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HomeMy WebLinkAboutTIR-4229
Brotherton Dealership
Dealership Construction and Expansion
Technical
Information Report
Prepared for:
Brotherton Cadillac
215 SW 12th Street
Renton, WA 98057
Contact: Brad Brotherton
Phone: (425) 336-1089
Prepared by:
Sitts & Hill Engineers, Inc.
4815 Center Street
Tacoma, Washington 98409
Contact: Don Davis, P.E.
Phone: (253) 474-9449
July 2022
Revised: March 2023
S&H Job Number 19,480
DEVELOPMENT ENGINEERING
NJanders 05/08/2023
SURFACE WATER UTILITY
JFarah 05/08/2023
Brotherton Dealership
Dealership Construction and Expansion
Technical Information Report
Prepared for:
Brotherton Cadillac
215 SW 12th Street
Renton, WA 98057
Contact: Brad Brotherton
Phone: (425) 336-1089
Prepared by:
Sitts & Hill Engineers, Inc.
4815 Center Street
Tacoma, Washington 98409
Contact: Don Davis, P.E.
Phone: (253) 474-9449
IN COMPLIANCE WITH CITY OF RENTON
STANDARDS
July 2022
Revised: March 2023 S&H Job Number 19,480
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
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TABLE OF CONTENTS
1.0 PROJECT OVERVIEW ............................................................................................................... 4
1.1 Scope ................................................................................................................................................................ 4
1.2 Existing Conditions ........................................................................................................................................ 5
1.3 Proposed Conditions ..................................................................................................................................... 7
2.0 Conditions and Requirements Summary ............................................................................. 10
2.1 Discussion of Core and Special Requirements ........................................................................................ 10
2.1.1 Core Requirement #1: Discharge at the Natural Location .............................................................. 10
2.1.2 Core Requirement #2: Off-site Analysis ............................................................................................ 10
2.1.3 Core Requirement #3: Flow Control ................................................................................................... 10
2.1.4 Core Requirement #4: Conveyance System ..................................................................................... 11
2.1.5 Core Requirement #5: Erosion and Sediment Control .................................................................... 11
2.1.6 Core Requirement #6: Maintenance and Operations ...................................................................... 11
2.1.7 Core Requirement #7: Financial Guarantees and Liability ............................................................. 11
2.1.8 Core Requirement #8: Water Quality ................................................................................................. 11
2.1.9 Core Requirement #9: On-site BMPs ................................................................................................. 11
2.1.10 Special Requirement #1: Other Adopted Area-Specific Requirements ...................................... 13
2.1.11 Special Requirement #2: Flood Hazard Area Delineation ............................................................ 13
2.1.12 Special Requirement #3: Flood Protection Facilities ..................................................................... 13
2.1.13 Special Requirement #4: Source Control ........................................................................................ 13
2.1.14 Special Requirement #5: Oil Control ................................................................................................ 14
2.1.15 Special Requirement #6: Aquifer Protection Areas ....................................................................... 14
3.0 OFF-SITE ANALYSIS ............................................................................................................... 19
3.1 Define and Map the Study Area ................................................................................................................ 19
3.2 Resource Review .......................................................................................................................................... 25
3.3 Field Inspection ............................................................................................................................................ 25
3.4 Drainage System Description and Problem Descriptions ..................................................................... 25
3.5 Mitigation of Existing or Potential Problems ......................................................................................... 26
4.0 FLOW CONTROL, LID, AND WATER QUALITY FACILITY ANALYSIS AND DESIGN ..... 27
4.1 Existing Site Hydrology ............................................................................................................................... 27
4.2 Developed Site Hydrology ......................................................................................................................... 27
4.3 Performance Standards .............................................................................................................................. 27
4.4 Flow Control System ................................................................................................................................... 28
4.4.1 Flow Control Exemptions Check ......................................................................................................... 28
4.4.2 Flow Control Area .................................................................................................................................. 28
4.4.3 Flow Control Area Requirements and Exceptions ........................................................................... 28
4.4.4 Identify Applicable Flow Control BMPs per Core Requirement #9 ................................................ 28
4.5 Water Quality ............................................................................................................................................... 29
5.0 CONVEYANCE SYSTEM ANALYSIS AND DESIGN ............................................................. 31
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6.0 SPECIAL REPORTS AND STUDIES ...................................................................................... 33
7.0 OTHER PERMITS ..................................................................................................................... 34
8.0 CSWPPP ANALYSIS AND DESIGN ....................................................................................... 35
9.0 BOND QUANTITIES and R/D FACILITY SUMMARIES ........................................................ 36
9.1 Bond Quantities ........................................................................................................................................... 36
9.2 Facility Summaries ....................................................................................................................................... 36
10.0 OPERATIONS AND MAINTENANCE MANUAL .................................................................. 37
10.1 Purpose ....................................................................................................................................................... 37
10.2 Permanent Facilities Description ............................................................................................................ 37
10.3 Discussion of Maintenance ...................................................................................................................... 37
10.4 Maintenance Frequency ........................................................................................................................... 38
10.5 Annual Cost Estimate ................................................................................................................................ 38
TABLE OF APPENDICES
A.1 TIR Worksheet ........................................................................................................................ 41
A.2 Bond Quantity Worksheet ..................................................................................................... 48
A.3 Existing and Proposed Surface Coverage Exhibits .......................................................... 49
A.4 Site Historical Aerial Photography ...................................................................................... 54
A.5 Stormwater Engineering Calculations ................................................................................ 62
A.6 Geotechnical Engineering Report........................................................................................ 91
A.7 WWHM Reports ...................................................................................................................... 92
A.8 SSA Reports.......................................................................................................................... 123
A.9 Water Quality GULDs ........................................................................................................... 143
A.10 Flygt NP 3085 SH Technical Information ........................................................................ 160
TABLE OF FIGURES
Figure 1 – Site Location Map – Proposed Building ...................................................................................... 5
Figure 2 – Site Location Map – Proposed Addition ...................................................................................... 6
Figure 3 – Drainage Review Flow Chart – Proposed Building ................................................................. 15
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Figure 4 – Drainage Review Flow Chart – Proposed Addition ................................................................. 16
Figure 5 – FEMA Map – Proposed Building ................................................................................................ 17
Figure 6 – FEMA Map – Proposed Addition ................................................................................................ 18
Figure 7 - Downstream Flow Path – Proposed Building ........................................................................... 19
Figure 8 – Downstream Flow Path – Proposed Addition .......................................................................... 20
Figure 9 – Topographic Survey ..................................................................................................................... 24
Figure 10- City of Renton Flow Control Application Map .......................................................................... 30
Figure 11 - WWHM Stormfall for the Eastern BioPod................................................................................ 31
Figure 12 - WWHM Stormfall Tributary to Western BioPod ...................................................................... 32
Figure 13 – TIR Worksheet ........................................................................................................................... 47
Figure 14 - Predeveloped conditions for the Cadillac site used for Water Quality ................................ 62
Figure 15 - Developed conditions for the Cadillac site used for Water Quality ..................................... 63
Figure 16 – WWHM 2012 Flow Frequency calculations for the Cadillac site ........................................ 64
Figure 17 - WWHM 2012 Water Quality calculations for the Cadillac site ............................................. 65
Figure 18 - Predeveloped conditions for the Buick-GMC site used for Water Quality .......................... 66
Figure 19 - Developed conditions for the Buick-GMC site used for Water Quality ............................... 66
Figure 20 - WWHM 2012 Flow Frequency calculations for the Buick-GMC site ................................... 68
Figure 21 - WWHM 2012 Water Quality calculations for the Buick-GMC site ....................................... 68
Figure 22 - WWHM 2012 Flow Frequency Calculations for the combined project area ...................... 69
Figure 23 - Pump Operation Envelope......................................................................................................... 74
Figure 24 - Minor Loss Nomograph .............................................................................................................. 75
Figure 25 – Minimum Pump Curve Head (ft) vs Flow (cfs) ....................................................................... 76
Figure 26 - Difference between upper and lower pump curve head (ft) vs flow (cfs) ........................... 77
Figure 27 - Storage curve for 5 StormCapture units .................................................................................. 78
Figure 28 - 2-year Total System Inflow, Pump Flow, and System Outflow vs Time ............................. 79
Figure 29 – 2-year Water Depth and Storage Volume for StormCapture units and lift station ........... 80
Figure 30 - 10-year Storage Depth, Pump Flow, and System Outflow vs Time .................................... 81
Figure 31 - 10-year Water Depth and Storage Volume for StormCapture units and lift station .......... 82
Figure 32 - 100-year Storage Depth, Pump Flow, and System Outflow vs Time .................................. 83
Figure 33 – 100-year Water Depth and Storage Volume for StormCapture units and lift station ....... 84
TABLE OF TABLES
Table 1. Existing and Developed Condition Description – Proposed Building ........................................ 8
Table 2. Existing and Developed Condition Description – Proposed Addition ........................................ 9
Table 3. Pump Total Dynamic Head vs Flow (gpm) .................................................................................. 73
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1.0 PROJECT OVERVIEW
1.1 Scope
This Technical Information Report (TIR) addresses improvements associated with the proposed
building located at 201 SW 12th Street, Renton, WA (Parcel Nos. 3340402780, 3340402805,
3340402880, and 3340402925) and the proposed building addition at 215 SW 12th Steet,
Renton, WA (Parcel Nos. 3340402820, 3340402850, 3340402860, 3340402870, and
3340402885). Please see Figure 1 for the Site Location Map of the proposed building and Figure
2 for the Site Location Map of the proposed building addition. This construction is proposed to
serve as a stand-alone Cadillac automotive dealership for Brotherton Cadillac and additional
shop space for the existing Brotherton Buick-GMC dealership. The new dealership will replace
existing residential development with driveway connections to SW 12th Street and the
neighboring Brotherton Buick-GMC dealership via the SW 13th Street former right of way. The
addition will replace part of the existing parking lot without changing the number or locations
of entrances.
This Technical Information Report has been prepared in accordance with the 2017 City of
Renton Stormwater Design Manual (SWDM). A copy of the TIR Worksheet, which provides basic
information about the scope of this project, is included with this report in Appendix A.1.
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Figure 1 – Site Location Map – Proposed Building
1.2 Existing Conditions
The subject sites are located on nine parcels, zoned as Commercial Arterial (CA), with a
combined area of 2.84 acres of developed land. The sites, as depicted on the topographical
survey, are relatively flat. The original dealership was graded with depressions to direct
stormwater into on-site catch basins. The privately owned stormwater system extends
upstream to the east, collecting stormwater runoff from two more parking areas to the east
and north of the subject property before discharging into the system of the Brotherton
automotive dealership.
The existing sites consist of residential development, a Cadillac, Buick, and GMC dealership, and
associated parking. Based on historical aerial photographs and the King County Assessor’s
Website, the site appeared to be residential housing as early as 1951. One of the residential
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lots was emptied between May of 2013 and July of 2014. Another was replaced with parking
between May of 2017 and May of 2018 and replaced with a fenced, gravel parking area. See
Appendix A.4, which includes a series of aerial photographs dating back to July, 1990.
Upon a visual examination of existing site conditions, stormwater runoff is either collected in a
private catch basin located on Parcel 3340402880, flows onto the neighboring Brotherton
Cadillac automotive dealership, or flows onto SW 12th St or SW 13th St to be collected by a public
catch basin. Stormwater collected in the private catch basin, or that flows onto the neighboring
dealership, is conveyed through an existing private wet vault water quality and detention vault
that discharges into the public stormwater system on the southwest corner of the dealership.
Stormwater in a portion of the southwest corner of the existing dealership is collected into a
system that conveys it west across Maple Ave into a neighboring private stormwater system.
Based upon a review of available information from the City of Renton, we are not aware of any
Figure 2 – Site Location Map – Proposed Addition
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capacity problems with the existing drainage facilities adjacent to this area. The City of Renton’s
Public Works Maps combined with King County GIS together indicate the site is not located
within or near any critical areas. In addition, it is located within the Peak Rate Flow Control
Standard Zone.
1.3 Proposed Conditions
The purpose of site improvements for this project is to create a new stand-alone automotive
dealership for Brotherton Cadillac, and an addition for the existing automotive dealership. A
shared access will be constructed between the new construction and the existing building that
connects with the existing rear entrance to the existing building. The project proposes grading,
paving, and drainage (water quality facilities, detention, and conveyance piping) improvements
for on-site and off-site areas. See Table 1 for a description of existing and proposed surface
conditions of the proposed building and Table 2 for a description of existing and proposed
surfaces for the proposed addition.
