiicable to atl LRRs,uniess otherwise noted.} Indicators tor ProblemaGc Hydric Soils:
_ yistosol(At) _ Sandy Redox(S5) _ 2 cm Muck(A70)
'�Histic Epipedo�(A2) _ Stripped Matrix{S6) _ Red Parenl Maieriai(fF2)
Black Nistic(A3j _ Loamy Mucky Mineral(F1)(ezcept MLRA 1) _ Other{Explain in Remarks)
_ Hydrogen Sutfide(A4) ,_,_ loemy Gleyed Matrix(F2)
_ Depleted Below Dark SuAace(A11) _ Depleted Matrix(F3)
_ Thick Dark Surface(Al2) _ Redox Dark Sur(ace(F6) 'Indicators ot hydrophytic vegelation and
_ Sandy Mucky Mineral(St) _ Depleted Dark SuAace(F7) weqar�hydrWogy must be preseM,
S�dy Gleyed MaVix(S4) Redox Depressions(F8) untess disturbed or�oblematic.
Restrictive Layer(et preseM):
Type�
Depth(inches): HydNc Soll Present? Yes � No
Remarks:
HYDF20LOCsY
WeUand Hydrology indkatora:
Prima_ry Indicatms(minimum of one rea�red:check aIl that aoolvl Secondarv Ind�cators(2 or rrare reauired)
_ Surface Water(A1) _ Water-Stained leaves(69j(except MLRA _ Water-Stained leaves{89)(MLRA 1,2,
�Hi h 1Nater Table(A2) 1,2,4A,and 4B) 4A,and 48)
uration(A3) _ Saft C�ust{Bt1) _ ihainage Patlems(610)
��Water Marks(B1) _ Aquatic Invertebrates(B13) _ Ory-Season Water Table{C2)
_ Sediment Deposifs(B2) _ Hyd�oge�Sulfide Odor(C1) _ Saturation Vsible on Aerial Imagery(C9)
_ DriR Deposits�83) _ Oxidized Rhizospheres along LH'rng Roots(C3) _ Geomorphic Position(D2)
_ Algal Mat or Crust(84) _ Presence of Reduced Iron(C4} _ Sha�ow Aquitard(D3)
_ Iron Deposits(B5) _ Recent fron Redudan in Tilled Soils{C6) _ FAC-Neutral Test(DS)
_ Surface Soil Cracks(�) _ Stunted or Stressed Plants(01)(LRR A) _ Ra�sed Ant Mounds{D6}(LRR A)
_ Inundation Visible on Aerial Imagery(B7) _ Other(Explain in Remarks} _ Frosi-Heave Hummocks(D7)
_ Sparsey Vegetated Coneave Surface(B8)
Field Observatioru:
Suhace Water Present? Yes No � Oepth(inches):�� ;
Water Table Present? Yes ✓No �epth(inches): b �
�i
Saiuration Present? Yes��No_ Depth(inches): � Wetland Hydrology Present? Yes No ,
{includes ca iRa lrin e)
Describe Recorded Data(stream gauge,mooitonng well,aerial photos,previous inspections),if available:
Remarks�
US Army Corps of Eng nee�s 11lestem�.lourtains Valleys.and Coast-Interim Vers�on
µ'clland n�mc orr,urt�ba Wctland nime m number
wETLAND RATING FORM-WESTERN WASHINGTON Docs the wetlnnd unit beinR rnted meet nny of the criteria below?
Vcnion 2•Updatcd July 2006 tu in 7c�u eccuracy and rcproducibility among uaen lf you enswer Y�:S to any of ihe questions below you will need to protect thc wctland
Updated Ocl 200A with thc new WDFW defutitiom for priority habiWU aeeording to the regulations rogarding the speeial ehnracteristics(nund in the wetland.
Nnme ofwetland(if Anou�n): WL ,
gl,1j -l�.xw DAt�or:ito�i9ir. G-01- Z
� �A Check List for Wetlands That May Need Additional Protection YES NO
Raccd by_ � 3�,..V� Treined by Ecology7 Yes_No Dace of training in addition to the rotecti0n recommended for its cate o �
_._.._._.--- -- _
SPI.Has rhe wetlnnd unit been docr�mented as n hnbitat for am�1�'edernllv lis�ed
SGC:__._TW NSI If':__I2NQ&:___ Is S/T/R in Appendix D7 Yes_ No_ T/�reneened rn Endangered anima[nr plant eprNes(l/E species)?
