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HomeMy WebLinkAboutEx 11_Drainage Report
PRELIMINARY
TECHNICAL INFORMATION REPORT
FOR
Towns on 12th
CITY OF RENTON, WASHINGTON
2/18/2022
Prepared by: Andrew Oh, E.I.T., Katie Lane, E.I.T.
Approved by: Holli Heavrin, P.E.
Date: 2/18/2022
Revised:
Core No.: 21008
RECEIVED
05/17/2022
AMorganroth
PLANNING DIVISION
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Core Design, Inc. TOWNS ON 12TH i
TOWNS ON 12TH
Table of Contents
1. PROJECT OVERVIEW .......................................................................................................................... 1-1
2. CONDITIONS AND REQUIREMENTS SUMMARY ................................................................................ 2-2
2.1 Core Requirements .......................................................................................................................... 2-3
2.1.1 Core Requirement #1: Discharge at the Natural Location ...................................................... 2-3
2.1.2 Core Requirement #2: Offsite Analysis .................................................................................... 2-3
2.1.3 Core Requirement #3: Flow Control......................................................................................... 2-3
2.1.4 Core Requirement #4: Conveyance System ............................................................................. 2-3
2.1.5 Core Requirements #5: Erosion and Sediment Control ........................................................... 2-3
2.1.6 Core Requirement #6: Maintenance and Operations .............................................................. 2-3
2.1.7 Core Requirement #7: Financial Guarantees and Liability ....................................................... 2-3
2.1.8 Core Requirement #8: Water Quality ...................................................................................... 2-5
2.1.9 Core Requirement #9: On-Site BMPs ....................................................................................... 2-6
2.2 Special Requirements ...................................................................................................................... 2-6
2.2.1 Special Requirement #1: Other Adopted Area Specific Requirements .................................... 2-6
2.2.2 Special Requirement #2: Flood Hazard Area Delineation ........................................................ 2-6
2.2.3 Special Requirement #3: Flood Protection Facilities ................................................................ 2-6
2.2.4 Special Requirement #4: Source Control ................................................................................. 2-6
2.2.5 Special Requirement #5: Oil Control ........................................................................................ 2-6
2.2.6 Special Requirement #6: Aquifer Protection Area ................................................................... 2-6
3. OFFSITE ANALYSIS ............................................................................................................................. 3-1
3.1 Resource Review .............................................................................................................................. 3-1
3.1.1 Sensitive Areas ......................................................................................................................... 3-1
3.2 Field Investigation ............................................................................................................................ 3-4
4. FLOW CONTROL AND WATER QUALITY DESIGN ............................................................................... 4-7
4.1 Hydraulic Analysis ............................................................................................................................ 4-7
4.1.1 Existing Conditions ................................................................................................................. 4-10
4.1.2 Upstream Conditions.............................................................................................................. 4-10
4.1.3 Developed Conditions ............................................................................................................ 4-12
4.2 Water Quality Treatment Analysis and Design .............................................................................. 4-19
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Core Design, Inc. TOWNS ON 12TH ii
5. CONVEYANCE SYSTEM ANALYSIS AND DESIGN ................................................................................. 5-1
6. SPECIAL REPORTS AND STUDIES ....................................................................................................... 6-1
7. OTHER PERMITS ................................................................................................................................ 7-1
8. ESC ANALYSIS AND DESIGN ............................................................................................................... 8-1
9. BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT ............................. 9-1
10. OPERATIONS AND MAINTENANCE .................................................................................................. 10-1
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1. PROJECT OVERVIEW
The proposed Towns on 12th project is located to the north of the intersection of NE 12th Street and NE
11th Place Renton, Washington within Section 4, Township 23 North, Range 5 East, W.M. See Vicinity
Map below.
The site is composed of seven parcels #042305-9063, #042305-9099, #042305-9067, #042305-9140,
#042305-9100, #042305-9101 and #032405-9247 with an area of approximately 6.55 acres. The site is
bordered by NE Sunset Blvd. (which is a major arterial) to the north, NE 12th Street (collector) to the
south, residential developed parcels to the west, and commercial developed parcels to the east.
The site has a high point in the middle of the site and slopes down in all directions ranging from 5-20%.
Proposed development of the property will include the construction of multiple townhomes, private
roads, utilities, and minor frontage improvements. All existing structures and hard surfaces will be
demolished and removed.
The subject project’s drainage facilities were designed using the guidelines and requirements
established in the 2017 City of Renton Surface Water Design Manual (RSWDM). Flow Control Duration
Standard (Matching Forested) and Enhanced Basic Water Quality Treatment are required for this
project.
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2. CONDITIONS AND REQUIREMENTS SUMMARY
The proposed project is classified as requiring “Full Drainage Review” per the 2017 RSWDM. Therefore,
all nine core requirements and six special requirements will be addressed per Section 1.2 and 1.3 of the
2017 RSWDM.
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2.1 Core Requirements
2.1.1 Core Requirement #1: Discharge at the Natural Location
The project discharges its drainage at the natural location which is to the City’s conveyance system
located along the south side of NE Sunset Blvd.
2.1.2 Core Requirement #2: Offsite Analysis
See Section 3 of this Report for the downstream analysis.
2.1.3 Core Requirement #3: Flow Control
The site falls within the City’s Flow Control Duration Standard (Matching Forested). See City’s Flow
Control Application Map on the following page. This flow control standard requires matching forested
conditions over the range of flows extending from 50% of 2-year up to the full 50-year flow AND
matches peaks for the 2- and 10-year return periods.
See Section 4 of this Report for details on the Flow Control Analysis.
2.1.4 Core Requirement #4: Conveyance System
This core requirement will be addressed during final design.
2.1.5 Core Requirements #5: Erosion and Sediment Control
This core requirement will be addressed during final design.