Over 50% of the stormwater generated on-site will be from a pollution-generating surface in a
commercial area and thus stormwater runoff generated will be subject to enhanced basic water
quality treatment before being conveyed to the conveyance system located within the City’s
right-of-way. Treatment for the proposed building and addition will be provided by Oldcastle
BioPod Biofilters. All proposed surfacing in the project area is considered new or replaced
surfacing. Please see Appendix A.5 for the sub-basin exhibit as it outlines the tributary area for
each catch basin.
ADA accessible ramps will also be installed at the adjacent corners, at the intersection of Maple
Ave SW and SW 12th Street. These ramps are not included in the surface coverages discussed in
this report as they replace impervious surface with impervious surface and will have no
noticeable impact on the public stormwater system.
Please see Appendix A.3 for Existing and Proposed Surface Coverage Exhibits.
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Table 1. Existing and Developed Condition Description – Proposed Building
Description On-site Off-site Total
Existing Conditions
Total Project Area (ft2) 51,250 6,710 57,960
Existing hard surface (ft2) 22,250 4,950 27,200
Existing landscaping/lawn area (ft2) 29,000 1,760 30,760
Total Project Area (ft2) 51,250 6,710 57,960
Amount of new hard surface (ft2) 25,350 400 25,750
Amount of new pollution generating hard surface (PGHS) (ft2) 16,850 400 17,250
Amount of replaced hard surface (ft2) 22,250 4,950 27,200
Amount of replaced PGHS (ft2) 14,450 4,950 19,400
Amount of new plus replaced hard surface (ft2) 47,600 5,350 52,950
Amount of new plus replaced PGHS (ft2) 31,300 5,350 36,650
Amount of existing hard surfaces converted to
vegetation/landscaping (ft2)
0 0 0
Amount of Land Disturbed (ft2) 51,250 6,710 57,960
Native Vegetation to Pasture (acres) 0 0 0
Existing vegetation area to remain (ft2) 3,650 1,360 5,010
Existing hard surface to remain unaltered (ft2) 0 0 0
Value of proposed improvements ($) $8.3M 0 $8.3M
Amount to be Graded/Approx. FILL (CY) 519 0 519
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Table 2. Existing and Developed Condition Description – Proposed Addition
Description On-site Off-site Total
Existing Conditions
Total Project Area (ft2) 13,630 1,850 15,480
Existing hard surface (ft2) 10,630 0 10,630
Existing landscaping/lawn area (ft2) 3,000 1,850 4,850
Developed Conditions
Total Project Area (ft2) 13,630 1,850 15,480
Amount of new hard surface (ft2) 4,660 930 5,590
Amount of new pollution generating hard surface (PGHS) (ft2) 240 930 1,170
Amount of replaced hard surface (ft2) 6,250 0 6,250
Amount of replaced PGHS (ft2) 6,250 0 6,250
Amount of new plus replaced hard surface (ft2) 10,910 930 11,840
Amount of new plus replaced PGHS (ft2) 6,490 930 7,420
Amount of existing hard surfaces converted to
vegetation/landscaping (ft2) 0 0 0
Amount of Land Disturbed (ft2) 13,630 1,850 15,480
Native Vegetation to Pasture (acres) 0 0 0
Existing vegetation area to remain (ft2) 2,720 920 3,640
Existing hard surface to remain unaltered (ft2) 0 0 0
Value of proposed improvements ($) $1.3M 0 $1.3M
Amount to be Graded/Approx. FILL (CY) 35 0 35
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2.0 CONDITIONS AND REQUIREMENTS SUMMARY
2.1 Discussion of Core and Special Requirements
These are two Commercial Arterial (CA) projects that each add more than 2,000 square feet of
new and replaced impervious surface. Therefore, the projects are subject to a full drainage
review and must satisfy all core requirements (1-9) and all special requirements (1-6) of the
2017 City of Renton Stormwater Design Manual (SWDM). See Figure 3 at the end of this Section
for the Drainage Review Flow Chart for the proposed building and Figure 4 for the Drainage
Review Flow Chart for the proposed addition. Although independently each project is subject
to a full drainage review, at the request of the City of Renton, the projects have been analyzed
and will be reviewed as a combined project. Below is a description of each core requirement
and how the project proposes to satisfy each requirement.
2.1.1 Core Requirement #1: Discharge at the Natural Location
This requirement will be met by discharging stormwater to existing private stormwater
networks, which ultimately discharge into Black River.
2.1.2 Core Requirement #2: Off-site Analysis
The Off-Site Analysis included in Section 3.0 of this TIR will satisfy this Core Requirement.
2.1.3 Core Requirement #3: Flow Control
Please see Section 4.0 for a discussion of flow control for the projects. The projects propose
work within the Peak Rate Flow Control Standards (Existing Site Conditions) Area. The project
must match the developed peak discharge rates to the existing site conditions peak discharge
rates for the 2-, 10-, and 100-year return periods. Existing flow volumes from the proposed
building will be matched through the use of a storage vault and variable speed pump station.
Flows from the new construction will flow through the existing stormwater system that exits
through the southwestern corner of the existing dealership parking lot. Runoff from the shared
accessway will be split between the existing Buick-GMC wetvault and the new Cadillac
stormwater system. The area flowing to the existing wetvault will be decreased due to
modifications made on the south side of the new Cadillac dealership and will not receive a
standalone flow control structure.
The proposed addition will not receive a flow control structure. Stormwater runoff from the
addition will not join the runoff from the new construction, but will maintain its current outfall
to the west of the site. Stormwater from the frontage improvements, new building and new
addition converge within ¼ mile of the site, downstream. As such, they are all considered to be
part of the same Threshold Discharge Area (TDA), and are all subject to flow control. To
mitigate the amount of storage required throughout the combined site, flow from the new
building will be attenuated such that the overall outflow from the site will match the 2-, 10-,
and 100-year return period rainfall events for the combined site. Flows will be attenuated
through the use of a variable-flow pump system so that the overall site outflow matches the
existing conditions.
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2.1.4 Core Requirement #4: Conveyance System
Please see Section 5.0 of this TIR for the conveyance system analysis and design. The new
building proposes to create a new stormwater system that will service stormwater that falls
on-site, directing it to the existing stormwater system that services the existing dealership. The
proposed addition will be connected to a private stormwater system to the west of the site,
per existing conditions. Stormwater from upstream that will be flowing through the site will
bypass storage and treatment before discharging into the existing downstream system in
conjunction with stormwater treated on-site. A spill control tee section will be placed within
CB08 and CB51 to handle spills on the new construction and new addition sites, respectively.
2.1.5 Core Requirement #5: Erosion and Sediment Control
A temporary Erosion and Sediment Control Plan (TESC) will be prepared and included in the
construction plan set. Additionally, a CSWPPP under a separate cover, will be provided to satisfy
this requirement.
2.1.6 Core Requirement #6: Maintenance and Operations
Please see Section 10.0 of this TIR for the Operations and Maintenance Manual, prepared to
satisfy this Core Requirement. Brotherton Cadillac will be responsible for maintenance and
operation of the proposed on-site stormwater facilities upon completion. The City of Renton
will continue to be responsible for operation and maintenance of stormwater systems in the
right-of-way.
2.1.7 Core Requirement #7: Financial Guarantees and Liability
We anticipate that Brotherton Cadillac will be required to provide a Construction Bond to the
City of Renton prior to issuance of the permit. The contractor/owner will be responsible for all
erosion and maintenance liabilities during construction.
2.1.8 Core Requirement #8: Water Quality
Please see Section 4.0 for a discussion of water quality for the project. Water quality treatment
will be provided by Oldcastle BioPod Biofilters for both the proposed building and addition.
Each BioPod will be sized and detailed according to the demands of the stormwater they are
treating. The GULD for the BioPod is attached in Appendix A.9. Basic treatment will also be
provided to the new building by a CONTECH CDS hydrodynamic separator. The GULD for the
CDS is also attached in Appendix A.9. The portion of stormwater from the shared access that is
not being treated by the Cadillac stormwater system will continue to be treated by the existing
wetvault.
2.1.9 Core Requirement #9: On-site BMPs
Target surfaces subject to Core Requirement #9 On-site BMPs include replaced impervious
surfaces, already mitigated with an approved on-site BMP. This site qualifies for the Large Lot
BMP Requirements per 1.2.9.2.2 of the City of Renton SWDM, since it is larger than 22,000
square feet. These requirements state that all proposed pervious surfaces must implement the
soil amendment BMP and roof downspout connections must be perforated pipe connections.
The soil amendment BMP will be implemented for every pervious service affected by
construction. The downspout BMP does not apply to the proposed project as infiltration is not
recommended on this site, per the geotechnical report in Section 6.0.
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In addition, these requirements require the consideration of the following BMPs: full
dispersion, full infiltration, limited infiltration, bioretention, permeable pavement, basic
dispersion, reduced impervious surface credit, native growth retention credit, tree retention
credit. None of the listed BMPs are feasible for implementation on the project site, and will
therefore not be implemented. The remainder of this section contains a discussion of
infeasibility for each BMP.
Full Dispersion – The application of this BMP depends on the sheet flow of runoff through an
area of native vegetation. The project site does not contain any native vegetation area (e.g.,
forested) in the existing or proposed condition. Therefore, full dispersion is infeasible for this
project.
Full Infiltration – Per Section C.2.2.2 of the Manual, full infiltration requires that “Existing soils
must be coarse sands or cobbles or medium sands and cannot be comprised of fill materials
where the infiltration device will be located.” Site soils meet this requirement, except for the
top layer of soil. However, the groundwater level renders infiltration on-site infeasible, as
infiltration would have to occur in a silt material. These conditions are described in the
Geotechnical Engineering Report prepared by Migizi Group, Inc. (dated July 8, 2021) for the
proposed project. This report shows test pit logs with four distinct soil horizons, none of which
provide viable infiltration due to either the groundwater level or material. The Geotechnical
Engineer does not find that site soils will support Full or Limited infiltration (see section 3.4
Infiltration Conditions of the Migizi report). Therefore, full infiltration is infeasible for this
project.
Limited Infiltration – The infeasibility criteria for limited infiltration are the same as those for
full infiltration except that appropriate soils may be fine sands, loamy sands, sandy loams, or
loams. Note that Section C.2.3.2 of the Manual states “Silt and clay loams, and cemented till
(hardpan) are not suitable for limited infiltration systems.” Site soils meet this requirement,
except for the top layer of soil. However, the groundwater level renders infiltration on-site
infeasible, as infiltration would have to occur in a silt material. The Geotechnical Engineer does
not find that site soils will support Full or Limited infiltration (see section 3.4 Infiltration
Conditions of the Migizi report). Therefore, limited infiltration is infeasible for this project.
Bioretention – This project is underlain by soil that makes infiltration impractical, as such a
bioretention facility is infeasible.
Permeable Pavement – The soil under a permeable pavement section must provide adequate
treatment for groundwater protection. The underlying soils should also infiltrate for this
surfacing to be durable and effective. The requirements for adequate treatment are a minimum
organic content of 1.0% and a minimum cation exchange capacity of 8 milliequivalents per 100
grams. The uppermost soil layer on the project site is made up of fill material and does not meet
these requirements. Again, the depth to groundwater renders BMPs that rely on infiltration
ineffective. Permeable Pavement is infeasible for this project.
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Basic Dispersion – The implementation of basic dispersion limits the area of impervious surface
that can run off to a dispersion structure to 700 square feet per structure. The proposed
construction will be adding over 16,500 square feet, which would require 24 separate flow
dispersion structures. It is also required for the dispersed stormwater to flow over a vegetated
surface, but there are no existing or proposed vegetated surfaces near the proposed
development. Such a flowpath cannot be provided on the project site without a drastic
reduction in the number of parking stalls and vehicle paths. We see basic dispersion as
infeasible to the project.
Reduced Impervious Surface Credit – This BMP presents four possible methods of impervious
surface reduction: restricted footprint, wheel strip driveways, minimum disturbance
foundation, and open grid decking over pervious surface. The restricted footprint method
requires less than 4,000 square feet of impervious area, which is not feasible for the proposed
use of the site as an automotive dealership. A wheel strip driveway is not applicable for a
commercial parking lot. A minimum disturbance foundation is not feasible for an automotive
workshop. Open grid decking over a pervious surface is also not applicable to a parking lot. The
reduced impervious surface credit is infeasible for this project.
Native Growth Retention Credit – The existing condition of the site does not contain any native
growth. Therefore, the native growth retention credit is infeasible for this project.