For thc purposes of this reting system,"documentcd"mcans the wetland is on the
Map of wettand unit:Figure_ Estlmated size a ro rinto state or federal database.
SI'2.Ha.s the wt!lnnd unit been documenred as habitnl jor any Slate listed
SUMMARY ON itA'CING 77mentened or Endattgered animal species?
For thc puryoses oCthis rating system,"documented"means the wetlend is on the
eppropriate stare detabese. Note: Wotlands with State listed plant species are
Cnte�nry based o UNCfIONS provided by wctland cate orized ns Cate or I Naturnl I lerita e Wetlands sec .19 of data form.
1_ IT_ ul_ Iv_ SP3. Does lhe welland unit confalri individuals ofPrirniry species listed!ry(he
WDFYP.Jbr tl�e.stafr?
Score for Water Quelity Punetions ZU SP4. Dceslhe wetland imit hm�e a local significrmc¢in addrNon to ils fimctionr7
Category I-Score>-70 For exam Iq the wetland has becn identificd in the Shoreline Master
Cntegory II-Swre 51-69 Score for Hydrologic Functions D
Category N=Score 30-50 Scoro for Hnbitet Functions Program,the Criticnl Araes Ordinence,or in a local management plan as
having special significancc.
CateHorv IV�Scorc<30 TO'I'AL score for FuncHons
Category bxsed on SPECiAL CHARACTERISTICS of wetland
I_ II_ Does not Apply,_ To complele the next nar!oflhe data sheet vor�wl/I need to delerminc the
Hvdrogeomorahic Class otthe we�lcmd be�nQ raled.
F(rt8I CAtCgOI'y'(chooee the"highest"cntegory from abovej L ]� ' The hydrogeomocphic classificetion groups wellands into those thet funetion in similar wnys. This
� simplifies the questions needed to nnswer how well the wetland functions. The Hydrogeomorphic
Class ofa wetland can be determincd using Ihe kcy below. Ste p.24 for more detfliled instructions
Summa of basic informeHon about thc wetlnnd unit on classifying wetlxnds.
Wetland Unit hrs Specinl Wetlend HGM Clsa� :
CharacterGttca useU for Ratln ,
Estuarine De ressional
Natural Heritn c Wctlnnd Riverine
Bo Lake-frtn e
Maturc Forest Slo
Old Growth Forest Flats
Caastsl La oon Fl�eshwater Ttdal
Inferciuoxl
None of thc ebove Check if unit hes multiple
HGM classes resent
WeOand Rntine Fnrtn-weetern Nashington 1 Angu�t 2Q)�1 Wctland Knting Form-wcetcrn�1'achingmn _ Aupust 2(x1J
veninn 2�Lo tx:cec<I with Fcningy Nihlica�ion 04.Ofi.0� ver�ion 2 Updamd uitl�ncw NpE'q'dcfini�innv(icc 200R
Wetland namc nr nnmber _, Wcqand name ar numbtt_
Clnssi�cation of Wetland Units in Western Washington S.Does the entire wetland unit mect ell of the follawing cri teria7
�e unit is in n vnlley,or strenm chnnnel,�vhere it gets inundnted by ovcrbank
If the hydrnlogic crl4erla►bted in eech questlon da not spply to'the enNre anit lieing flooding from that stream or river
�7he overbank llooding occurs al lesst oncc every two years.
rated,you probably have s untt wlth mulHple HGM claeses. In thi�case,iilenHty whlcL NOTE:The riverine unit cnn contnin depressions that are frlled with wnter yv{ee�i the river is
hydrologic crlterla in quesNons 1•7 epply;fndgo to�uestlon 8. "--^�
notflooding. , .,-- _� . ,. ..,_,._.
NO•go to 6 1,'ES -The wetland dass is Riverine
'ti......._..�.........Q.
1.Are th� . cvcts in the cntirc unit usually controlled by tides(i.c.cxcept during tloods)7 6.Is the entire wetland unit in e topographic depression in which�vater ponds,or is saturated ro the
'SG'O– o YES–lhe wetland dass is Tidel Fringe surfAce,at some time during the year. Thr.r means lhat any outlet,ijpresent,is highPr than the
ICyes,is the salinity of the water during penods of annual low flow below 0.5 ppt(parts per rnrerror ofthe wetlond
thousand)? YE5–Freshwater Tidel Frinqe NO–Selhvater Tidel Fringe(F.stuerine) NO–go to 7 YES–Thc wetland clnss is Depressionel
/jyour wetlm�d can he classified as a I�reshwater Tidnl F'ringc nse[he fornes far Rivnine Z Is the ontire�vetlnnd unit locuted in a very flat area with no obvious depression and no overbank
wetlands. Ifit is Salhvater%'idalFsinge it is rated ns an Esluarine wrtluncl Wetlands that flooding. The unit does not pond suttace water more thun a few inches,The unit seems to be
were callcd cstuarinc in the frst and second editions ofthe rating system are cnlled Selt maintained by high groundwater in the nrea. The wetiand mey hc ditchcd,but hns no obvious
Water Tidal Fringc in the Hydragcomorphic Clessification. Estuarine wetlands werc natural outlet.