2.1.6 Core Requirement #6: Maintenance and Operations
This core requirement will be addressed during final design.
2.1.7 Core Requirement #7: Financial Guarantees and Liability
This core requirement will be addressed at the time the permit is issued.
DocuSign Envelope ID: CB3FEE37-E3FD-4E9A-BBDA-38822A5CC20E
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Flow Control Application Map
Reference 1-A
Date: 01/09/2014
Flow Control Standards
Peak Rate Flow Control Standard (Existing Site Conditions)
Flow Control Duration Standard (Existing Site Conditions)
Flow Control Duration Standard (Forested Conditions)
Flood Problem Flow
Unincorporated King County Flow Control Standards
Renton City Limits
Potential Annexation Area
PROJECT SITE
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2.1.8 Core Requirement #8: Water Quality
As the City of Renton does not have Sensitive Lake or Sphagnum Bog Water Quality Treatment Areas,
Basic Water Quality Treatment is the only other option available. As the proposed project is a
Multifamily Residential development, Enhanced Basic Water Quality Treatment is required.
See Section 4 of this Report for details on Water Quality Facility Sizing.
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2.1.9 Core Requirement #9: On-Site BMPs
See Section 4.1.2 of this Report for discussion on how this Core Requirement is addressed.
2.2 Special Requirements
2.2.1 Special Requirement #1: Other Adopted Area Specific Requirements
There are no known additional requirements for the subject project.
2.2.2 Special Requirement #2: Flood Hazard Area Delineation
Not applicable since the project does not contain nor is adjacent to a flood hazard area.
2.2.3 Special Requirement #3: Flood Protection Facilities
Not applicable since the project does not rely on an existing flood protection facility or plans to modify
or construct a new flood protection facility.
2.2.4 Special Requirement #4: Source Control
Not applicable since the project is not a commercial development.
2.2.5 Special Requirement #5: Oil Control
Not applicable since the project is not a high use site. The expected average daily traffic is less than 100
vehicles per 1,000 square feet of gross building area.
2.2.6 Special Requirement #6: Aquifer Protection Area
Not applicable since the project is not in an Aquifer Protection Area.
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3. OFFSITE ANALYSIS
3.1 Resource Review
The proposed project is located within the Lake Washington Cedar River Watershed.
3.1.1 Sensitive Areas
Renton GIS was reviewed for sensitive areas. The proposed project site falls within the following
sensitive areas: landslide and regulated slopes. The proposed project site does not fall within the
following sensitive areas: coal mines, erosion hazard, flood hazard, floodway, channel migration zone,
seismic hazard, regulated stream, or wellhead protection.
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According to the Renton GIS Map, there is a portion of the site along the north boundary which falls
within a landslide hazard area. See picture below.
Landslide Hazard (Per Renton GIS Data)
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According to the Renton GIS Map, there is a portion of the site along the north boundary which falls
within 15%-90% regulated slope. See picture below.
Regulated Slope: 15% to 90% Slope Area (Per Renton GIS Data)
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3.2 Field Investigation
A field investigation was completed on June 9, 2021.
Upstream Tributary Analysis
There is a neighborhood directly west of the project site. In this neighborhood there are three side roads
that are located to the northwest of the project boundary that point towards the site: NE 14th Place, NE
14th Court, and NE 14th Street.. The southern-most road (NE 14th Street) slopes east towards the site, but
has a mound and catch basin located at the low point of the road. This would prevent any runoff from
this road from entering the project site. The other two roads slope west away from the project site. We
will assume that the site’s western boundary acts as a high point for the purposes of the basin boundary.
The rest of the homes located to the south of these three side roads drain directly into the existing
detention pond located in this neighborhood. There is a storm system located in the backyard of these
homes that will collect all backyard drainage and direct it to the detention pond as well. We can assume
that this portion of the site’s western boundary is also a high point for the purposes of the basin
boundary.
There is additional upstream area to the site that is accounted for in the existing wetland located along
the west boundary of the site. The area from four existing homes to the south of the wetland, drains to
the wetland and discharges into the site.
Along the south property line lies NE 12th Street. No runoff from NE 12th Street will enter the project site
as there is an existing mound along the north edge of NE 12th Street that prevents any runoff from
entering into the site.
Downstream Drainage Complaints
Drainage complaints were researched within a quarter mile of the project site. City of Renton does not
list any current complaints along the project’s downstream route.
Onsite Drainage System Description
The site consists of seven connected parcels. The center of the project site contains a single-family
residence and shed. A dirt roadway creates a passage between the west and east portions of the site
which connects through the center of the site. There are two additional single-family homes in the
southern portion of the site. The remainder of the site is undeveloped consisting of thick forest cover.
The northwestern portion of the site contains a large meadow with thick grass cover. Large trees are
found in abundance throughout the project site. The entire site is located within the May Creek drainage
basin.
The topography of the entire site generally slopes to the north. Steep slopes are found along the
northern boundary of the parcel bordering NE Sunset Blvd. The site also contains steep slopes along the
eastern boundary of the project site. These slopes lead downhill eastward towards the adjacent
businesses on NE Sunset Blvd. These slopes lead to the existing stormwater collection system along the
southern border of NE Sunset Blvd. The meadow in the northwestern region of the map is a localized
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low point for site runoff. The slope is directed in a northeastern direction towards the adjacent road
from this point.
Downstream Drainage System Description
Runoff travels over the site via sheet flow over thick forested ground cover. All flow onsite is eventually
directed towards NE Sunset Blvd. which is located north of the site. An existing catch basin network
along the southern boundary of NE Sunset Blvd. serves to collect runoff and continue the flow eastward
(see downstream map). All the receiving catch basins north of site are located along the southern edge
of NE Sunset Blvd. All runoff is directed to the point where it is conveyed across the highway and then
directed northward into Honey Dew Creek. Honey Dew Creek flows northward and eventually joins May
Creek beyond the ¼ mile extent of the analysis. At this point the downstream analysis is terminated. See
downstream map for details.