Tree Retention Credit – The existing condition of the site contains approximately 28 trees that
will all be removed by the current owner as a condition of the lease agreement. Therefore, the
tree retention credit is infeasible for this project.
2.1.10 Special Requirement #1: Other Adopted Area-Specific Requirements
N/A. The project site is not in a designated critical drainage area or in an area included in an
adopted master drainage plan, basin plan, salmon conservation plan, stormwater compliance
plan, flood hazard management plan, lake management plan, or shared facility drainage plan.
2.1.11 Special Requirement #2: Flood Hazard Area Delineation
N/A. Per the FEMA floodplain map at the end of this Section, Figures 5 and 6, the project sites
lie within Zone X which is defined as “areas determined to be outside 500-year floodplain” and
therefore flood-related delineation on the project site is not required.
2.1.12 Special Requirement #3: Flood Protection Facilities
N/A. This project does not propose to rely on an existing flood protection facility nor does it
modify or construct a new flood protection facility.
2.1.13 Special Requirement #4: Source Control
Brotherton shall implement Operational and Structural Source Control BMPs that includes the
maintenance of stormwater drainage and treatment systems as described in the Operations
and Maintenance Manual, included in Section 10.0 of this report.
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2.1.14 Special Requirement #5: Oil Control
This project does not propose to develop a high-use site as defined by City of Renton SWDM;
therefore, this Special Requirement is not applicable.
2.1.15 Special Requirement #6: Aquifer Protection Areas
This project is not located within an Aquifer Protection Area per King County GIS.
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Figure 3 – Drainage Review Flow Chart – Proposed Building
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Figure 4 – Drainage Review Flow Chart – Proposed Addition
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Figure 5 – FEMA Map – Proposed Building
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Figure 6 – FEMA Map – Proposed Addition
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3.0 OFF-SITE ANALYSIS
Per City of Renton SWDM Section 1.2.2, this project must provide an off-site analysis report
that assesses potential off-site drainage and water quality impacts associated with the
redevelopment of the project site. The level of analysis required depends on the specific site
and downstream conditions. In accordance with Section 1.2.2.1, a Level 1 Downstream Analysis
has been performed.
3.1 Define and Map the Study Area
Based on the current topographic survey and our observations of the site, the site is mostly
tributary to an existing, private conveyance system. Those portions of the site that do not
discharge to the existing, private conveyance system are tributary to an existing City
conveyance system. The project does not propose any significant improvements to the existing
conveyance elements on-site. Downstream of the project discharge locations, according to City
of Renton GIS, stormwater from the proposed building site is conveyed west, into, and through,
the neighboring Brotherton Cadillac automotive dealership stormwater system. Stormwater
from the site of the proposed addition flows west into, and through, the neighboring Good
Chevrolet automotive dealership stormwater system before heading south. The conveyance
from both sites continues southward until it reaches Interstate 405 (I405). Before intersecting
I405, stormwater flows into a catch basin on the north side and is diverted to the west. The pipe
daylights and discharges the stormwater to flow over the surface before being collected in
another City stormwater conveyance pipe on the south side of the existing Good Chevrolet, INC
Chevrolet dealer. Stormwater then flows in another enclosed system under Lind Ave. SW
before again daylighting and being discharged to run along the north side of I405. Stormwater
continues flowing over the surface north of I405 before sheet flowing onto SW 13th St and
being collected in a City catch basin. The pipe network downstream of this catch basin
ultimately discharges into Black River. A topographic site map is featured in Figures 7 and 8 of
this Report.
Figure 7 - Downstream Flow Path – Proposed Building
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Figure 8 – Downstream Flow Path – Proposed Addition
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Figure 9 – Topographic Survey
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3.2 Resource Review
A thorough review of the resources provided by the City of Renton Maps, as outlined on page
2-11 of the SWDM, has been completed for the study area. Research conducted on 1/17/2022
has shown that there are not any adopted basin plans available for the study area. According
to the FEMA Map presented in Figures 5 and 6 of this report, the project sites lie within Zone X,
which is defined as areas outside the 500-year floodplain. The sites are located within the
Duwamish – Green River Watershed, the Black River Basin, and the Springbrook Creek Sub
Basin. Based on the City of Renton GIS, the project area has not been defined as a sensitive
area. To our knowledge, there have not been any reported road drainage problems associated
with the roads surrounding the site. It was also found that the site does not have a migrating
river study, a 303d listing, or an adopted stormwater compliance plan available. Please see
Section 4.0 for a discussion of water quality for the project. A geotechnical report completed
by Migizi Group can be found in Appendix A.6.
3.3 Field Inspection
During field inspections, the system appeared to be working sufficiently with no obvious clogs
or flooding. We do not anticipate any future problems with the proposed stormwater system.
The proposed conveyance system has more catch basins: therefore each individual catch basin
will have a smaller tributary area. Stormwater flows on the site of the proposed building are
expected to increase due to an increase in impervious surface, and will be handled by a pump
station and supplementary detention system to match existing discharge into the existing
downstream system. The amount of area tributary to the existing conveyance system
connected to the proposed addition will remain largely the same – there is not a substantive
increase in stormwater runoff tributary to the existing conveyance system as a result of the
proposed addition. Please see Section A.5 for the modeled areas in the predeveloped and
mitigated scenarios for both sites.
Since it has been determined that there are no anticipated stormwater problems associated
with this project, Level 2 and Level 3 downstream analyses are not required.
No problems were found related to constrictions, capacity deficiencies, flooding, scouring,
overtopping hazards, sedimentation or erosion, aquatic organisms or their habitation.
Land use associated with the study area includes commercial/residential land applications, such
as several automotive dealerships and the residential lots to the east of the site. In addition,
the study area includes utilities and roadways. Existing impervious surfaces located within the
study area include commercial businesses, compacted gravel access, paved parking lots, paved
driveways, and the paved public right-of-way. Based on existing site topography, stormwater
runoff is captured within the City’s right-of-way where it is collected by a storm conveyance
system and discharged to the Black River.
3.4 Drainage System Description and Problem Descriptions
No drainage system problems were observed during the field inspection.
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3.5 Mitigation of Existing or Potential Problems
The proposed project area does not have any existing or anticipated drainage problems as
outlined in Section 1.2.2.1 of the City of Renton SWDM.
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4.0 FLOW CONTROL, LID, AND WATER QUALITY FACILITY ANALYSIS AND
DESIGN
4.1 Existing Site Hydrology
The site of the proposed building currently has four residences, two sheds, shared lawn
surfacing, and a large parking area composed of both crushed rock surfacing and asphalt
cement pavement. Stormwater that does not infiltrate into the lawn sheetflows off-site,
primarily onto either SW 12th St or SW 13th St. Run-off can flow onto the nearby existing
Brotherton Cadillac dealership, although the site is graded in such a way that this is unlikely.
From SW 12th St or SW 13th St, stormwater flows into City stormwater conveyance facilities.
The site of the proposed addition currently has an automotive dealership with paved
parking/display space that drains to one of two existing stormwater facilities on-site. One is a
catch basin that flows directly into the City stormwater system from the southwest area of the
site, which then discharges into Good Chevrolet’s private system. The other is a regional
network that begins to the east of the site and directs stormwater into a large detention
structure under the western parking area on-site. Prior to construction of the structural
addition, the project site surfacing consisted of asphalt pavement, roofing, and landscaped
islands. The addition and nearby parking are tributary to the neighboring Good Chevrolet’s
conveyance system located on the west side of Maple Ave SW.
4.2 Developed Site Hydrology
The proposed building site will be comprised of primarily asphalt pavement surfacing and roof
area. There will be landscaped islands around the perimeter of the site, with approximately
4,840 square feet of landscaping. Stormwater on-site will be collected and conveyed into an on-
site storage facility after treatment. The project does not propose to alter the downstream
flow path and will maintain discharge to the natural location.
The proposed addition site will be comprised of similar surfaces to existing, though some
asphalt paved area will be converted to roofed area. In the developed condition, approximately
4,420 square feet of area which was previously asphalt pavement will now be rooftop surfacing.
The project does not propose to alter the downstream flow path and will maintain discharge to
the natural location.
4.3 Performance Standards
The sites are within a Peak Rate Flow Control Standards (Existing Site Conditions) Area, which
requires matching the existing site conditions 2-, 10-, and 100- year peak flows. The
predeveloped sites are comprised of asphalt pavement, rooftop surfacing, lawn, and crushed
rock surfacing. The proposed building site conditions include a significantly higher quantity of
impervious surface than the existing conditions. The proposed addition site conditions include
approximately 240 square feet more of impervious surfaces than the existing conditions on-
site. Frontage improvements for the addition will replace approximately 930 square feet of
landscaping with impervious surfaces.
In areas where conveyance features are required, they have been designed in accordance with
Section 1.2.4 of the SWDM. The proposed private conveyance elements for the proposed
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building include conveyance piping from the new asphalt surfacing to an Oldcastle BioPod
Biofilter before it is detained. Stormwater from the new roof will be conveyed directly to the
detention facility. Enhanced basic water quality treatment is required for stormwater that falls
on, or runs off of, pollution-generating surfaces on-site such as the parking lot. The treatment
will be provided by the BioPod. Downstream of the storage structure is a pump that is set to
match the existing 2, 10, and 100-year flow conditions that is tributary to the existing
downstream stormwater system.
The proposed private conveyance elements for the proposed addition include conveyance
piping from the new roof to a private Type 1 catch basin that is separate from the stormwater
network on site. Conveyance piping connects this catch basin to another existing private Type
1 catch basin, which then connects to the neighboring Good Chevrolet’s stormwater system on
the west side of Maple Ave SW. It is proposed to install a small Oldcastle BioPod Biofilter on-
site for treatment.
4.4 Flow Control System
Flow control is required for the whole project. The proposed addition and frontage
improvements will receive no flow control to either mitigate storage required on-site, or due
to the receiving stormwater system being off-site. Flow control for the new building will be
provided by a variable flow lift station. The lift station will attenuate flows from the new
building site to provide flow control for the whole site.
4.4.1 Flow Control Exemptions Check
The proposed building site is not exempt from flow control. See Section 2.1.3 of this report for
further discussion. The proposed addition site is exempt from flow control due to an increase
of less than 0.15 cfs in the 100-year storm event. See Section 2.1.3 of this report for further
discussion.
4.4.2 Flow Control Area
The site falls within a Peak Rate Flow Control Standard – Match Existing Area, based on the
Flow Control Application Map provided by the City of Renton (Figure 10 of this TIR).
4.4.3 Flow Control Area Requirements and Exceptions
Peak Rate Flow Control Standard – Match Existing – Areas must match existing site conditions
2-,10-, and 100-year peak rate runoff for areas draining to constructed (man-made) or highly
modified drainage systems so as to not create a downstream flooding problem. Per Section
1.2.3.1.A, Exception 1, of the SWDM, the target surfaces of the proposed building subject to
the Peak Rate Flow Control Standard Areas facility requirements will generate more than a
0.15-cfs increase in the existing site conditions peak flows. Therefore, the proposed building
project proposes a pump station and supplementary detention system to serve as a flow
control facility. The proposed addition is not expected to generate a 0.15cfs or greater increase
in the 100-year peak flow, therefore flow control is not required for that project.
4.4.4 Identify Applicable Flow Control BMPs per Core Requirement #9
Please see Section 2.1.9 of this report for an evaluation of Flow Control BMPs per Core
Requirement #9.
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4.5 Water Quality
As mentioned in Section 4.3, both projects propose to satisfy the enhanced water quality
requirement by installing an Oldcastle BioPod Biofilter.
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Figure 10- City of Renton Flow Control Application Map
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5.0 CONVEYANCE SYSTEM ANALYSIS AND DESIGN
Proposed conveyance elements include conveyance piping, storage, and a pump station for the
new building. 8” PVC piping will be used for the roof drains of the new building, and 6” PVC
piping will be used for the roof drains of the addition. 12” CPEP piping will be used for
stormwater conveyance throughout the site at a minimum angle of 0.5%. The two graphs below
were created with the use of WWHM, using a 15-minute time step to determine the expected
25 year peak flow that would be experienced by the eastern and western BioPods on-site,
servicing the addition and new building, respectively. The WWHM Models used the surfaces and
areas flowing into the BioPods, therefore they do not include areas for frontage improvements,
or similar non-tributary areas.