catcgorized separately in the earlier cditions,and this separation ia being kept in this NO–go to 8 YES–The wetland class is Aepresslonxl
revision. To maintain cunsistoncy between editions,the[crm"Estuerine"wctland is kept.
Please note,however,ihnt the charncteristics thet define Cetegory I and II estuarine 8.Your wetland unit seems to be difIicult to classify and probably contains several diifbrent HGM
wetlands have changed(see p. ). clasee. For examplq seeps at the base of a slopc may grade into a rivorine floodplain,or a smell
stream within a depressionel wctlnnd has a zone of flooding along its sides.GO BACK ANb
2.The entire wetland unit is flat and precipitation is the only source(>90%)of water to it. ID�NTIFY WHICH OF THE HYDROLOGIC RE(3IMES DESCRIBED IN QUESTIONS 1-7
�G-�,ro�u-n--d-w�-a�te�r,nnd surface water runotF are NOT sourcea of water to thc uniL APPLY TO DIFFERENT AREAS IN THF.iJNIT(makc a rough skctch to hclp you dccide). Usc
�:__n;yu,r' YES–The wetland cfass is Flnts the following tnble to identily the�pproprintc ctass to usc for the rnting system if you hnve scvcrrl
If your wctland can be classified as a'Tlats"wetlend,use the form for Depressional HGM classes present within your wetland. NOTE:Usc this table only if the class that is
wettands. recommended in the second column rnpresents 10°/or more ofthe total area ofthe we0and unit
bcing ratcd. If thc arca of thc cless listcd in column 2 is Icas than 10%of thc unit;classify thc
3. Does the entire wetland unit meet bath of tho following criteria? wctland uaing the clase that roprosents more than 9U%of the tota!area.
_'Ihe vegetated paR of the wetlnnd is on the shores af a body of pertnenrnt open wnter
(without any vcgetation on the surface)at Ica�t 20 ecres(8 ha)in sizc; HGMClnsses within thr,werlmrd��ni!bein rnted HGMCIass m Use inRntm
t Ieast 30%of the ope�water area is deeper then 6.6 ft(2 m)7 Slo e+��verino Riverine
""`�O go YES–T'he wetland class is Lake-trinqe(Lecustrine Fringe) Slo e+De ressional Dc ressional
4.Docs the tntire wetland unit mcet s11 of the following critoria? Slo e+�ke-£rin e Luke-frin e
_ Thc weUxnd is on a slope(slope can be very grad�mn, De ressional+Kiverine along slrram within boundnry De ressionnl
_The water flows through the wetland in one direction(unidircctional)and usually De roasional �Lakc-Gin c Dc ressional
comes from seeps. It may flow subsurface,es sheetflow,or in n s�vale without Salt Water Tidal Fringe and any other class of freshweter Treat as ES'CUARINli under
diatinct banks. wetland wctlnnds with specinl
The water]eaves the wetland without being impounded7 charectoristics
NOT'E: Surjace waler does not pond in lhese lype ojwetlandt except occasionafly in
verv smrsll andshal(aw depressians ar b¢hind hummocks(depressions are usunlly If you are uneblc still to determine which of the nbove criterin apply to your weflsnd,or if you
diameter nnd Ie.rs thnn 1 joot daep). have more than 2 HGM classcs within a wctland boundary,classify the wetland es Depreseionnl
�NO-go to 5 YES–The wetland class is Slope for the rating.