Downstream Reach Description to a quarter mile
Pipe Material Pipe Diameter
(in)
Overall Length
(ft)
Cumulative Length
(ft)
Concrete 18 262 262
Concrete 18 55 317
Concrete 18 53 370
Unknown 18 47 417
Honey Dew Creek N/A 1,273 1,320
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4. FLOW CONTROL AND WATER QUALITY DESIGN
A flow control facility is proposed as the project is required to meet the City’s Flow Control Duration
Standard (Matching Forested). This flow control standard requires matching forested conditions over
the range of flows extending from 50% of 2-year up to the full 50-year flow and matching peaks for the
2- and 10-year return periods. A water quality treatment facility is proposed as the project is required to
provide enhanced basic water quality treatment as delineated in Section 4.2 of this Report.
4.1 Hydraulic Analysis
The drainage analysis was modeled using WWHM. Per the City of Renton Soil Survey, the site soil is
Alderwood (AgC), hydrologic soil group “C”, Till for modeling.
DocuSign Envelope ID: CB3FEE37-E3FD-4E9A-BBDA-38822A5CC20E
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114488tthhAAvveeSSEEWWMMeerrcceerrWWaayy115544tthhPPllSSEEEEddmmoonnddssAAvveeNNEEAAbbeerrddeeeennAAvveeNNEEWWeessttVVaalllleeyyHHwwyyEast Valley RdEast Valley Rd,§-405
,§-405
Reference 1-C
Renton City Limits
Potential Annexation Area
Groundwater Protection Area Boundary
Aquifer Protection Area Zone 1
Aquifer Protection Area Zone 1 Modified
Soil Type
AgB
AgC
AgD
AkF
AmB
AmC
An
BeC
BeD
Bh
Br
EvB
EvC
EvD
EwC
InA
InC
InD
KpB
KpC
KpD
Ma
Ng
Nk
No
Or
Os
OvC
OvD
PITS
Pc
Pk
Pu
Py
RdC
RdE
Re
Rh
Sh
Sk
Sm
So
Tu
Ur
W
Wo
Date: 01/09/2014
012
MilesμSoil Survey
PROJECT SITE
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4.1.1 Existing Conditions
See Existing/Upstream Conditions exhibit on the following pages.
The existing basin boundary area, 6.70 acres, will include the property area, 6.55 acre, plus the proposed
frontage improvement area along NE 12th Street, 0.15 acre. As part of the project, the City has
requested the existing sidewalk along NE Sunset Blvd. be relocated to create a planter strip. As the
project is simply moving the existing sidewalk, this sidewalk construction will not be considered as a
targeted impervious surface for the purpose of drainage design.
Some areas of the subject site discharge west offsite providing recharge to the existing offsite wetland.
During final design, an area will be designated to discharge to this offsite wetland. Drainage collected by
this wetland though, discharges back onto the project site and will be conveyed through the stormwater
flow control and treatment facilities.
The following information was used for generating flow frequencies.
EXISTING CONDITIONS Total Area = 6.70 acres
GROUND COVER AREA (acres)
Till-Forest 6.70
4.1.2 Upstream Conditions
See Existing/Upstream Conditions exhibit on the following pages.
The project site has two upstream areas. The first upstream area is located along the southern half of
the west boundary line of the site. This upstream area is tributary to the existing wetland located on
site. The second upstream area is located at the southwest corner of the site. This area is tributary to
the site.
Impervious coverage from all these areas were delineated through the use of aerial images at correct
scales to outline the impervious areas.
The following information was used for generating flow frequencies.
UPSTREAM CONDITIONS Total Area = 1.19 acres
GROUND COVER AREA (acres)
Till-Grass 0.78
Impervious 0.41
The below inputs into WWHM for the basin include both the existing area (6.70 acres) and the upstream
areas draining to the site (1.19 acres).
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DESIGNE N G I N E E R I N G P L A N N I N G S U R V E Y I N G12100 NE 195th St, Suite 300Bothell, Washington 98011425.885.7877 Fax 425.885.796321008DocuSign Envelope ID: CB3FEE37-E3FD-4E9A-BBDA-38822A5CC20E
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4.1.3 Developed Conditions
See Developed/Upstream Conditions exhibit on the following pages.
For preliminary design, the developed basin boundary area is equal to and the same as the existing basin
boundary area, 6.70 acres.
For the final design, some area swapping will be incorporated into the flow control and water quality
treatment design. Drainage along NE 12th Street will be collected and discharged to the existing
conveyance system along NE 12th Street. Modeling of upstream areas will be adjusted in final design to
account for the runoff from NE 12th Street which will not be collected by the proposed system.
Impervious areas for the site were calculated based on the proposed site plan per the project’s
designation as multi-family. The impervious areas are summarized in the table below. The site areas for
the upstream condition are provided in Section 4.1.2 of this report.
Credits received for Onsite BMPs are not considered for this preliminary design. Onsite BMP credits will
be reviewed and incorporated during final design.
DEVELOPED CONDITIONS
Total Area Impervious Area Pervious Area
Sidewalk 16,750 16,750 0
Road/Driveway 64,392 64,392 0
Roof 78,646 78,646 0
Grass 132,199 0 132,199
Total Area (SF) 291,987 159,788 132,199
Total Area (AC) 6.70 3.67 3.03
The inputs into WWHM for the basin include both the developed basin area (6.70 acres) and the
upstream areas draining to the site (1.19 acres).