Figure 11 - WWHM Stormfall for the Eastern BioPod
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Figure 12 - WWHM Stormfall Tributary to Western BioPod
Using Manning’s Equation:
𝑄= 1.49
𝑛𝐴𝑄2 3⁄𝑄1 2⁄
Where A = 0.785ft2 for a 12” pipe, n = 13 for PVC or CPP, and S = 0.5% to represent the
shallowest designed slope, yields a flow, Q, of 2.526cfs. This is above the 25 year peak flow rate
for either system. A 6” diameter pipe, with an area of 0.196ft2 yields a flow of 0.398cfs, which
is high enough to convey the 100 year peak flow rate for the system servicing the addition.
The lift station servicing the new building was designed with the use of Autodesk Storm and
Sanitary Analysis (SSA) to match the 2, 10, and 100-year storms while minimizing required
storage for the entire project site, including frontage improvements. SSA reports are included
in Appendix A.8. Design of the lift station was attempted with WWHM, but it was determined
that the dual-pump system cannot be properly modeled in WWHM. The mitigated condition for
the full site is included with the WWHM model for the full site, but it should be ignored.
The design of the proposed conveyance systems, including the lift station, is discussed in more
detail in Appendix A.5.
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6.0 SPECIAL REPORTS AND STUDIES
We are not aware of any site characteristics that are particularly sensitive to stormwater runoff.
A geotechnical report by Migizi Group can be found in Appendix A.6 of this report.
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7.0 OTHER PERMITS
We anticipate that a Right-of-Way Use permit, Land Use Master Application, Civil Construction
Permit, Building Permit, NPDES permit, and an Environmental Review Permit (SEPA) will be
required. A leachable materials covenant will be required for the constructed rooftops to
qualify them as NPGIS (non-pollution generating impervious surface). Franchise permits will
be required for each franchise affected by overhead utilities being undergrounded.
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8.0 CSWPPP ANALYSIS AND DESIGN
The Construction Stormwater Pollution Prevention Plan reports is included under a separate
cover.
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9.0 BOND QUANTITIES AND R/D FACILITY SUMMARIES
9.1 Bond Quantities
See Appendix A.2 for a copy of the City of Renton bond report.
9.2 Facility Summaries
These projects propose to implement a Contech CDS hydrodynamic separator, Oldcastle
BioPod Biofilters, Oldcastle StormCapture water detention, stormwater pump station,
collection catch basins, and conveyance piping.
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10.0 OPERATIONS AND MAINTENANCE MANUAL
10.1 Purpose
The purpose of this manual is to provide guidelines for maintaining the storm drainage system
as a part of the construction for the new Brotherton Cadillac building and new Brotherton
Buick-GMC building addition. The neighboring site addresses are 201 SW 12th Street and 215
SW 12th Street, Renton, WA 98057.
Storm utility improvements that have been proposed as a part of the projects include:
o Contech CDS hydrodynamic separator
o Oldcastle BioPod Biofilter
o Oldcastle StormCapture
o Storm Drainage Piping
o Catch Basins
o Pump Station
Each portion of the system has to be maintained in good working condition for the system to
function properly.
Operations and Maintenance of the private drainage systems will be the responsibility of the
Owner, Brotherton. Brad Brotherton is the contact person at Brotherton. His contact
information is:
Brad Brotherton
Brotherton Cadillac
215 Southwest 12th Street
Renton, WA 98057
Phone: (425) 336-1089
The City of Renton will continue to be responsible for the Operation and Maintenance of public
improvements.
10.2 Permanent Facilities Description
Conveyance piping will convey stormwater from the new rooftop and paved surfaces to the
existing stormwater facilities on-site. The project does not propose to alter downstream flow
paths and will maintain ultimate discharge to the Black River. For the proposed building, a
Contech CDS hydrodynamic separator and Oldcastle BioPod Biofilter will provide water quality
treatment. Oldcastle StormCapture will store stormwater so it can be discharged at a
controlled rate by the proposed pump station. The proposed addition will be treated by n
Oldcastle BioPod Biofilter.
10.3 Discussion of Maintenance
Any buildup of sediment, debris, vegetation, or trash that impedes the catch basins will reduce
the storm system capacity. As a result, care must be taken to keep all inlets clear of debris.
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The applicable maintenance checklists and excerpts from the 2017 SWDM have been included
with the Operations and Maintenance Manual for review during routine maintenance
inspections.
10.4 Maintenance Frequency
Following construction of the project, the storm drainage system shall be inspected and
maintained according to their respective maintenance checklists included at the end of this
manual.
Facilities will be inspected annually, or after every significant storm event where the
precipitation is greater than or equal to one inch in 24 hours
When deficiencies are noted, the problems are to be corrected as soon as possible. Any spill of
hazardous material (e.g. fuel, lubricant, herbicide, etc.) shall be cleaned up immediately and
shall be reported to the Division of Emergency Management (1-800-523-5044). Contaminated
material will be disposed of properly.
Any questions about the existence of a problem should be directed to a Professional Engineer.
10.5 Annual Cost Estimate
Annual maintenance costs for the proposed stormwater conveyance system on-site for the
proposed building is expected to increase the costs of maintaining the private stormwater
system by $1 for every linear foot of new piping, $500 for each CDS, $500 for every BioPod,
$500 per pump station, and $300 for each StormCapture unit. Approximately 1850 linear feet
of proposed pipe, one CDS, one BioPod, one pump station, and 5 StormCapture units will have
an annual cost of maintenance of $4,850 for the proposed building.
Annual maintenance costs for the proposed stormwater conveyance system on-site for the
proposed addition is expected to increase the costs of maintaining the private stormwater
system by $1 for every linear foot of new piping and $500 for every BioPod. Approximately 200
linear feet of proposed pipe and one BioPod will increase the cost of maintenance by $700.
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Cover Sheet for Inspection Forms
Name of Inspector:
_____________________________________________________________
Date of Inspection:
_____________________________________________________________
Number of Sheets Attached:
_____________________________________________________________
Inspector’s Signature:
_____________________________________________________________
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Maintenance Log
Action
Taken
Name Date How Procedure
Was Performed
Problems
Encountered
Additional Actions
Recommended
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A.1 TIR Worksheet
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Figure 13 – TIR Worksheet
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A.2 Bond Quantity Worksheet
The Bond Quantity Worksheet is included under a separate cover.
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A.3 Existing and Proposed Surface Coverage Exhibits
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A.4 Site Historical Aerial Photography
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A.5 Stormwater Engineering Calculations
Proposed Building:
Conditions
This project is in a location subject to meeting the Peak Rate Flow Control Standard, as
described in Section 4.4. Therefore, we have prepared the following calculations to determine
if flow control will be required for this project.
As previously mentioned, the site is predominantly currently covered by lawn and several small
structures. The site presently discharges offsite to the west. There is presently no treatment or
flow control in this system. Flow control will be required to be installed in this system to match
the existing discharge rate for the 2-, 10-, and 100-year storm peak flow rates.
Predeveloped Conditions:
Based on aerial photographs, included in Section A.4, the site had previously been, and is
currently, a residential location. The eastern residences appear to have been replaced with
parking between May of 2013 and May of 2018. Areas of the replaced residential space used
for stormwater design were acquired from aerial photographs taken in May of 2010 as they are
clear enough to use for approximate surface areas. Spaces that appear to have remained largely
unchanged had their areas gathered from survey data of the site.
See the following excerpt from WWHM indicating the assumptions used in the “Predeveloped”
Condition:
Figure 14 - Predeveloped conditions for the Cadillac site used for Water Quality
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Mitigated Conditions:
The mitigated site coverage is comprised of asphalt pavement parking and the rooftop of the
proposed structure with sidewalks and landscaping along the perimeter of the site and
proposed automotive dealership.
See the following excerpt from WWHM indicating the assumptions used in the “Mitigated”
Condition:
Figure 15 - Developed conditions for the Cadillac site used for Water Quality
Flow Frequency Results:
The flow frequency table included on the following page indicates that the peak stormwater
runoff from the developed site will increase by more than 0.15cfs for the 100-year storm
condition. As the flow is expected to change by more than 0.15cfs, and more than 5,000 square
feet of new and replaced impervious surface are proposed, a flow control structure will be
necessary. It is proposed to use a pump station for flow control, and to maintain connection
with the existing downstream facilities. Excess flow will be detained in connected Contech
clamshell storage vaults. Design of the flow control structure is explained in more detail in the
Combined Site section.
Water Quality
More than 5,000 square feet of impervious surface is being installed or replaced as a result of
this project: therefore water quality treatment is required. Water quality treatment flows
calculated by WWHM are shown below. Surfaces tributary to the BioPod installed on the
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Cadillac site were used to determine sizing. These surfaces include the parking lot and installed
asphalt, but not frontage improvements. The proposed single-ply TPO or PVC membrane fabric
rooftop was not included in the water quality calculations as it is considered to not be a
pollution-generating surface and will bypass the treatment structure. It was, however, included
in the calculations for detention requirements. Treatment flows did not change with, or
without, the inclusion of the roof surface.
Using the off-line correction factor located in Table 6.2.1.A of The Manual, with a 2-year storm
rainfall intensity of 2 inches from the isopluvial maps located in Section 3.2.1 of The Manual,
the correction factor is 3.5312. Using this correction factor and multiplying it by the calculated
off-line water quality flow, 0.0974 cfs, the design water quality treatment flow for an off-line
treatment structure for the new construction is 0.344 cfs. An 8x16 Oldcastle BioPod Biofilter
has been selected as an off-line treatment structure, as it has an enhanced treatment capacity
of 0.384 cfs.
Figure 16 – WWHM 2012 Flow Frequency calculations for the Cadillac site
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Figure 17 - WWHM 2012 Water Quality calculations for the Cadillac site
Proposed Addition:
Conditions
This project is in a location subject to meeting the Peak Rate Flow Control Standard, as
described in Section 4.4. Therefore, we have prepared the following calculations to determine
if flow control will be required for this project.
As previously mentioned, the site is predominantly already covered by asphalt parking areas
and a structure. The asphalt being replaced presently discharges offsite to the west, separate
from the existing wet vault. There is presently no treatment or flow control in this system. No
flow control would normally be required, or proposed, to be installed in this system, as the peak
flow produced by the 100-year storm does not increase by more than 0.15 cfs if the existing
site conditions are assumed to be lawn. As this site is part of a larger TDA that is subject to flow
control, it will receive flow control. However, the flow control will be provided by attenuation
of the stormwater from the new building on the Cadillac site to match the existing storm flows.
Predeveloped Conditions:
Based on aerial photographs, included in Section A.4, the site had previously been a residential
location before the construction of the existing Brotherton Cadillac automotive dealership. Any
reference we have access to showing this residential development are too blurry to acquire
usable areas for stormwater calculations. As such, it will be assumed that the existing site
condition is flat lawn covering, as that is the most restrictive from a stormwater design
perspective that would be possible.
See the following excerpt from WWHM indicating the assumptions used in the “Predeveloped”
Condition:
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Figure 18 - Predeveloped conditions for the Buick-GMC site used for Water Quality
Mitigated Conditions:
The mitigated site coverage is comprised of primarily asphalt pavement parking and the
rooftop of the proposed structure.
See the following excerpt from WWHM indicating the assumptions used in the “Mitigated”
Condition:
Figure 19 - Developed conditions for the Buick-GMC site used for Water Quality
Flow Frequency Results:
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The flow frequency table included on the following page indicates that the peak stormwater
runoff from the developed site will increase by less than 0.15cfs for the 100-year storm
condition. As the flow is expected to change by less than 0.15cfs, a stand-alone flow control
structure will not be provided for the addition. Instead, flow control for the entirety of the
project site will be handled by a pump station located in the parking lot of the new building.
Water Quality
More than 5,000 square feet of impervious surface is being replaced during this project. While
the net pollution-generating surface is decreasing, water quality treatment is required. Water
quality treatment flows calculated by WWHM are shown below. Surfaces included for
treatment sizing of the Western BioPod are the replaced asphalt and the rooftop of the
addition. The proposed rooftop was included in the water quality calculations, even though it
is considered to not be a pollution-generating surface, as it will not bypass the treatment
structure. Frontage improvements, on- and off-site, were not included in treatment sizing
calculations.
Using the off-line correction factor located in Table 6.2.1.A of The Manual, with a 2-year storm
rainfall intensity of 2 inches from the isopluvial maps located in Section 3.2.1 of The Manual,
the correction factor is 3.5312. Using this correction factor and multiplying it by the calculated
off-line water quality flow, 0.0198cfs, the design water quality treatment flow for an off-line
treatment structure for the new construction is 0.0699 cfs. An 4x8 Oldcastle BioPod Biofilter
has been selected as an off-line treatment structure, as it has a treatment capacity of 0.096 cfs.