Wetlend Reting Fortn--weetem Waelungton 3 Augnst 2004 Welland Rsting Form-wcetcm Washington 4 Auqust 2004
vtteiort 2 UpAaled wi�h new WpF W definitiomi pet 200R venion 2 Updated witli new WDFW definitiona Ocl 2008
Wetland namc or number WctlenJ namc or numbcr
R Riverine and Fresh�vater Tidal FriaQe Wetlands Points
wAI'ER QuALTTY FiINCT7oNs - Inaicatore thet w�tland fdnetiona to improve «i��� R' ltiverine and Freshwatcr Tidul Fringe Wetlands Points
water uali P`6oi� HYDROLOOIC FtJNCTTONS - Indicatore that wotland fUnetione to reduce ����
]t R 1.Does the wetiend unit hnve the t t 1 to Impmve water quafity? (see p.52) tloodie and stream'crbsion'
R 3.Doea the wetland unit 6ave t6e te tia to reduce t]ooding and erosion? (see p.54)
R l.l Aran of surface depressions within the rivcrine wetland that can trap sediments Flqure_
R R R J.1(.'haracteristics of the overbank storaga the unit provides: figure_
during n flooding event: Esttmate Ihe m+erage wtdth nfthe wetland unit perpendicular la the dtrection nfthe
Depressions cover`3/4 area of�+efl¢nd points=8 flrnv und the wtdt{�ofthe atream or river channe!(distance fxtween banks). Calaelate
llepfessi0ns Covef?1/2&tea of wetland points=4 �he rutio:(averug¢width oJuniQ/(avrruge widrh ojstream brtween band•sJ.
Ii depressions>'/a of area af untt draiw polygom on aarial photo or map.,,
Depressions prescnt but cover<1/2 aree of'wetlend +,rpo�nt�'_� ]f the ratio is more tlien 20 points�9
No de ressions rosen[ oints-0 �' If the ratio is betwten 10-20 points a 6
R 1.2 Cheracteristics of the vegetatiun in[he unit(ereaz with>90%covm et parwn height): � Flqure_ If the ratio is S-<10 .
R � If the rafio is 1•�5 in =�
Troes or shrubs?7/a the aroe of the unit
Trces or shrube>V3 eree of the unit points=6 If the ratio is<1 pomts-I Z
Un�nzed,herbaceous plents>2/3 nrce of unit poinis=6 Aedal hoto or ma showin avere e widths
R 3.2 Characteristics of'vegetation that slow down water veloci[ies during tloods:Trear Figure_
Unprnzed harbacaous pinnt�>I C.!erea of unit points^'3 � R Iqrge woody d¢brls as'forest or shrub". Choose the potnfs approprlate for the best
7'rees,sluubs,und ungazeA herbecaous<1/3 area of unit points-0 descnptton.(polypans need ro have>90Yo mver et person height NOT Cownrdin cle.veel
Aedel hoto or me showin ol ons of dlMuront vo oM[ion s Forest or shntb for>I/3 aree OR harbeceous plants>?/3 aroa mts=
R Add fhe points in(he bosca nbove ��,' I Foreat or shrub Por>1/10 nrea OR herbaceous plents>1/3¢rea pomts=4
jt R 2.Uoes the wetland unit heve the oonortunitv to[mprove water quellty? (set p.53) Vegetation doos oot meet ebove critarie points�0 �
Answa YES if you know or believe thrne arc pollutents in p{oundweta a sud'aca weter Aerial hoto or ma ahowin ol one of dkfareM ve atation s � ��
coming into the wetland thnt would otherwix roduce wnter qualiry in streams,leke+or R .4dd the poinra in the boses above �— �_—�
groundwater downgredient from the wetlend?Note whtch ofthe fallowrng condttions R R 4.Dnes the wetlend unit have the onnortunitv to reduce floading and erosion? (see p.57)
prnvide the sourrea ofpollutarttr. A unit may have pallu�ants coming from severa! Mswer YES if the imit is in n location in ihe watershed wltere tha flood storage,or
aoureea,fnU any single source would qvaltfy aa oppartuniry.
reduction in water velociry,it provides helps protect downsfieum property and sqiu�tic
�3ruing in the wat(md or within 150it resources from flooding or excessive and/a eroaiva tlows.Note which of d�e fvf(owirtg
— Llnhented stormwxter diachargas to wetlend cortdltlons apply.
— Tillad fields or orcharda within 150 feot of wetlend 1�'Itiere ere human muctures and nctivities downstream(roeds,buildings,bridges,
— A stream or culvert Jischacges into wetland thxt dreins developed areeq fertns)thet can bo damagad by ilooding.