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04230590630423059099042305906704230591400423059100DESIGNE N G I N E E R I N G P L A N N I N G S U R V E Y I N G12100 NE 195th St, Suite 300Bothell, Washington 98011425.885.7877 Fax 425.885.796321008DocuSign Envelope ID: CB3FEE37-E3FD-4E9A-BBDA-38822A5CC20E
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FLOW CONTROL FACILITY ANALYSIS
Flow control facilities have been designed using WWHM. Proposed vault dimensions are given below
along with WWHM generated modeling reports. The project will utilize a standard detention vault to
provide flow control. The required surface area of the vault is 7,392 square feet. Using the maximum
water surface of the 50-year storm (Elev. 405.82) as calculated in the vault overflow analysis below
under VAULT OVERFLOW ANALYSIS, along with the normal water surface elevation (Elev. 393.50), the
minimum required volume will be the surface area times the live storage depth, 7,392 square feet x
(405.82 – 393.50) = 91,069 cubic feet. The proposed detention vault will provide a volume of 95,234
cubic feet, exceeding the required volume, and therefore providing adequate flow control. The full
WWHM generated report is provided in Appendix A.
VAULT OVERFLOW ANALYSIS
The water surface elevations within the vault are conservatively calculated based on the equation below
as WWHM does not accurately calculate the water surface when the water surface starts to exceed the
riser elevation.
The primary overflow for the vault is the riser pipe on the control structure. The water surface elevation
above the riser for the 100-year developed flow is calculated assuming all orifices are plugged. The 100-
year, 15-minute return period storm for the developed tributary area is 5.82 cfs. See snip from WWHM
model below which shows the developed site undetained flows.
To pass the 100-year, 15-minute return period storm, 5.82 cfs, through a 36-inch overflow riser, 0.34
feet of head is required per the following equation:
= 9.739
/ 5.82 = 9.739 3 /
The primary overflow elevation, elevation 405.84, would therefore, be equal to the elevation of the top
of the riser, elevation 405.50, plus the amount of head required to pass the 100-year return period
storm, 0.34 feet. This primary overflow elevation will be utilized as the vault’s tailwater elevation for
sizing of the conveyance system during final design.
The 50-year maximum water surface for the vault is determined in the same way as the 100-year
overflow. The water surface elevation above the riser for the 50-year developed flow is calculated
assuming all orifices are plugged. The 50-year, 15-minute return period storm for the developed
tributary area is 5.18 cfs. See snip from WWHM model below which shows the developed site
undetained flows.
To pass the 50-year, 15-minute return period storm, 5.18 cfs, through a 36-inch overflow riser, 0.32 feet
of head is required per the following equation:
= 9.739
/ 5.18 = 9.739 3 /
The 50-year maximum water surface elevation, elevation 405.82, would therefore, be equal to the
elevation of the top of the riser, elevation 405.50, plus the amount of head required to pass the 100-
year return period storm, 0.32 feet.
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ON-SITE BMPs
Per Section 1.2.9.1 in the RSWDM, projects subject to Core Requirement #9 must apply flow control
BMPs to either supplement the flow mitigation provided by required flow control facilities or provide
flow mitigation where flow control facilities are not required. Flow control BMPs must be implemented
per the requirements and approach detailed in Sections 1.2.9.2 and 1.2.9.3 for individual lots and
subdivisions or road improvement projects, respectively. The Section applicable to this project is Section
1.2.9.2.
Per Section 1.2.9.2, projects on individual sites/lots, flow control BMPs must be selected and applied
according to the individual lot BMP requirements. The category of requirements applicable to the
subject project is the Large Lot BMP Requirements (for sites/lots >22,000 square feet).
1. The feasibility and applicability of full dispersion as detailed in Appendix C, Section C.2.1 must be
evaluated for all target impervious surfaces. If feasible and applicable, full dispersion must be
implemented as part of the proposed project. Typically, large lot full dispersion will be applicable
only in subdivisions where enough forest was preserved by tract, easement, or covenant to meet
the minimum requirements for full dispersion in Appendix C, Section C.2.1.1
Full Dispersion is not feasible due to being unable to meet the minimum required flow path with the
appropriate slopes.
2. Where full dispersion of target impervious roof areas is not feasible or applicable, or will cause
flooding or erosion impacts, the feasibility and applicability of full infiltration as detailed in Appendix
C, Section C.2.2 must be evaluated (note, this will require a soils report for the site/lot). If feasible
and applicable, full infiltration of roof runoff must be implemented as part of the proposed project.
Full Infiltration is not feasible due to existing onsite non-infiltrating till soils.
3. All target impervious surfaces not mitigated by Requirements 1 and 2 above, must be mitigated to
the maximum extent feasible using one or more BMPs from the following list. Use of a given BMP is
subject to evaluation of its feasibility and applicability as detailed in Appendix C. Feasible BMPs are
required to be implemented. The BMPs listed below may be located anywhere on the site/lot
subject to the limitations and design specifications for each BMP. These BMPs must be
implemented as part of the proposed project.
• Full Infiltration per Appendix C, Section C.2.2, or per Section 5.2, whichever is applicable
Full Infiltration is not feasible due to existing onsite non-infiltrating till soils
• Limited Infiltration per Appendix C, Section C.2.3,
Opportunities for Limited Infiltration will be further reviewed during final design. At this time, limited
infiltration is not feasible per the project’s geotechnical engineer. Per the Geotechnical Report
prepared by Terra Associates, Inc, dated 8/5/21, soils observed on site are not suitable for Flow
Control BMPs due to the presence of weathered glacial till at shallow depths.