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Figure 20 - WWHM 2012 Flow Frequency calculations for the Buick-GMC site
Figure 21 - WWHM 2012 Water Quality calculations for the Buick-GMC site
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Combined Site
Flow Control
As stated in Section 2.1.3 of this report, the site is subject to Peak Rate Flow Control Standard
(Existing Site Conditions) and must therefore match the developed peak discharge rates of the
existing condition’s 2-, 10-, and 100-year return period storms. Western Washington Hydrology
Model (WWHM) was used to determine the peak storm flows for the site, based on existing
conditions. Existing conditions are described in Section 1.2 of this report, as well as A.3. The full
project boundary, including frontage improvements, was used to determine the existing and
proposed surface conditions used for flow control calculations. These surface conditions can
be seen in Appendix A.3, and Tables 1 and 2. Additionally, the area for the existing portion of
the shared access that is not being affected by this project was included in both the WWHM
and SSA models. This area was included to ensure all runoff flowing through a control structure
was being accounted for. It is not included in Tables 1 and 2, or in Appendix A.3. however, it can
be seen in the drainage basin exhibits at the end of A.5. The WWHM process is described in A.5,
and the results are included as A.7. These flows were used as design flows for the pump station.
The target flows for the whole site are also highlighted in Figure 22.
Figure 22 - WWHM 2012 Flow Frequency Calculations for the combined project area – Bypass and Pumped
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A style of variable-speed pump was originally chosen that could handle flow control
requirements for the Cadillac site, and only the Cadillac site. The original plan was to use two
pumps with a series of floats that would toggle minimum and maximum flow states for the two
pumps. One pump (lead pump) was to start at a minimum flow state for the 2-year storm, then
the second (lag pump) would activate at a minimum flow state for the 10-year storm, and both
would engage a maximum flow state for the 100-year storm. However, after consultation with
the City of Renton, it was determined that the pump would need to serve as flow control for
the whole site. As such, the timing and operation of the pumps has been modified. The current
design has one pump engage a minimum flow state for the 2-year storm and then increase to a
maximum flow state for the 10-year storm. The lag pump will then engage in a minimum flow
state for the 100-year storm. From the results of the SSA model, discussed further in this
appendix, if the lag pump were to engage in a maximum flow state to assist with the 100-year
storm, then the downstream system would experience more flow than the existing conditions.
Using the lag pump in a minimum flow state in this manner also allows for the lag pump to be
engaged in a maximum flow state should it be required. Pumps will be engaged in minimum or
maximum flow states by controlling the current they receive through a series of float switches.
Once activated, a pump will remain in the last state activated until the water level in the lift
station is low enough to trigger the pump off float switch. The designation of lead and lag pump
will alternate to mitigate wear and tear on the pumps.
Included in the pump station structure are a series of float switches that will activate the pumps
at their required flow states, and low and high water level alarm floats. The low water level
alarm will alert the owner that the pump is no longer submerged, which could cause damage to
the pump. The high water level alarm will alert the owner that the water level is becoming close
to overtopping the structure. The elevations of each of the previously mentioned float switches
is provided on sheet C3.10C of the civil construction drawing set. To prevent overtopping, in
the case of a pump failure, a 12” pipe will be installed near the top of the structure that will
connect to the nearby bypass for surface water from surfaces to the east to serve as an
emergency overflow.
To determine the required pump characteristics, a system-demand curve (SDC) was generated
using a combination of the static head and frictional losses in the pump system. A system-
demand curve represents the amount of total dynamic head (TDH) that will be generated at
certain flows through the system. The static head is the difference between the standing water
level of the pump station and the invert elevation of the outlet. Frictional losses were
computed using the Hazen-Williams friction coefficient:
ℎ𝑓=10.44 ∗(𝐿)∗((𝑄)1.85
(𝐶)1.85 ∗(𝑑)4.8655)
Where:
• hf is the head for the frictional loss in a pipe, in feet
• L is the length of the pipe, in feet
• Q is the flow through the pipe, in gallons per minute
• C is the Hazen-Williams roughness coefficient
• d is the diameter of the pipe, in inches
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Frictional loss was calculated for every different pipe diameter and material used in the force
main. Both pipes used in this force main are PVC, one is 4 inches and the other is 6 inches. PVC
has a Hazen-Williams roughness coefficient of 150. To account for minor losses of pipe fittings
(e.g., bends, enlargements, valves, etc.) that can greatly affect the performance of a pump, a
nomograph was used to convert minor losses into an equivalent length of pipe for each pipe.
The nomograph, Figure 9.2 of the Handbook of PVC Pipe, 5th Edition, is included as Figure 24.
The equivalent length of the 4 inch diameter pipe used for calculations was 105.5 feet, and the
6 inch pipe’s equivalent length was 46.1. Frictional losses for each pipe are added together, with
the static head to determine the TDH for a given flow. To create an SDC, TDH is determined for
several flows and graphed. This project started with a flow of 0 gpm and calculated the TDH for
every flow up to 300 gpm in 50 gpm increments.
TDH was calculated for the 2-, 10-, and 100-year design flows using the same method as the
SDC. The design flows were gathered from WWHM and converted into gallons per minute. On
the graph, they are represented by enlarged, hollow circles to highlight their location relative
to the operational envelope of the pumps. After the original design flows had been calculated
and graphed, the envelopes of several variable-flow pumps were compared to the design flows.
When comparing the pump curves of various multi-phase pumps to original project
requirements, the Flygt NP 3085 SH was deemed to be the most appropriate. The lower and
upper limits of the pump curve for the NP 3085 SH were graphed against the system demand
curve in Figure 23. Technical cut sheets for the selected pump can be found in A.10. The four
pump curves shown are the minimum output of a single pump operating, the minimum output
of both pumps operating, a mix of one pump operating at minimum and one at maximum, and
both pumps operating at maximum output. These curves generate an “operational envelope,”
that bounds the potential flows the pump system can produce. Each of the design flows appear
within the operational envelope, meaning this pump configuration can handle the original
design flows for the Cadillac site. This model of multi-phase pump was used when the design
shifted to include flow control for the entire project site and was found through SSA modeling
to still be sufficient.
Float switch elevations were determined through the use of an SSA model of the proposed
stormwater system and an iterative process of adjusting the pump activation depth. SSA has
four options for pump curves, one that moderates flow by available volume, one that
moderates flow by the head difference between the structure inlet and outlet, and two that
determine the flow by the depth of water in the structure. One of the two options that
determines flow based on the depth of water in the structure uses a variable-flow pump curve
while the other uses a step function to determine set flows at set depths. The option that
utilizes the difference in head between the inlet and outlet was used to determine the float
elevations as it most closely resembles the proposed conditions.
Two pump curves were created in SSA to represent the proposed conditions. One curve was
created to mimic the minimum output pump curve, included as Figure 25. The other pump
curve, included as Figure 26, is the difference between the minimum and maximum output for
a single pump. With these two pump curves set up in this fashion, it is possible to model a pump
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running at minimum output until water reaches a depth that would activate the maximum
output mode. At the depth that the pump would switch to maximum output, the second pump
curve is activated so the two curves are being used concurrently, representing one pump
running at maximum output. This is shown on Figures 30 and 32, where a new pump flow curve
appears on the graph and does not match the one that is already there. On Figure 32, the lag
pump can be seen activating at minimum output, after the maximum output curve for the lead
pump has been activated, and matching the minimum output curve of the lead pump
Activation depths for the pumps and their flow states were designed iteratively with the use of
SSA. The objective for each activation depth was to activate a pump flow state that would
match the required storm design flow without flooding the system, and to prevent a lower-
severity storm from activating a higher-severity storm (e.g. a 2-year storm triggering the 10-
year storm design flow). Beginning with the 2-year storm event, activation depths were
determined that would allow the overall system outflow to match the design 2-year flow from
WWHM through the use of the lead pump, while it was set to minimum output. The same
process was taken for the 10-year storm event, but the depth at which the lead pump switches
to maximum output instead of a pump activating at minimum output. The lag pump’s minimum
output was used to determine if there was a viable activation depth to assist with the 100-year
activation depth that did not require the lag pump to switch into maximum output. It was found
through iterative design that the lag pump did not need to engage in maximum output to assist
with the 100-year storm flow, which will mitigate wear put on the lag pump. If the activation
depths were too low, the pump would cause too much water to flow downstream during the
peak of the storm and if they were too high, it brought the system to flooding or requiring an
additional StormCapture storage unit.
During the design process, activation depths were compared to the depth of the selected
StormCapture stormwater storage system. Increasing and decreasing the amount of storage in
the system greatly affected each activation depth. Each StormCapture unit has an internal
functional depth and width of seven feet, with an internal functional length of 15 feet. Each
unit has a floor area of 105 square feet and a total volume of 735 cubic feet. Storage curves
were created to represent available storage volumes offered by different amounts of
StormCapture units, as necessary. Each storage curve also included the volume offered by
access manholes and service vents, but this space was treated as “emergency-only storage.”
The storage curves are shown as Figure 27.
If the WWHM Water Quality storage volumes for the Cadillac and Buick-GMC sites were
combined into a single storage volume, it would be 0.1699 acre-feet, or 7,400 cubic feet. This
volume would require the installation of ten StormCapture units. While the site has space for
that many StormCapture units, it was determined through iterative SSA design that only five
units were needed in conjunction with the staged pump station.
Figures 28-33 are screenshots from SSA showing the depth of water in the pump station and
the storage vault, the flow through the pump over a 24-hour period, and the total outfall for
the entire expanded project area. The expanded project area includes the frontage
improvements for the new construction and existing building, surfaces directly affected by the
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73
project, as well as the portion of the southeast existing Buick-GMC parking lot that is
unaffected by the project but will still flow through the .
These graphs show that the structures will not overflow for the 2-, 10-, and 100-year return
storm events and that the pump will provide the required water flows. Peak flow for the 2-year
storm of the developed condition from SSA is 0.40cfs, which is approximately 0.01cfs lower
than the WWHM-calculated flow of 0.41cfs. SSA modeling shows the 10-year developed
condition to have a flow of 0.63cfs, which is approximately 0.01cfs lower than the WWHM-
calculated flow of 0.64cfs. Similarly, the peak flow of the developed 100-year storm is 0.94cfs,
which is approximately 0.02cfs less than the WHM-calculated flow of 0.96cfs. These are very
small differences and should not cause problems downstream of the lift station.
Type IA 24-hour storms compiled from historical rainfall data for King County, Washington were
used in the SSA model to calculate surface water for each basin for each design storm event.
Drainage basins are illustrated in the exhibits included at the end of A.5.
Table 3. Pump Total Dynamic Head vs Flow (gpm)
Pump Curve
TDH
(FT)
Single Pump, Min
Flow
Single Pump, Max
Flow
Both Pumps, One Max-
One Min
Both Pumps, Max
Flow
5 138 192 330 384
10 94 164 258 328
15 42 126 168 252
20 0 85 85 170
25 0 40 40 80
30 0 6 6 12
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Figure 23 - Pump Operation Envelope
0
5
10
15
20
25
30
35
0.00 50.00 100.00 150.00 200.00 250.00 300.00 350.00 400.00 450.00TDH (FT)Flow (GPM)
Single Pump, Minimum Flow
Single Pump, Maximum Flow
2-year Storm
10-year Storm
100-year Storm
Both Pumps, One Max-One Min
System Demand Curve
Both Pumps, One Max-One Min
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Figure 24 - Minor Loss Nomograph
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Figure 25 – Minimum Pump Curve Head (ft) vs Flow (cfs)
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Figure 26 - Difference between upper and lower pump curve head (ft) vs flow (cfs)
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Figure 27 - Storage curve for 5 StormCapture units
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Figure 28 - 2-year Total System Inflow, Pump Flow, and System Outflow vs Time
Lead Pump Low-Flow
Peak Flow: 0.25cfs
Total Combined (Pumped and Bypass) Site
Peak Outflow: 0.40cfs
Total Combined (Pumped and Bypass) Site
Peak Inflow: 0.75cfs
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Figure 29 – 2-year Water Depth and Storage Volume for StormCapture units and lift station
StormCapture
Peak Volume: 2100.32 ft3
Lift Station
Peak Volume: 121.42 ft3
StormCapture
Peak Depth: 4.00 ft
Lift Station
Peak Depth: 4.15 ft
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Figure 30 - 10-year Storage Depth, Pump Flow, and System Outflow vs Time
Lead Pump Low-Flow
Peak Flow: 0.28cfs
Total Combined (Pumped and Bypass) Site
Peak Outflow: 0.63cfs
Lead Pump High-Flow
Peak Additional Flow: 0.17cfs
Total Combined (Pumped and Bypass) Site
Peak Inflow: 1.13cfs
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Figure 31 - 10-year Water Depth and Storage Volume for StormCapture units and lift station
StormCapture
Peak Volume: 2856.04 ft3
Lift Station
Peak Volume: 163.46 ft3
StormCapture
Peak Depth: 5.54 ft
Lift Station
Peak Depth: 5.58 ft
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Figure 32 - 100-year Storage Depth, Pump Flow, and System Outflow vs Time
Lead Pump Low-Flow
Peak Flow: 0.27cfs
Total Combined (Pumped and Bypass) Site
Peak Outflow: 0.94cfs
Lag Pump Low-Flow
Peak Flow: 0.22cfs
Lead Pump High-Flow
Peak Additional Flow: 0.18cfs
Total Combined (Pumped and Bypass) Site
Peak Inflow: 1.63cfs
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Figure 33 – 100-year Water Depth and Storage Volume for StormCapture units and lift station
StormCapture
Peak Volume: 3468.52 ft3
Lift Station
Peak Volume: 197.40 ft3
StormCapture
Peak Depth: 6.61 ft
Lift Station
Peak Depth: 6.74 ft
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A.6 Geotechnical Engineering Report
The Geotechnical Report, prepared by Migizi Group, Inc, dated July 8, 2021, is included under
a separate cover.