�esidenfial areas,fatmed fields,roads,a dear-cut logging — 'Ihere ere netural resources do�msheam(e.g.salmon reddx)thet can bc damaged
�ResidenAnl,urban areas,golfcourses nra within 150 ft of wetlend by floodinq
— The river or stream linked to the wetland has a contributing basin whae human — Other�________ __.,___, ._ ,. �_ multipf ier
activitics have raisul lovels of saliment,tuxic compounds or nunients in the rivcr (�1 nawer NO rflhe major aource of water to the wetland is controlled hy a reservoir or Nre
water a6we xtandards for weter quelity multiplier wedand it h a o the aedea afa dtkeJ Z
— Other 'Z YES ultiplier i NO muitiplier is I
YES mu ' lier' NO multiplier is 1 ---- R TOTAL -Hydrologic Functlons Multiply lhe seore f'rom R 3 hy R 4 / </
R TOTAL-Water QualIty FtincNons Multiply the scorc Gom R 1 by R 2 zD Add score to ta6le on p.1 � ��
Add score fo table on .1 Commeots
Commen[s
NcHanARn�ingFnrm-weatemWaahinginn 7 August2(N)4 Wet6ndHatingForm-weaternWaehingtort 8 Auguat2004
venion 2 Updated with new WDFW definitioro Oct 2008 vcniun 2 Updited with new WDFW definiuons Oct 2008
Nctland name or number Wetland namc m number I
7he.se questiores apply to-wdlands of af!HGM clusses. Points �i�.a.�,icrsoers�o�otn8b��acg�Se�R �6� ig�r�_
(onlyi.are Decidn from the diagams belaw�.fiather interspersion between Cowardin vegetation
HABITAT FUNC'ITONS•Indicators that unit funatib�Yo provide ittipottant habiffit pcb� classes(descri6ed in H 1.1),or the classes end unvegetated areas(can include open water or
mudflfl[s)is high,medium,low,ornone.
H 1.Dues the wetland unit have the tno entiul to provide hebitet for many species?
H l.t Ve�otntionsfi�cmre(�rep.72J Figure_ �O
Check rhelypes ojvegetation clatsea presenr(as defrned by Cowardin)-SITe threshold jor each �
cla.es ts'/.acre or more than 1�of tAe area!f unil is amal/er than 2.S acres. �
., Aquetic bed
Ewergent plsnts
�c�ub/ahrub(erees where shntbs have%30%cnver) b None-0 points ow�1 poi Moderatc-2 points
✓F'orested(areas where tras hevc>30%covar) �°`+• � `���!r��
1
/fthe unit har af�rexted elass ciuck tr ��
'fht fotested cless hna 3 out oC5 strate(cenopy,subcennpy,shrubs,herb8ceou�, �
moss/ground-cover)that eech covnr 20%within�he forested polygan .�
Add�he n:�mber ofvegetanan snuctures ihal qaalify. Ijyou hme: �
4 shucmros or morc points�4
Map of Cowartlin vegetatlon alasses 3 structuros poinn-2 �
2 siructuros points�1 � � � [riparien braidod channels]
I structure ints=0 High =3 points
H 1.2.H�drvneriods(see p.73) Figure_ NOTE:lf you have four or moro ctasyes or flvee vegetation classes and open water �
Check rhe rypes oJwater regtmer(lrydraperiodsl prescmt w7thin the wadand The waler the ratin is alwa s"hi ". Use ma o!Cowerdin ve etatan elasses
regime har 10 cover more rhan 1056 of fhe wetland or�/�acre to count(see trrxr jor {I I.S.SpOC16I H6bltflf FCAh1i05 �SLL�J.��f
desenpriona ojhydropertodaJ CHeck�he habJratfearures thnr are present in the wetlarrd The mimber ofchecks(e d�e
Permnnently flooded or inundatod 4 or moro rypes present points�3 rrumher ofpointr yrn�put into the rteet cnlumn.
=Seasonally flooded or inundated 3 types present pointa=2 _�ge,dnwned,woody debris within the wetlnnA(>4in.diameter and 6 ft long).