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• Bioretention per Appendix C, Section C.2.6, sized as follows:
o SeaTac regional scale factor equals 1.0: In till soils, provide bioretention volume based on 0.6
inches of equivalent storage depth; in outwash soils provide bioretention volume based on 0.1
inches of equivalent storage depth,
o SeaTac regional scale factor greater than 1.0: In till soils, provide bioretention volume based on 0.8
inches of equivalent storage depth; in outwash soils, provide bioretention volume based on 0.4
inches of equivalent storage depth,
Opportunities for Bioretention will be further reviewed during final design. Bioretention is not feasible
per the project’s geotechnical engineer. Per the Geotechnical Report prepared by Terra Associates,
Inc, dated 8/5/21, soils observed on site are not suitable for Flow Control BMPs due to the presence of
weathered glacial till at shallow depths.
• Permeable Pavement per Appendix C, Section C.2.7
Opportunities for Permeable Pavement will be further reviewed during final design. Permeable
Pavement is not feasible per the project’s geotechnical engineer. Per the Geotechnical Report
prepared by Terra Associates, Inc, dated 8/5/21, soils observed on site are not suitable for Flow
Control BMPs due to the presence of weathered glacial till at shallow depths.
4. All target impervious surfaces not mitigated by Requirements 1, 2 and 3 above, must be mitigated to
the maximum extent feasible using the Basic Dispersion BMP described below. Use of Basic
Dispersion is subject to evaluation of its feasibility and applicability as detailed in Appendix C.
Feasible BMPs are required to be implemented. Basic Dispersion BMPs may be located anywhere on
the site/lot subject to the limitations and design specifications cited in Appendix C. The BMP must
be implemented as part of the proposed project.
• Basic Dispersion per Appendix C, Section C.2.4,
Basic dispersion is not feasible due to being unable to meet the minimum required flow path with the
appropriate slopes and the steep slope adjacent to the site.
5. BMPs must be implemented, at minimum, for impervious area amounts defined as follows.
• For projects that will result in an impervious surface coverage on the buildable portion of the
site/lot of less than 45%, on-site BMPs must be applied to 50% of target impervious surfaces.
• For projects that will result in an impervious surface coverage 45-65% on the buildable portion
of the site/lot, on-site BMPs must be applied to 50% of target impervious surfaces reduced by
1.5% for each 1% of impervious surface coverage above 45% (e.g., impervious coverage of 55%
results in a requirement of on-site BMPs applied to 35% of target impervious surfaces).
• For projects that will result in an impervious surface coverage greater than 65% on the buildable
portion of the site/lot, on-site BMPs must be applied to 20% of the target impervious surfaces or
to an impervious area equal to at least 10% of the site/lot, whichever is less.
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The buildable portion of the site/lot is the total area of the site/lot minus any critical areas and
minus 200 ft. buffer areas from a steep slope hazard, landslide hazard, or erosion hazard area. If
these minimum areas are not mitigated using feasible BMPs from Requirements 1, 2, 3, and 4
above, one or more BMPs from the following list are required to be implemented to achieve
compliance. These BMPs must be implemented as part of the proposed project
• Reduced Impervious Surface Credit per Appendix C, Section C.2.9,
• Native Growth Retention Credit per Appendix C, Section C.2.10.
• Tree Retention Credit per Appendix C, Section C.2.14
The impervious area requiring mitigation is equal to 10% of the Site Area. The Site Area (285,453
square feet) is defined as the property area (289,606 square feet) less the ROW dedication area (4,153
square feet). The site includes buffer areas which totals to 19.268 square feet. This leaves the
buildable area at 266,185 square feet, with the proposed impervious of 163,622 square feet
The impervious area requiring mitigation is, therefore, equal to 10% of 266,185 square feet, or 26,619
square feet.
Opportunities for Reduced Impervious Surface Credit will be reviewed during final design. The only
feasible options possible under this option are open grid decking over pervious surface and wheel strip
driveways.
Since the proposed project will develop the entire site with the exception of sensitive areas and
associated buffers, a Native Growth Retention Credit is not feasible.
Tree Retention Credits will be applied during final design.
6. The soil moisture holding capacity of new pervious surfaces (target pervious surfaces) must be
protected in accordance with the soil amendment BMP as detailed in Appendix C, Section C.2.13.
Soil amendment will be incorporated for disturbed areas not covered with hard surfaces.
7. Any proposed connection of roof downspouts to the local drainage system must be via a perforated
pipe connection as detailed in Appendix C, Section C.2.11.
All proposed connections to the local drainage system will be provided via a perforated pipe
connection.
Exhibit 11
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4.2 Water Quality Treatment Analysis and Design
Per Core Requirement #8: Water Quality, the project is required to provide a water quality system to
treat stormwater runoff from pollution-generating surfaces. The site is located within an Enhanced Basic
Water Quality Area and is therefore required to implement a system from the Enhanced Basic Water
Quality Menu described in Section 6.1.2 of the 2017 RSWDM.
The project proposes to implement a Biopod proprietary water quality media filter manufactured by
Oldcastle as per Enhanced Basic Option 5 in the 2017 RSWDM. The Biopod filter has General Use Level
Designation (GULD) Approval from the Department of Ecology. Water Quality calculations are shown
below.
The Biopod system is located downstream of the vault, therefore the design flow for sizing of the system
is the 2-year flow rate from the vault. The flow rate is 0.2635 as provided from WWHM.
Using this table provided by Oldcastle, the 8’x16’ Biopod has sufficient capacity for the flow of 0.2635 cfs
out of the vault.
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5. CONVEYANCE SYSTEM ANALYSIS AND DESIGN
Conveyance system analysis and design will be addressed during final design.
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6. SPECIAL REPORTS AND STUDIES
The following reports and assessments are provided for reference and informational purposes only.
Core Design takes no responsibility or liability for these reports, assessments, or designs as they were
not completed under the direct supervision of Core Design.