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A.7 WWHM Reports
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WWHM2012
PROJECT REPORT
___________________________________________________________________
Project Name: 19480 - Brotherton Buick-GMC - Treatment
Site Name: Brotherton Buick-GMC
Site Address: 215 SW 12th St
City : Renton, WA
Report Date: 3/15/2023
Gage : Seatac
Data Start : 1948/10/01
Data End : 2009/09/30
(adjusted) Precip Scale: 0.00
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 : Existing
Bypass: No
GroundWater: No
Pervious Land Use acre
C, Lawn, Flat .22
Pervious Total 0.22
Impervious Land Use acre
Impervious Total 0
Basin Total 0.22
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
MITIGATED LAND USE
Name : Proposed
Bypass: No
GroundWater: No
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Pervious Land Use acre
C, Lawn, Flat .004
Pervious Total 0.004
Impervious Land Use acre
ROOF TOPS FLAT 0.101
PARKING FLAT 0.115
Impervious Total 0.216
Basin Total 0.22
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
___________________________________________________________________
ANALYSIS RESULTS
Stream Protection Duration
___________________________________________________________________
Predeveloped Landuse Totals for POC #1
Total Pervious Area:0.22
Total Impervious Area:0
___________________________________________________________________
Mitigated Landuse Totals for POC #1
Total Pervious Area:0.004
Total Impervious Area:0.216
___________________________________________________________________
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.017328
5 year 0.03143
10 year 0.042905
25 year 0.059793
50 year 0.074091
100 year 0.08985
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.082611
5 year 0.104431
10 year 0.119265
25 year 0.138517
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50 year 0.153257
100 year 0.168361
___________________________________________________________________
Stream Protection Duration
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.036 0.107
1950 0.041 0.115
1951 0.019 0.067
1952 0.008 0.059
1953 0.006 0.064
1954 0.012 0.067
1955 0.013 0.076
1956 0.017 0.075
1957 0.021 0.085
1958 0.012 0.069
1959 0.009 0.070
1960 0.021 0.069
1961 0.015 0.073
1962 0.005 0.063
1963 0.015 0.070
1964 0.016 0.069
1965 0.024 0.088
1966 0.009 0.059
1967 0.041 0.101
1968 0.019 0.115
1969 0.021 0.080
1970 0.014 0.077
1971 0.022 0.092
1972 0.035 0.095
1973 0.007 0.057
1974 0.020 0.084
1975 0.023 0.096
1976 0.015 0.065
1977 0.013 0.070
1978 0.014 0.086
1979 0.005 0.117
1980 0.044 0.106
1981 0.013 0.086
1982 0.039 0.122
1983 0.019 0.099
1984 0.010 0.062
1985 0.014 0.086
1986 0.018 0.075
1987 0.018 0.115
1988 0.006 0.070
1989 0.005 0.087
1990 0.083 0.148
1991 0.052 0.118
1992 0.013 0.062
1993 0.008 0.054
1994 0.005 0.058
1995 0.012 0.076
1996 0.035 0.082
1997 0.021 0.079
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1998 0.016 0.080
1999 0.060 0.164
2000 0.016 0.082
2001 0.004 0.090
2002 0.033 0.105
2003 0.026 0.082
2004 0.041 0.154
2005 0.018 0.070
2006 0.019 0.062
2007 0.077 0.144
2008 0.050 0.116
2009 0.026 0.106
___________________________________________________________________
Stream Protection Duration
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.0827 0.1643
2 0.0770 0.1537
3 0.0602 0.1483
4 0.0517 0.1437
5 0.0505 0.1219
6 0.0440 0.1182
7 0.0411 0.1173
8 0.0410 0.1161
9 0.0405 0.1154
10 0.0389 0.1150
11 0.0364 0.1147
12 0.0352 0.1072
13 0.0352 0.1065
14 0.0331 0.1060
15 0.0258 0.1049
16 0.0258 0.1009
17 0.0239 0.0989
18 0.0229 0.0962
19 0.0224 0.0951
20 0.0214 0.0918
21 0.0213 0.0895
22 0.0213 0.0877
23 0.0210 0.0871
24 0.0196 0.0863
25 0.0194 0.0861
26 0.0191 0.0857
27 0.0189 0.0851
28 0.0187 0.0838
29 0.0183 0.0817
30 0.0181 0.0817
31 0.0177 0.0815
32 0.0175 0.0801
33 0.0161 0.0799
34 0.0158 0.0792
35 0.0157 0.0770
36 0.0154 0.0765
37 0.0150 0.0761
38 0.0149 0.0749
39 0.0142 0.0745
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40 0.0137 0.0727
41 0.0137 0.0704
42 0.0135 0.0702
43 0.0129 0.0700
44 0.0128 0.0698
45 0.0127 0.0697
46 0.0118 0.0688
47 0.0116 0.0688
48 0.0116 0.0685
49 0.0103 0.0672
50 0.0090 0.0670
51 0.0087 0.0649
52 0.0079 0.0641
53 0.0075 0.0632
54 0.0070 0.0625
55 0.0063 0.0621
56 0.0057 0.0619
57 0.0051 0.0593
58 0.0049 0.0585
59 0.0049 0.0581
60 0.0047 0.0572
61 0.0042 0.0535
___________________________________________________________________
Stream Protection Duration
POC #1
The Facility FAILED
Facility FAILED duration standard for 1+ flows.
Flow(cfs) Predev Mit Percentage Pass/Fail
0.0087 3480 57194 1643 Fail
0.0093 2710 52167 1924 Fail
0.0100 2214 47890 2163 Fail
0.0106 1824 43868 2405 Fail
0.0113 1455 40296 2769 Fail
0.0120 1215 36960 3041 Fail
0.0126 977 33965 3476 Fail
0.0133 766 31206 4073 Fail
0.0140 598 28747 4807 Fail
0.0146 467 26501 5674 Fail
0.0153 385 24447 6349 Fail
0.0159 315 22544 7156 Fail
0.0166 250 20805 8322 Fail
0.0173 220 19248 8749 Fail
0.0179 180 17879 9932 Fail
0.0186 153 16578 10835 Fail
0.0192 135 15370 11385 Fail
0.0199 124 14262 11501 Fail
0.0206 116 13267 11437 Fail
0.0212 109 12386 11363 Fail
0.0219 99 11541 11657 Fail
0.0225 91 10712 11771 Fail
0.0232 86 9965 11587 Fail
0.0239 82 9306 11348 Fail
0.0245 78 8727 11188 Fail
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0.0252 76 8164 10742 Fail
0.0258 71 7584 10681 Fail
0.0265 68 7069 10395 Fail
0.0272 66 6624 10036 Fail
0.0278 62 6175 9959 Fail
0.0285 61 5794 9498 Fail
0.0292 57 5450 9561 Fail
0.0298 53 5086 9596 Fail
0.0305 49 4765 9724 Fail
0.0311 48 4470 9312 Fail
0.0318 45 4194 9320 Fail
0.0325 43 3927 9132 Fail
0.0331 38 3681 9686 Fail
0.0338 37 3476 9394 Fail
0.0344 36 3290 9138 Fail
0.0351 35 3121 8917 Fail
0.0358 33 2937 8900 Fail
0.0364 30 2753 9176 Fail
0.0371 30 2592 8640 Fail
0.0377 28 2458 8778 Fail
0.0384 26 2338 8992 Fail
0.0391 24 2205 9187 Fail
0.0397 22 2074 9427 Fail
0.0404 22 1954 8881 Fail
0.0410 19 1838 9673 Fail
0.0417 18 1733 9627 Fail
0.0424 15 1645 10966 Fail
0.0430 15 1549 10326 Fail
0.0437 13 1448 11138 Fail
0.0444 11 1379 12536 Fail
0.0450 11 1303 11845 Fail
0.0457 10 1230 12300 Fail
0.0463 9 1172 13022 Fail
0.0470 9 1095 12166 Fail
0.0477 8 1035 12937 Fail
0.0483 8 984 12300 Fail
0.0490 8 938 11725 Fail
0.0496 7 885 12642 Fail
0.0503 7 854 12200 Fail
0.0510 6 817 13616 Fail
0.0516 6 775 12916 Fail
0.0523 5 740 14800 Fail
0.0529 5 709 14180 Fail
0.0536 5 669 13380 Fail
0.0543 5 631 12620 Fail
0.0549 5 606 12120 Fail
0.0556 5 586 11720 Fail
0.0562 5 558 11160 Fail
0.0569 4 540 13500 Fail
0.0576 4 513 12825 Fail
0.0582 4 489 12225 Fail
0.0589 3 460 15333 Fail
0.0596 3 439 14633 Fail
0.0602 3 423 14100 Fail
0.0609 2 409 20450 Fail
0.0615 2 389 19450 Fail
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0.0622 2 375 18750 Fail
0.0629 2 359 17950 Fail
0.0635 2 344 17200 Fail
0.0642 2 327 16350 Fail
0.0648 2 319 15950 Fail
0.0655 2 307 15350 Fail
0.0662 2 293 14650 Fail
0.0668 2 278 13900 Fail
0.0675 2 269 13450 Fail
0.0681 2 261 13050 Fail
0.0688 2 249 12450 Fail
0.0695 2 239 11950 Fail
0.0701 2 228 11400 Fail
0.0708 2 220 11000 Fail
0.0714 2 211 10550 Fail
0.0721 2 204 10200 Fail
0.0728 2 196 9800 Fail
0.0734 2 184 9200 Fail
0.0741 2 180 9000 Fail
_____________________________________________________
The development has an increase in flow durations
from 1/2 Predeveloped 2 year flow to the 2 year flow
or more than a 10% increase from the 2 year to the 50
year flow.
The development has an increase in flow durations for
more than 50% of the flows for the range of the
duration analysis.
___________________________________________________________________
Water Quality BMP Flow and Volume for POC #1
On-line facility volume: 0.0266 acre-feet
On-line facility target flow: 0.035 cfs.
Adjusted for 15 min: 0.035 cfs.
Off-line facility target flow: 0.0198 cfs.
Adjusted for 15 min: 0.0198 cfs.
___________________________________________________________________
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
Total Volume Infiltrated 0.00 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.
___________________________________________________________________
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BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
100
shall Clear Creek Solutions Inc. be liable for any damages whatsoever (including without limitation to
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BROTHERTON DEALERSHIP
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101
WWHM2012
PROJECT REPORT
___________________________________________________________________
Project Name: 19480 - Brotherton Cadillac Treatment
Site Name: Brotherton Cadillac
Site Address: 209 SW 12th St
City : Renton, WA
Report Date: 3/15/2023
Gage : Seatac
Data Start : 1948/10/01
Data End : 2009/09/30
Precip Scale: 1.00
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 : Existing
Bypass: No
GroundWater: No
Pervious Land Use acre
C, Lawn, Flat .667
Pervious Total 0.667
Impervious Land Use acre
ROOF TOPS FLAT 0.179
SIDEWALKS FLAT 0.034
PARKING FLAT 0.298
Impervious Total 0.511
Basin Total 1.178
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
MITIGATED LAND USE
Name : ProposedDevel
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Bypass: No
GroundWater: No
Pervious Land Use acre
C, Lawn, Flat .109
Pervious Total 0.109
Impervious Land Use acre
ROOF TOPS FLAT 0.374
SIDEWALKS FLAT 0.039
PARKING FLAT 0.656
Impervious Total 1.069
Basin Total 1.178
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
Storm Capture 1 Storm Capture 1
___________________________________________________________________
Name : Storm Capture 1
Facility Name: Storm Capture 1
Dimensions
Depth: 7 ft.