Occa.eianally flooded or inundated 2 types presrnt point=1 Stending mags(diameter at the bottam>4 inches)in tha wetland
�SeNra[ed only 1 type preaent poinLc=0 —
Permanently flowing sireem or river in,or edjacent to,the wetlanJ _Undacut banks ere present for at least ti.6 ft(2m)and/or overhanging vogetation extands at
�Seesonnlly flowing slream in,or adjflcrnt to,the wetlnnd leaffi 33 fl(]m)ove�d st[enm(or ditch)in,or ccmtiguous with thn uni[,for nt lenst 33 ft
_Lakrjringe wetland-2 polnts r (I Om)
Freshwa(er lidal wtlGtnd-2 polnls Map of hydroperiods _SMblt steep banks of fine mnlerial Ihat might be used by beaver or muskral Rn denning
(>70dcgrce slopc)OR signs of recent beever ac[iviry nre present(cur shn�ba nr�rees that
H 1.3.Richness of Yl�.t 3necies(ste p.75) _ � l�ave not ye!trarrred grey/brown)
Count tho numba of plant specios in thc wetlend that cover at least lU ft. (dt/ferenr p�rchea At laaet%.acre of thin-stemmed persishnt vegetation or woody brenches are present in areas
of the sarKe epecies cm!be combined to meer rhe rtze 7hreshold) ihet nre pamanenHy or seesonelly inundnted.(srructurer for egg-(aying by ampldbians)
You do not have to nome Ihe specter. ✓Invasiva pinnts caver less ffien 25%of tha wetland eree in eech strntum nf plents
Da not�rtclude Euraslan Mi foil,reed canarygrarr,purple loosestrije, Canadian Thistle — Z
If you countad: >19 species points=2 NOTF_:The 20%stated rn early prinlings ofthe manua!on puge 78 tt an error.
L/st species below tjyou wanr to: 5-19 species s- H 1.TOTAL Swre- potential for providing habitat � /_ �
<5 species �iirtS'�--0 Add the scores om tll.l,H1.2,Nl.3,H1.4,III.S � «� �
Comments r
�
Total for pegc�
WetLndRatingForm-weeternWoshington 13 Augtta[2004 We�landRatingForm-weetemWashington 14 puguxt2004
venion 2 Updatcd with new WDFW definitiom Oct.2008 vcninn 7 l;pdatrd wi[h ncw WUPW dctinitin v(lct 700R
Wetland name nr numba W'ctland nama or numbcr__._
H 2.3 Near or ediAcent to other p iot rin�hebRats listal bv W1�1W(see new ared crm�pMe
H 2.Does the wetland unit have the opportunity to provide habltat for many epeclrsR descripliores ojwDf�7Ypr'wray hobuats,and the canv6es in whirh Ihry ean he jound in
H 2.7 pyt�g(seep.80) Flpur�_ lhePllSreparr hfln://rvdlw.warov/hnh/nhdi�tJmreJ
Chooae ihe descrtpri��n fhar bt.rt represents condmon of buJf'erajwerland unte The hlghear scoring Which of the following priority habitats ue within 33Uft(100m)of the we�land unit7 NpTF_:the
cNterion thnt opp(eea�to 1he we�land 7a to be ueed ln�he ra�trtg.Seo�az�for definttfon oj connecMons do not have ro be rela�ively undisturbed.
"undisrurbed" _�apen Stonda:Pure or mixed stands of aspen greeter tlian 0.4 he(1 acre).
Oiodlversity Arces and Corrldnr+:proas of hebitet that are reletively importnnt to vuiws
— 100 m(330ft)of relntivoly undisNrbed vegeteted ereas,rocky�ra�s,or open weter>95% species of netive fish and wildlife(ful!descr�pfionr ir.WDFW PXS reporr p.IS7).
of oiroumCa��noe. tio shuctures ere within the undixtu�bed pM of buffa. (relatively �rbaeeoua Balds:Veriable size petches of�ass andl Forbs on shellow suils uver beJrcek.
undisturbod��lso menns no-grazing no landsceping,no daly human use) Po�nts-S Old-Qrowth/Matun forosts:(Old-erowth west of('ascade cres�l Stends of nt leest 2 troe
— 100 m(330 Y3)of reletivcly undisntrbod vegchted areas,rocky ereas,or open water? species,fonning a multi-leyared canopy with occssionnl smal!openings;witli At leest 2U
50%circumference. Polnt�-4 treeyRta(B trees/ecro)?8l cm(32 in)dbh or>200 yaers of ega (Mahire Ic�reslg) Stnnds
— 50 m(17DII)of reletively undisNrbed vegetaled amas,rc>cky ereas,nr open weter�95% with nvorage diemetars exceeding 53 cm(21 in)dbh;cro�m cover may be lesa that 100%;
circumferetu;e. po�s s 4 crown cover mey be less thet 100°%;dceey,decndrnu:,numbers of snags,and quantity of
— ]00 m(330ft)of relatively undiaturbed vegetated arees,rocky�reas,a open weter>25% latge downed mnterial is generetly less than thet found in old-growth;RO-200,��evs old
cimimference,. P���a�3 west of the Cascede cres[.