• Geotechnical Report by Terra Associates, Inc, dated 8/5/21
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7. OTHER PERMITS
No other permits relevant to this Preliminary TIR are known to be required at this time.
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8. ESC ANALYSIS AND DESIGN
The ESC analysis and design will be addressed during final design.
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9. BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF
COVENANT
The bond quantities, facility summary, and declaration of covenant will be addressed during final design.
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10. OPERATIONS AND MAINTENANCE
The operations and maintenance manual will be addressed during final design.
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Appendix A
WWHM Report
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WWHM2012
PROJECT REPORT
___________________________________________________________________
Project Name: New Vault
Site Name:
Site Address:
City :
Report Date: 4/11/2022
Gage : Seatac
Data Start : 1948/10/01
Data End : 2009/09/30
Precip Scale: 1.17
Version Date: 2021/08/18
Version : 4.2.18
___________________________________________________________________
Low Flow Threshold for POC 1 : 50 Percent of the 2 Year
___________________________________________________________________
High Flow Threshold for POC 1: 50 year
___________________________________________________________________
PREDEVELOPED LAND USE
Name : Basin 1
Bypass: No
GroundWater: No
Pervious Land Use acre
C, Forest, Mod 6.7
C, Lawn, Mod .78
Pervious Total 7.48
Impervious Land Use acre
ROOF TOPS FLAT 0.41
Impervious Total 0.41
Basin Total 7.89
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
MITIGATED LAND USE
Name : Basin 1
Bypass: No
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GroundWater: No
Pervious Land Use acre
C, Lawn, Mod 3.81
Pervious Total 3.81
Impervious Land Use acre
ROOF TOPS FLAT 4.08
Impervious Total 4.08
Basin Total 7.89
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
Vault 1 Vault 1
___________________________________________________________________
Name : Vault 1
Width : 84 ft.
Length : 88 ft.
Depth: 13 ft.
Discharge Structure
Riser Height: 12 ft.
Riser Diameter: 18 in.
Orifice 1 Diameter: 2 in. Elevation: 0 ft.
Orifice 2 Diameter: 1.5 in. Elevation: 7.2 ft.
Orifice 3 Diameter: 2.25 in. Elevation: 10.5 ft.
Element Flows To:
Outlet 1 Outlet 2
___________________________________________________________________
Vault Hydraulic Table
Stage(feet) Area(ac.) Volume(ac-ft.) Discharge(cfs) Infilt(cfs)
0.0000 0.169 0.000 0.000 0.000
0.1444 0.169 0.024 0.041 0.000
0.2889 0.169 0.049 0.058 0.000
0.4333 0.169 0.073 0.071 0.000
0.5778 0.169 0.098 0.082 0.000
0.7222 0.169 0.122 0.092 0.000
0.8667 0.169 0.147 0.101 0.000
1.0111 0.169 0.171 0.109 0.000
1.1556 0.169 0.196 0.116 0.000
1.3000 0.169 0.220 0.123 0.000
1.4444 0.169 0.245 0.130 0.000
1.5889 0.169 0.269 0.136 0.000
1.7333 0.169 0.294 0.142 0.000
1.8778 0.169 0.318 0.148 0.000
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2.0222 0.169 0.343 0.154 0.000
2.1667 0.169 0.367 0.159 0.000
2.3111 0.169 0.392 0.165 0.000
2.4556 0.169 0.416 0.170 0.000
2.6000 0.169 0.441 0.175 0.000
2.7444 0.169 0.465 0.179 0.000
2.8889 0.169 0.490 0.184 0.000
3.0333 0.169 0.514 0.189 0.000
3.1778 0.169 0.539 0.193 0.000
3.3222 0.169 0.563 0.197 0.000
3.4667 0.169 0.588 0.202 0.000
3.6111 0.169 0.612 0.206 0.000
3.7556 0.169 0.637 0.210 0.000
3.9000 0.169 0.661 0.214 0.000
4.0444 0.169 0.686 0.218 0.000
4.1889 0.169 0.710 0.222 0.000
4.3333 0.169 0.735 0.226 0.000
4.4778 0.169 0.759 0.229 0.000
4.6222 0.169 0.784 0.233 0.000
4.7667 0.169 0.808 0.237 0.000
4.9111 0.169 0.833 0.240 0.000
5.0556 0.169 0.857 0.244 0.000
5.2000 0.169 0.882 0.247 0.000
5.3444 0.169 0.906 0.250 0.000
5.4889 0.169 0.931 0.254 0.000
5.6333 0.169 0.956 0.257 0.000
5.7778 0.169 0.980 0.260 0.000
5.9222 0.169 1.005 0.264 0.000
6.0667 0.169 1.029 0.267 0.000
6.2111 0.169 1.054 0.270 0.000
6.3556 0.169 1.078 0.273 0.000
6.5000 0.169 1.103 0.276 0.000
6.6444 0.169 1.127 0.279 0.000
6.7889 0.169 1.152 0.282 0.000
6.9333 0.169 1.176 0.285 0.000
7.0778 0.169 1.201 0.288 0.000
7.2222 0.169 1.225 0.300 0.000
7.3667 0.169 1.250 0.319 0.000
7.5111 0.169 1.274 0.331 0.000
7.6556 0.169 1.299 0.341 0.000
7.8000 0.169 1.323 0.350 0.000
7.9444 0.169 1.348 0.358 0.000
8.0889 0.169 1.372 0.366 0.000
8.2333 0.169 1.397 0.373 0.000
8.3778 0.169 1.421 0.380 0.000
8.5222 0.169 1.446 0.387 0.000
8.6667 0.169 1.470 0.393 0.000