Length : 60 ft.
Width : 7 ft.
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Orifice 1 Diameter: 8 in. Elevation: 0 ft.
Element Flows To:
Outlet 1 Outlet 2
___________________________________________________________________
SCapture Hydraulic Table Stage(feet) Area(ac.) Volume(ac-ft.) Discharge(cfs) Infilt(cfs)
0.0000 0.009 0.000 0.000 0.000
0.0778 0.009 0.000 0.484 0.000
0.1556 0.009 0.001 0.685 0.000
0.2333 0.009 0.002 0.838 0.000
0.3111 0.009 0.003 0.968 0.000
0.3889 0.009 0.003 1.083 0.000
0.4667 0.009 0.004 1.186 0.000
0.5444 0.009 0.005 1.281 0.000
0.6222 0.009 0.006 1.370 0.000
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0.7000 0.009 0.006 1.453 0.000
0.7778 0.009 0.007 1.531 0.000
0.8556 0.009 0.008 1.606 0.000
0.9333 0.009 0.009 1.677 0.000
1.0111 0.009 0.009 1.746 0.000
1.0889 0.009 0.010 1.812 0.000
1.1667 0.009 0.011 1.875 0.000
1.2444 0.009 0.012 1.937 0.000
1.3222 0.009 0.012 1.997 0.000
1.4000 0.009 0.013 2.055 0.000
1.4778 0.009 0.014 2.111 0.000
1.5556 0.009 0.015 2.166 0.000
1.6333 0.009 0.015 2.219 0.000
1.7111 0.009 0.016 2.271 0.000
1.7889 0.009 0.017 2.322 0.000
1.8667 0.009 0.018 2.372 0.000
1.9444 0.009 0.018 2.421 0.000
2.0222 0.009 0.019 2.469 0.000
2.1000 0.009 0.020 2.516 0.000
2.1778 0.009 0.021 2.563 0.000
2.2556 0.009 0.021 2.608 0.000
2.3333 0.009 0.022 2.652 0.000
2.4111 0.009 0.023 2.696 0.000
2.4889 0.009 0.024 2.739 0.000
2.5667 0.009 0.024 2.782 0.000
2.6444 0.009 0.025 2.824 0.000
2.7222 0.009 0.026 2.865 0.000
2.8000 0.009 0.027 2.906 0.000
2.8778 0.009 0.027 2.946 0.000
2.9556 0.009 0.028 2.985 0.000
3.0333 0.009 0.029 3.024 0.000
3.1111 0.009 0.030 3.063 0.000
3.1889 0.009 0.030 3.101 0.000
3.2667 0.009 0.031 3.139 0.000
3.3444 0.009 0.032 3.176 0.000
3.4222 0.009 0.033 3.212 0.000
3.5000 0.009 0.033 3.249 0.000
3.5778 0.009 0.034 3.285 0.000
3.6556 0.009 0.035 3.320 0.000
3.7333 0.009 0.036 3.355 0.000
3.8111 0.009 0.036 3.390 0.000
3.8889 0.009 0.037 3.424 0.000
3.9667 0.009 0.038 3.459 0.000
4.0444 0.009 0.039 3.492 0.000
4.1222 0.009 0.039 3.526 0.000
4.2000 0.009 0.040 3.559 0.000
4.2778 0.009 0.041 3.592 0.000
4.3556 0.009 0.042 3.624 0.000
4.4333 0.009 0.042 3.656 0.000
4.5111 0.009 0.043 3.688 0.000
4.5889 0.009 0.044 3.720 0.000
4.6667 0.009 0.045 3.751 0.000
4.7444 0.009 0.045 3.783 0.000
4.8222 0.009 0.046 3.813 0.000
4.9000 0.009 0.047 3.844 0.000
4.9778 0.009 0.048 3.874 0.000
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104
5.0556 0.009 0.048 3.905 0.000
5.1333 0.009 0.049 3.934 0.000
5.2111 0.009 0.050 3.964 0.000
5.2889 0.009 0.051 3.994 0.000
5.3667 0.009 0.051 4.023 0.000
5.4444 0.009 0.052 4.052 0.000
5.5222 0.009 0.053 4.081 0.000
5.6000 0.009 0.054 4.109 0.000
5.6778 0.009 0.054 4.138 0.000
5.7556 0.009 0.055 4.166 0.000
5.8333 0.009 0.056 4.194 0.000
5.9111 0.009 0.057 4.222 0.000
5.9889 0.009 0.057 4.250 0.000
6.0667 0.009 0.058 4.277 0.000
6.1444 0.009 0.059 4.305 0.000
6.2222 0.009 0.060 4.332 0.000
6.3000 0.009 0.060 4.359 0.000
6.3778 0.009 0.061 4.386 0.000
6.4556 0.009 0.062 4.412 0.000
6.5333 0.009 0.063 4.439 0.000
6.6111 0.009 0.063 4.465 0.000
6.6889 0.009 0.064 4.491 0.000
6.7667 0.009 0.065 4.517 0.000
6.8444 0.009 0.066 4.543 0.000
6.9222 0.009 0.066 4.569 0.000
7.0000 0.009 0.067 4.595 0.000
___________________________________________________________________
___________________________________________________________________
ANALYSIS RESULTS
Stream Protection Duration
___________________________________________________________________
Predeveloped Landuse Totals for POC #1
Total Pervious Area:0.667
Total Impervious Area:0.511
___________________________________________________________________
Mitigated Landuse Totals for POC #1
Total Pervious Area:0.109
Total Impervious Area:1.069
___________________________________________________________________
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.240286
5 year 0.325062
10 year 0.385779
25 year 0.467872
50 year 0.533031
100 year 0.601702
Flow Frequency Return Periods for Mitigated. POC #1
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105
Return Period Flow(cfs)
2 year 0.409806
5 year 0.519353
10 year 0.593973
25 year 0.690961
50 year 0.765324
100 year 0.841598
___________________________________________________________________
Stream Protection Duration
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.349 0.521
1950 0.332 0.554
1951 0.216 0.335
1952 0.148 0.296
1953 0.160 0.317
1954 0.194 0.333
1955 0.210 0.383
1956 0.210 0.379
1957 0.264 0.429
1958 0.185 0.332
1959 0.165 0.336
1960 0.227 0.340
1961 0.218 0.371
1962 0.163 0.312
1963 0.211 0.350
1964 0.192 0.336
1965 0.279 0.451
1966 0.162 0.290
1967 0.336 0.493
1968 0.328 0.518
1969 0.253 0.406
1970 0.223 0.377
1971 0.267 0.444
1972 0.330 0.491
1973 0.142 0.276
1974 0.257 0.417
1975 0.270 0.469
1976 0.198 0.318
1977 0.187 0.343
1978 0.230 0.422
1979 0.290 0.547
1980 0.382 0.600
1981 0.242 0.425
1982 0.391 0.612
1983 0.258 0.499
1984 0.179 0.312
1985 0.245 0.431
1986 0.217 0.370
1987 0.293 0.577
1988 0.165 0.340
1989 0.206 0.388
1990 0.598 0.794
1991 0.434 0.567
1992 0.177 0.309
BROTHERTON DEALERSHIP
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106
1993 0.141 0.267
1994 0.138 0.291
1995 0.210 0.376
1996 0.278 0.444
1997 0.251 0.396
1998 0.211 0.400
1999 0.520 0.803
2000 0.241 0.403
2001 0.224 0.427
2002 0.347 0.545
2003 0.270 0.392
2004 0.476 0.807
2005 0.220 0.360
2006 0.204 0.313
2007 0.540 0.662
2008 0.426 0.557
2009 0.266 0.560
___________________________________________________________________
Stream Protection Duration
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.5979 0.8074
2 0.5400 0.8026
3 0.5196 0.7939
4 0.4761 0.6625
5 0.4340 0.6123
6 0.4256 0.5996
7 0.3912 0.5770
8 0.3824 0.5672
9 0.3491 0.5600
10 0.3472 0.5566
11 0.3356 0.5542
12 0.3324 0.5473
13 0.3302 0.5449
14 0.3285 0.5212
15 0.2930 0.5183
16 0.2897 0.4986
17 0.2791 0.4927
18 0.2775 0.4907
19 0.2700 0.4686
20 0.2698 0.4513
21 0.2666 0.4442
22 0.2663 0.4436
23 0.2642 0.4313
24 0.2577 0.4295
25 0.2570 0.4273
26 0.2527 0.4251
27 0.2513 0.4221
28 0.2447 0.4170
29 0.2420 0.4064
30 0.2413 0.4031
31 0.2298 0.3997
32 0.2266 0.3962
33 0.2244 0.3918
34 0.2230 0.3877
BROTHERTON DEALERSHIP
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35 0.2202 0.3832
36 0.2179 0.3787
37 0.2170 0.3771
38 0.2160 0.3764
39 0.2111 0.3709
40 0.2108 0.3704
41 0.2105 0.3605
42 0.2104 0.3503
43 0.2096 0.3432
44 0.2063 0.3403
45 0.2035 0.3401
46 0.1982 0.3363
47 0.1944 0.3363
48 0.1916 0.3345
49 0.1867 0.3334
50 0.1854 0.3321
51 0.1787 0.3177
52 0.1772 0.3172
53 0.1655 0.3125
54 0.1649 0.3123
55 0.1634 0.3120
56 0.1617 0.3093
57 0.1598 0.2961
58 0.1476 0.2909
59 0.1418 0.2898
60 0.1409 0.2757
61 0.1376 0.2665
___________________________________________________________________
Stream Protection Duration
POC #1
The Facility FAILED
Facility FAILED duration standard for 1+ flows.
Flow(cfs) Predev Mit Percentage Pass/Fail
0.1201 1502 9199 612 Fail
0.1243 1350 8504 629 Fail
0.1285 1209 7786 644 Fail
0.1327 1078 7144 662 Fail
0.1368 975 6594 676 Fail
0.1410 885 6070 685 Fail
0.1452 770 5491 713 Fail
0.1493 704 5050 717 Fail
0.1535 640 4652 726 Fail
0.1577 584 4316 739 Fail
0.1618 539 4004 742 Fail
0.1660 474 3655 771 Fail
0.1702 441 3409 773 Fail
0.1744 408 3161 774 Fail
0.1785 383 2956 771 Fail
0.1827 358 2770 773 Fail
0.1869 326 2588 793 Fail
0.1910 302 2368 784 Fail
0.1952 286 2205 770 Fail
0.1994 264 2055 778 Fail
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108
0.2036 253 1901 751 Fail
0.2077 233 1759 754 Fail
0.2119 210 1650 785 Fail
0.2161 192 1494 778 Fail
0.2202 172 1390 808 Fail
0.2244 155 1314 847 Fail
0.2286 150 1222 814 Fail
0.2327 140 1147 819 Fail
0.2369 135 1083 802 Fail
0.2411 126 1003 796 Fail
0.2453 119 940 789 Fail
0.2494 114 893 783 Fail
0.2536 107 835 780 Fail
0.2578 103 784 761 Fail
0.2619 99 736 743 Fail
0.2661 91 687 754 Fail
0.2703 87 653 750 Fail
0.2745 80 615 768 Fail
0.2786 77 586 761 Fail
0.2828 74 555 750 Fail
0.2870 72 527 731 Fail
0.2911 63 487 773 Fail
0.2953 60 467 778 Fail
0.2995 56 445 794 Fail
0.3036 54 422 781 Fail
0.3078 52 402 773 Fail
0.3120 50 386 772 Fail
0.3162 47 361 768 Fail
0.3203 46 344 747 Fail
0.3245 45 330 733 Fail
0.3287 43 312 725 Fail
0.3328 40 296 740 Fail
0.3370 33 270 818 Fail
0.3412 33 251 760 Fail
0.3454 32 240 750 Fail
0.3495 30 230 766 Fail
0.3537 28 218 778 Fail
0.3579 26 210 807 Fail
0.3620 25 202 808 Fail
0.3662 23 195 847 Fail
0.3704 23 188 817 Fail
0.3745 22 176 800 Fail
0.3787 21 158 752 Fail
0.3829 20 150 750 Fail
0.3871 18 145 805 Fail
0.3912 17 144 847 Fail
0.3954 15 139 926 Fail
0.3996 15 133 886 Fail
0.4037 15 122 813 Fail
0.4079 15 118 786 Fail
0.4121 15 116 773 Fail
0.4163 14 111 792 Fail
0.4204 12 109 908 Fail
0.4246 10 107 1070 Fail
0.4288 9 102 1133 Fail
0.4329 9 96 1066 Fail
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0.4371 8 93 1162 Fail
0.4413 8 87 1087 Fail
0.4454 7 84 1200 Fail
0.4496 7 82 1171 Fail
0.4538 7 74 1057 Fail
0.4580 6 70 1166 Fail
0.4621 5 67 1340 Fail
0.4663 5 66 1320 Fail
0.4705 5 63 1260 Fail
0.4746 5 63 1260 Fail
0.4788 4 61 1525 Fail
0.4830 3 60 2000 Fail
0.4872 3 57 1900 Fail
0.4913 3 54 1800 Fail
0.4955 3 49 1633 Fail
0.4997 3 48 1600 Fail
0.5038 3 48 1600 Fail
0.5080 3 46 1533 Fail
0.5122 3 44 1466 Fail
0.5163 3 41 1366 Fail
0.5205 2 39 1950 Fail
0.5247 2 36 1800 Fail
0.5289 2 34 1700 Fail
0.5330 2 33 1650 Fail
_____________________________________________________
The development has an increase in flow durations
from 1/2 Predeveloped 2 year flow to the 2 year flow
or more than a 10% increase from the 2 year to the 50
year flow.