— 50 m(170ft)of relatively undishubad vegetatcd ercaa,rocky ereas,or open wata fa> OreRnn white Oak: Woodlanda Stends of purc oak ar oek/conifar essocietions avhere
SO°o circumtl'erence. Poinb-3 —�cmopy coverege of the oak componcnt is impor�ant(,�ufl dercripriona in WDF'�V'PNS
If buffer doee not meet arry of the crit�rfs above �porr p.I58).
— No pnved arcas(except pnved trails)or buildings within 25 m(80tt)of wailand>95% _NLperlan: The erea ndjecent to equetic systertts with tlowing water that contnina��loments of
circumferrnce. Light to moderete grazing,or lewns aro OK. Polnb-2 both equstic and terrestrixl ecosystems which mutually intluence eech ather.
— No pevad e�+:as or buildings within SOm of wetlend for�SO%cimumference. � '�•� _�V�atalde Pnirlea: Habaceons,non-&irested plant emnmunities that can either tnkn tha
LigM to moFlarntn�v.ing,or lawn�are OK. � fortn of e dry prairie or a wet preirie(ful/descrlptions in WDFW PHS reporr p.!61).
— Heavy grezing in buffer, Polnts�1 _Instnsm:The wmbinauon of physicel,biological,enN chanical processes and¢onditions
— Vegeuted buffers nre<2m wide(6.6fl)for more than 95%of the circumfaronce(e.g.titled thet intttact to provide funetionel life hietory requirements for instream fish and wildlife
fields,pevin3.besalt bedrock emend ro edge of wedand Pointa�0. —7 «�«g•
— BuRer daesmot meet eny of the criuria ebove. Polnt��1 �i _Neanhorc:Reletively undisMbed nearshore habitets. These include Cosstal Nearshore,
Asrial hoto showl bufTan Open Caast Neershrne,and Puget Sound Nearohoro.,(ju!!deacript(ona ojhabirdrr and rhe
H 2.2 CorriAors and Connections(setµBI) deJimnon ojrelative[y tmdlsturfred are in WDFW rep�rt:pp.167-169 andg/osrary m
H 2.2.1[s thn wetland pert of n rolativoly undisturbed end unbroken vege�ted ecxTidor Appendix AJ.
(eitha ripxrian or upland)that is at least L 50 ft wide,hes at leaat 30^h cover of stwbs,forest Csve�:A naturally occurring cavity,recess,void,or system of interconnected pnssnges undcr
ur netivn undisturtred preirie,that emtnxts to estusries,other wetlands or undisturbed the earth in soils,rock ice,or othtt geological formMions and is la'ge enough to wn�ein e
uplands that a�e at Iaest 250 naex in sixe7 (dams in riparian corndora,Jreavdy used grave! human.
rocds,paved r��ads,or¢conslderad 6r¢aks 1x tha corndar). _C11Rs:Oreata then 7.6 m(25 ft)high end cecurring befow 5000 ft.
YGS�4 polnta (go ro H 1.3) �"O�go tn- 22 Talw:Homogenous veaa of rock rubble ranging in avurego siu 0.t S-2.0 m(0�-6.5 R),
H 2.2.2 Is the wvetland pert of e relatively undisNrbed and u vegetated cortida cotnposed of basalt,andesite,sttd/or sedimenta[y rouF:,indtiding riprep slides end mine
(either ripannn or uplend)thet is at leest SOtI wide,has at leeri 30%cover of shru6�or tailinge.May be aewcieted with cliffs.