8.8111 0.169 1.495 0.399 0.000
8.9556 0.169 1.519 0.405 0.000
9.1000 0.169 1.544 0.411 0.000
9.2444 0.169 1.568 0.417 0.000
9.3889 0.169 1.593 0.422 0.000
9.5333 0.169 1.617 0.428 0.000
9.6778 0.169 1.642 0.433 0.000
9.8222 0.169 1.666 0.439 0.000
9.9667 0.169 1.691 0.444 0.000
10.111 0.169 1.715 0.449 0.000
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10.256 0.169 1.740 0.454 0.000
10.400 0.169 1.764 0.459 0.000
10.544 0.169 1.789 0.493 0.000
10.689 0.169 1.813 0.528 0.000
10.833 0.169 1.838 0.553 0.000
10.978 0.169 1.862 0.573 0.000
11.122 0.169 1.887 0.591 0.000
11.267 0.169 1.911 0.607 0.000
11.411 0.169 1.936 0.623 0.000
11.556 0.169 1.960 0.637 0.000
11.700 0.169 1.985 0.651 0.000
11.844 0.169 2.010 0.664 0.000
11.989 0.169 2.034 0.677 0.000
12.133 0.169 2.059 1.460 0.000
12.278 0.169 2.083 2.949 0.000
12.422 0.169 2.108 4.584 0.000
12.567 0.169 2.132 5.902 0.000
12.711 0.169 2.157 6.669 0.000
12.856 0.169 2.181 7.300 0.000
13.000 0.169 2.206 7.842 0.000
13.144 0.169 2.230 8.347 0.000
13.289 0.000 0.000 8.821 0.000
___________________________________________________________________
___________________________________________________________________
ANALYSIS RESULTS
Stream Protection Duration
___________________________________________________________________
Predeveloped Landuse Totals for POC #1
Total Pervious Area:7.48
Total Impervious Area:0.41
___________________________________________________________________
Mitigated Landuse Totals for POC #1
Total Pervious Area:3.81
Total Impervious Area:4.08
___________________________________________________________________
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.525386
5 year 0.821257
10 year 1.052694
25 year 1.387507
50 year 1.669031
100 year 1.97922
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.261109
5 year 0.360508
10 year 0.437405
25 year 0.548134
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Core Design, Inc. TOWNS ON 12TH Page 10-8
50 year 0.641141
100 year 0.743756
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Stream Protection Duration
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.876 0.219
1950 0.818 0.262
1951 0.717 0.499
1952 0.343 0.188
1953 0.259 0.201
1954 0.423 0.243
1955 0.510 0.263
1956 0.536 0.277
1957 0.614 0.237
1958 0.369 0.243
1959 0.342 0.219
1960 0.714 0.431
1961 0.457 0.234
1962 0.231 0.177
1963 0.466 0.240
1964 0.492 0.227
1965 0.531 0.248
1966 0.348 0.215
1967 0.885 0.255
1968 0.542 0.216
1969 0.455 0.217
1970 0.485 0.224
1971 0.566 0.259
1972 0.724 0.353
1973 0.315 0.226
1974 0.563 0.243
1975 0.677 0.256
1976 0.489 0.250
1977 0.329 0.183
1978 0.419 0.235
1979 0.330 0.177
1980 1.266 0.399
1981 0.445 0.209
1982 0.948 0.405
1983 0.448 0.256
1984 0.324 0.195
1985 0.318 0.216
1986 0.655 0.352
1987 0.651 0.392
1988 0.262 0.205
1989 0.214 0.195
1990 2.029 0.436
1991 1.158 0.438
1992 0.437 0.231
1993 0.314 0.216
1994 0.193 0.164
1995 0.423 0.264
1996 1.096 0.512
1997 0.732 0.455
1998 0.457 0.219
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1999 1.385 0.356
2000 0.485 0.256
2001 0.275 0.177
2002 0.674 0.374
2003 0.849 0.209
2004 0.851 0.628
2005 0.552 0.258
2006 0.534 0.245
2007 1.667 0.845
2008 1.440 0.669
2009 0.771 0.333
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Stream Protection Duration
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 2.0286 0.8446
2 1.6669 0.6690
3 1.4402 0.6278
4 1.3853 0.5122
5 1.2656 0.4989
6 1.1576 0.4549
7 1.0956 0.4379
8 0.9482 0.4363
9 0.8848 0.4311
10 0.8764 0.4050
11 0.8514 0.3986
12 0.8486 0.3918
13 0.8184 0.3737
14 0.7713 0.3557
15 0.7317 0.3526
16 0.7235 0.3516
17 0.7174 0.3333
18 0.7143 0.2774
19 0.6766 0.2643
20 0.6735 0.2633
21 0.6552 0.2620
22 0.6505 0.2588
23 0.6145 0.2580
24 0.5656 0.2565
25 0.5627 0.2562
26 0.5523 0.2559
27 0.5419 0.2552
28 0.5357 0.2505
29 0.5336 0.2481
30 0.5308 0.2450
31 0.5098 0.2430
32 0.4917 0.2430
33 0.4887 0.2428
34 0.4854 0.2404
35 0.4853 0.2372
36 0.4656 0.2350
37 0.4573 0.2335
38 0.4565 0.2311
39 0.4550 0.2266
40 0.4475 0.2265
41 0.4448 0.2238
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42 0.4373 0.2191
43 0.4234 0.2191
44 0.4225 0.2189
45 0.4187 0.2168
46 0.3692 0.2164
47 0.3484 0.2162
48 0.3434 0.2160
49 0.3425 0.2149
50 0.3300 0.2093
51 0.3294 0.2085
52 0.3237 0.2049
53 0.3183 0.2013
54 0.3153 0.1948
55 0.3139 0.1948
56 0.2746 0.1884
57 0.2622 0.1830
58 0.2591 0.1772
59 0.2306 0.1771
60 0.2144 0.1771
61 0.1930 0.1642
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Stream Protection Duration
POC #1
The Facility PASSED
The Facility PASSED.
Flow(cfs) Predev Mit Percentage Pass/Fail
0.2627 5950 5805 97 Pass
0.2769 5159 4472 86 Pass
0.2911 4436 3328 75 Pass
0.3053 3882 3104 79 Pass
0.3195 3364 2911 86 Pass
0.3337 2922 2588 88 Pass
0.3479 2545 2271 89 Pass
0.3621 2199 1931 87 Pass
0.3763 1948 1655 84 Pass
0.3905 1706 1434 84 Pass
0.4047 1501 1175 78 Pass
0.4190 1308 923 70 Pass
0.4332 1167 591 50 Pass
0.4474 1025 415 40 Pass
0.4616 911 302 33 Pass
0.4758 819 283 34 Pass
0.4900 719 257 35 Pass
0.5042 608 231 37 Pass
0.5184 527 218 41 Pass
0.5326 455 205 45 Pass
0.5468 396 190 47 Pass
0.5610 341 171 50 Pass
0.5752 293 145 49 Pass
0.5894 255 127 49 Pass
0.6036 217 109 50 Pass
0.6178 193 92 47 Pass
0.6320 171 64 37 Pass
0.6462 143 53 37 Pass
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0.6604 126 34 26 Pass
0.6747 112 13 11 Pass
0.6889 97 9 9 Pass
0.7031 85 6 7 Pass
0.7173 78 5 6 Pass
0.7315 63 4 6 Pass
0.7457 58 4 6 Pass
0.7599 55 4 7 Pass
0.7741 50 2 4 Pass
0.7883 48 2 4 Pass
0.8025 43 2 4 Pass
0.8167 41 2 4 Pass
0.8309 34 2 5 Pass
0.8451 33 0 0 Pass
0.8593 28 0 0 Pass
0.8735 27 0 0 Pass
0.8877 24 0 0 Pass
0.9019 24 0 0 Pass
0.9161 23 0 0 Pass
0.9303 22 0 0 Pass
0.9446 20 0 0 Pass
0.9588 19 0 0 Pass
0.9730 19 0 0 Pass
0.9872 15 0 0 Pass
1.0014 14 0 0 Pass
1.0156 13 0 0 Pass
1.0298 13 0 0 Pass
1.0440 13 0 0 Pass
1.0582 13 0 0 Pass
1.0724 13 0 0 Pass
1.0866 13 0 0 Pass
1.1008 11 0 0 Pass
1.1150 10 0 0 Pass
1.1292 10 0 0 Pass
1.1434 9 0 0 Pass
1.1576 9 0 0 Pass
1.1718 8 0 0 Pass
1.1860 8 0 0 Pass
1.2003 8 0 0 Pass
1.2145 8 0 0 Pass
1.2287 8 0 0 Pass
1.2429 8 0 0 Pass
1.2571 8 0 0 Pass
1.2713 6 0 0 Pass
1.2855 6 0 0 Pass
1.2997 6 0 0 Pass
1.3139 6 0 0 Pass
1.3281 6 0 0 Pass
1.3423 6 0 0 Pass
1.3565 6 0 0 Pass
1.3707 6 0 0 Pass
1.3849 6 0 0 Pass
1.3991 5 0 0 Pass
1.4133 5 0 0 Pass
1.4275 5 0 0 Pass
1.4417 4 0 0 Pass
1.4559 4 0 0 Pass
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1.4702 4 0 0 Pass
1.4844 4 0 0 Pass
1.4986 3 0 0 Pass
1.5128 3 0 0 Pass
1.5270 3 0 0 Pass
1.5412 3 0 0 Pass
1.5554 2 0 0 Pass
1.5696 2 0 0 Pass
1.5838 2 0 0 Pass
1.5980 2 0 0 Pass
1.6122 2 0 0 Pass
1.6264 2 0 0 Pass
1.6406 2 0 0 Pass
1.6548 2 0 0 Pass
1.6690 1 0 0 Pass
_____________________________________________________
___________________________________________________________________
Water Quality BMP Flow and Volume for POC #1
On-line facility volume: 0.4133 acre-feet
On-line facility target flow: 0.2116 cfs.
Adjusted for 15 min: 0.2116 cfs.
Off-line facility target flow: 0.1323 cfs.
Adjusted for 15 min: 0.1323 cfs.
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LID Report
LID Technique Used for Total Volume Volume Infiltration Cumulative
Percent Water Quality Percent Comment
Treatment? Needs Through Volume Volume
Volume Water Quality
Treatment Facility (ac-ft.) Infiltration
Infiltrated Treated
(ac-ft) (ac-ft) Credit
Vault 1 POC N 1066.13 N
0.00
Total Volume Infiltrated 1066.13 0.00 0.00
0.00 0.00 0% No Treat. Credit
Compliance with LID Standard 8
Duration Analysis Result = Failed
___________________________________________________________________
Perlnd and Implnd Changes
No changes have been made.
___________________________________________________________________
This program and accompanying documentation are provided 'as-is' without warranty of any kind.
The entire risk regarding the performance and results of this program is assumed by End User.
Clear Creek Solutions Inc. and the governmental licensee or sublicensees disclaim all warranties,
either expressed or implied, including but not limited to implied warranties of program and
accompanying documentation. In no event shall Clear Creek Solutions Inc. be liable for any
damages whatsoever (including without limitation to damages for loss of business profits, loss of
business information, business interruption, and the like) arising out of the use of, or
inability to use this program even if Clear Creek Solutions Inc. or their authorized
representatives have been advised of the possibility of such damages. Software Copyright © by :
Clear Creek Solutions, Inc. 2005-2022; All Rights Reserved.
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Appendix B
Special Reports
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Insert reports referenced in section 6
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