forest,and connects to eaNeries,other wotlends or undi�turbed uplends that ere et leest 25 . _Snage tnd Log�: 'I'rees ere con�idered snegs if they nra deed or dying and axhibit sufficient
acros in sicc7�OR n 4ake-fringe wetlend,if it does not hnva an undisturbad wrridor ns in decny cheractaristics m rnehle caviry exeevetior✓urelhy wildlife.Priority snegs have fl
the question a6me? diemeter nt brenst height of>S1 cm(20 in)in westem Washington nnd are>2im(G.S ft)in
YFiS-2 polnts (go ro H 1.3) NO-H 2.2.3 heighi. Priority logs are>30 cm(12 in)in diameta ut the largesi end,snd?6 m(20 R)
H 2 2.3 Is the�vetland: �O"g�
within.'�mi(8km)of e breckish or uli wnter aetunry OR If wetlend has 3 or mon priority habitats�4 po6ite
within 5 mi of n lagc field or pasture('40 ecees)OR / 1(wetland has 2 priaity habitats=3 potnt�
within D mi greata thnn 20 ecres? ! If wetland has 1 priwiry hnbitat-1 painl No hebitau-0 points
YF� 1 NO-0 Inb Nore.•A!!vagera�ed werlandr are by deJtnitlon a prJo�l.y habimr but are not tncluded in th�s �
liat. Nem6�x�etlara[r ore addre.rsed in uestion H lrl)
"1'otal for paµe �
A'ctland Rating Form-weekrn R'aehington IS Auguet 2004 Wct4nd ILling Furm-wee�crn Wyehingtun 1! Augu+t ZO(14
vereinn 2 UpdateJ with new\b'DFW definitione(kL 2008 vcnion 2 Updalcd with new WDPW'definitions Oct 2008
I
R'etland namc or number R'etland name or mm�bcr
L CATEGORIZATION BASED ON SPECIAL CHARACTERISTICS
H 2.4 Wcllend I,nnM;cno�(choore�hc ont destriptiort of�he landscape aroued 1he wdland that
best firs)(.see p.8f)
Thare ue at leasi 3 other wetlmds within Y'�mile,end the connectiofls betweea ihem ere Please determine if the wetlaxd meets the attributes�lescribed belo„�and circle the
reletively undish�rbed(light gtazing boC,vern wetlends Ol�as is I�ka shoti wilh aomc pppropriate answers ax�!Category.
bneting,but oonnections should NOT bu bisected by peved roads,ffill,fields,or vthar
development. �ints-5 W�►Aod"I'ype Cateqory
The wetland is laka-fringe on a leke with linle disturbence md ficrti erc 3 other lakafringe Check off mry crilena that apply[o lhe welland Circle Ihe Calegory wherr!he
weflnnds within h mile �ints�S
There ere at ler�t 3 other wetlands witktin'/,mile,PiTC the connectitms batwoert them nr a ro riate cri(oia ax met.
disturbai �n SC 1.0 Estuerine wetlends(set p.8�
The wetiand is 7.ake-fringe on a lake with disturbance and thera ere3 other lekafringo Does the wetland unit meet the following criteria for Estuanne wetlancls?
wetland within'/:mile poinri=3
Thcrc is nt lasst 1 wetlend witl�in'/,mile. points=Z —The dominant water regime is tidal,
Thae are no wotlands within 15 mile. points=0 — Vegetated,and
3 — With a salinity greatcr than 0.5 ppt.
H 2.TbTAL Score- opportuniry for pmviding habitat 1 I YES- Go to SC 1.1 NO_
Add the scnre.sfrorn fl?.I,H2.2,H23,H2.4 � _�__� SC 1.1 Is the wetland unit within a National Wildlife Refuge,National Park,
Tc)TAO. Cor H 1 from page 14 G National Estuary Reurvc,Natural Area Presen�e,State Park or F.ducational, Ca�•�
Environmentnl,ar Scienfific Rescrve designated under WAC 332-30-151 T
Totel Score for Hebitet Funcfione -add the points for H 1,H 2:and record the rcsult on YES�Ca[e orv 1 NO o to SC 12
P•�- �� SC 1.2 Is the wetlend unit at lesst 1 acre in siu and mcets at least two ofthe
following three conditions? YES-Category I NO-Category II Cat 1
—The wctland is relatively undisturbed(has no diking,ditching,filling, Cat.11
cultivetion,grezing,and has less then 109 e covcr of non-netive plent
species. If the non-nalive Spartina spp.em Uic only species thxt cover
more then 10°%of the wetland, then the weUand should be givcn a dual Dual
rating(UII). The aren of Spartina would be reted e Category II while the rating
reletively undistivbed upper marsh with native species would bc a ��I�
Category I. Do not,howevcr,exclude the area of Spartina in
determining the size threshold of 1 acre.
—At least%.of the]andward edge of the wetland has a l00 R buffer of
shrub,fo�est,or un-grazed or un-mowed grasslend.
—The wetland has¢t leaet 2 ofthc Collowing feahues�tidal channels,
depressions with optn water,or contiguous f'reshwater wetlands.
Welland Rating Porm--weefem Waehington 17 Augue[2004 WetUnA ILting�orm�we�tern Waxhington l8 Augttnt 2(H14
venion 2 Updatcd with new WDPW defini[iona Ck4 2008 venion 2 Updated with new WDFW dcfinifio�u Oc�200R