The development has an increase in flow durations for
more than 50% of the flows for the range of the
duration analysis.
___________________________________________________________________
Water Quality BMP Flow and Volume for POC #1
On-line facility volume: 0.1349 acre-feet
On-line facility target flow: 0.1724 cfs.
Adjusted for 15 min: 0.1724 cfs.
Off-line facility target flow: 0.0974 cfs.
Adjusted for 15 min: 0.0974 cfs.
___________________________________________________________________
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
Storm Capture 1 POC N 160.76 N 0.00
Total Volume Infiltrated 160.76 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
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
110
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
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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. 2005-2023; All Rights Reserved.
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
111
WWHM2012
PROJECT REPORT
___________________________________________________________________
Project Name: 2022-12 19480 Brotherton Full-Site Flow Control
Site Name: Brotherton
Site Address: 215 SW 12th Street
City : Renton
Report Date: 3/15/2023
Gage : Seatac
Data Start : 1948/10/01
Data End : 2009/09/30
(adjusted) Precip Scale: 0.00
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 : Buick-GMC-Predev
Bypass: No
GroundWater: No
Pervious Land Use acre
C, Lawn, Flat .111
Pervious Total 0.111
Impervious Land Use acre
SIDEWALKS FLAT 0.012
PARKING FLAT 0.233
Impervious Total 0.245
Basin Total 0.356
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
Name : Cadillac-Not-Pumped-Predev
Bypass: No
GroundWater: No
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112
Pervious Land Use acre
C, Lawn, Flat .039
Pervious Total 0.039
Impervious Land Use acre
SIDEWALKS FLAT 0.001
PARKING FLAT 0.18
Impervious Total 0.181
Basin Total 0.22
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
Name : Cadillac-Pumped-Predev
Bypass: No
GroundWater: No
Pervious Land Use acre
C, Lawn, Flat .667
Pervious Total 0.667
Impervious Land Use acre
ROOF TOPS FLAT 0.179
SIDEWALKS FLAT 0.034
PARKING FLAT 0.298
Impervious Total 0.511
Basin Total 1.178
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
MITIGATED LAND USE
Name : Buick-GMC-Mit
Bypass: Yes
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113
GroundWater: No
Pervious Land Use acre
C, Lawn, Flat .084
Pervious Total 0.084
Impervious Land Use acre
ROOF TOPS FLAT 0.102
SIDEWALKS FLAT 0.038
PARKING FLAT 0.132
Impervious Total 0.272
Basin Total 0.356
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
Name : Cadillac-Not-Pumped-Mit
Bypass: Yes
GroundWater: No
Pervious Land Use acre
C, Lawn, Flat .006
Pervious Total 0.006
Impervious Land Use acre
SIDEWALKS FLAT 0.032
PARKING FLAT 0.182
Impervious Total 0.214
Basin Total 0.22
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
___________________________________________________________________
Name : Cadillac-Pumped-Mit
Bypass: No
GroundWater: No
Not-Pumped surface conditions
are derived from the Figures at
the end of Section A.5.
BROTHERTON DEALERSHIP
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114
Pervious Land Use acre
C, Lawn, Flat .109
Pervious Total 0.109
Impervious Land Use acre
ROOF TOPS FLAT 0.374
SIDEWALKS FLAT 0.039
PARKING FLAT 0.656
Impervious Total 1.069
Basin Total 1.178
___________________________________________________________________
Element Flows To:
Surface Interflow Groundwater
Storm Capture 4 Storm Capture 4
___________________________________________________________________
Name : Storm Capture 4
Facility Name: Storm Capture 4
Dimensions
Depth: 7 ft.
Length : 60 ft.
Width : 7 ft.
Discharge Structure
Riser Height: 0 ft.
Riser Diameter: 0 in.
Orifice 1 Diameter: 12 in. Elevation: 0 ft.
Element Flows To:
Outlet 1 Outlet 2
___________________________________________________________________
SCapture Hydraulic Table Stage(feet) Area(ac.) Volume(ac-ft.) Discharge(cfs) Infilt(cfs)
0.0000 0.009 0.000 0.000 0.000
0.0778 0.009 0.000 1.089 0.000
0.1556 0.009 0.001 1.541 0.000
0.2333 0.009 0.002 1.887 0.000
0.3111 0.009 0.003 2.179 0.000
0.3889 0.009 0.003 2.436 0.000
0.4667 0.009 0.004 2.669 0.000
0.5444 0.009 0.005 2.883 0.000
0.6222 0.009 0.006 3.082 0.000
0.7000 0.009 0.006 3.269 0.000
0.7778 0.009 0.007 3.446 0.000
0.8556 0.009 0.008 3.614 0.000
Pumped surface conditions
are derived from the Figures
at the end of Section A.5.
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115
0.9333 0.009 0.009 3.775 0.000
1.0111 0.009 0.009 3.929 0.000
1.0889 0.009 0.010 4.077 0.000
1.1667 0.009 0.011 4.220 0.000
1.2444 0.009 0.012 4.359 0.000
1.3222 0.009 0.012 4.493 0.000
1.4000 0.009 0.013 4.623 0.000
1.4778 0.009 0.014 4.750 0.000
1.5556 0.009 0.015 4.873 0.000
1.6333 0.009 0.015 4.994 0.000
1.7111 0.009 0.016 5.111 0.000
1.7889 0.009 0.017 5.226 0.000
1.8667 0.009 0.018 5.338 0.000
1.9444 0.009 0.018 5.449 0.000
2.0222 0.009 0.019 5.556 0.000
2.1000 0.009 0.020 5.662 0.000
2.1778 0.009 0.021 5.766 0.000
2.2556 0.009 0.021 5.868 0.000
2.3333 0.009 0.022 5.969 0.000
2.4111 0.009 0.023 6.067 0.000
2.4889 0.009 0.024 6.164 0.000
2.5667 0.009 0.024 6.260 0.000
2.6444 0.009 0.025 6.354 0.000
2.7222 0.009 0.026 6.447 0.000
2.8000 0.009 0.027 6.538 0.000
2.8778 0.009 0.027 6.629 0.000
2.9556 0.009 0.028 6.718 0.000
3.0333 0.009 0.029 6.805 0.000
3.1111 0.009 0.030 6.892 0.000
3.1889 0.009 0.030 6.978 0.000
3.2667 0.009 0.031 7.062 0.000
3.3444 0.009 0.032 7.146 0.000
3.4222 0.009 0.033 7.229 0.000
3.5000 0.009 0.033 7.310 0.000
3.5778 0.009 0.034 7.391 0.000
3.6556 0.009 0.035 7.471 0.000
3.7333 0.009 0.036 7.550 0.000
3.8111 0.009 0.036 7.628 0.000
3.8889 0.009 0.037 7.706 0.000
3.9667 0.009 0.038 7.782 0.000
4.0444 0.009 0.039 7.858 0.000
4.1222 0.009 0.039 7.933 0.000
4.2000 0.009 0.040 8.008 0.000
4.2778 0.009 0.041 8.082 0.000
4.3556 0.009 0.042 8.155 0.000
4.4333 0.009 0.042 8.227 0.000
4.5111 0.009 0.043 8.299 0.000
4.5889 0.009 0.044 8.371 0.000
4.6667 0.009 0.045 8.441 0.000
4.7444 0.009 0.045 8.511 0.000
4.8222 0.009 0.046 8.581 0.000
4.9000 0.009 0.047 8.650 0.000
4.9778 0.009 0.048 8.718 0.000
5.0556 0.009 0.048 8.786 0.000
5.1333 0.009 0.049 8.853 0.000
5.2111 0.009 0.050 8.920 0.000
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116
5.2889 0.009 0.051 8.986 0.000
5.3667 0.009 0.051 9.052 0.000
5.4444 0.009 0.052 9.118 0.000
5.5222 0.009 0.053 9.182 0.000
5.6000 0.009 0.054 9.247 0.000
5.6778 0.009 0.054 9.311 0.000
5.7556 0.009 0.055 9.374 0.000
5.8333 0.009 0.056 9.438 0.000
5.9111 0.009 0.057 9.500 0.000
5.9889 0.009 0.057 9.563 0.000
6.0667 0.009 0.058 9.624 0.000
6.1444 0.009 0.059 9.686 0.000
6.2222 0.009 0.060 9.747 0.000
6.3000 0.009 0.060 9.808 0.000
6.3778 0.009 0.061 9.868 0.000
6.4556 0.009 0.062 9.928 0.000
6.5333 0.009 0.063 9.988 0.000
6.6111 0.009 0.063 10.04 0.000
6.6889 0.009 0.064 10.10 0.000
6.7667 0.009 0.065 10.16 0.000
6.8444 0.009 0.066 10.22 0.000
6.9222 0.009 0.066 10.28 0.000
7.0000 0.009 0.067 10.33 0.000
___________________________________________________________________
___________________________________________________________________
ANALYSIS RESULTS
Stream Protection Duration
___________________________________________________________________
Predeveloped Landuse Totals for POC #1
Total Pervious Area:0.817
Total Impervious Area:0.937
___________________________________________________________________
Mitigated Landuse Totals for POC #1
Total Pervious Area:0.199
Total Impervious Area:1.555
___________________________________________________________________
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.41146
5 year 0.543838
10 year 0.636972
25 year 0.761139
50 year 0.858486
100 year 0.960094
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.604012
5 year 0.767173
WWHM used to determine full site 2-,
10-, and 100-year flow conditions. SSA
was used to determine the developed
conditions flow rates for the overall
site. Disregard the WWHM Mitigated
condition flow rates for this report.
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
117
10 year 0.878503
25 year 1.023399
50 year 1.134625
100 year 1.248814
___________________________________________________________________
Stream Protection Duration
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.581 0.791
1950 0.535 0.829
1951 0.361 0.495
1952 0.266 0.430
1953 0.288 0.467
1954 0.335 0.492
1955 0.367 0.555
1956 0.364 0.551
1957 0.446 0.631
1958 0.326 0.495
1959 0.303 0.499
1960 0.376 0.506
1961 0.371 0.540
1962 0.291 0.457
1963 0.359 0.514
1964 0.331 0.493
1965 0.468 0.655
1966 0.282 0.424
1967 0.539 0.733
1968 0.567 0.824
1969 0.424 0.593
1970 0.384 0.560
1971 0.458 0.667
1972 0.540 0.714
1973 0.248 0.409
1974 0.435 0.617
1975 0.452 0.689
1976 0.336 0.475
1977 0.319 0.505
1978 0.397 0.617
1979 0.524 0.839
1980 0.620 0.819
1981 0.420 0.625
1982 0.646 0.902
1983 0.458 0.728
1984 0.309 0.458
1985 0.423 0.631
1986 0.364 0.541
1987 0.524 0.839
1988 0.302 0.499
1989 0.378 0.611
1990 0.944 1.152
1991 0.700 0.882
1992 0.306 0.454
1993 0.250 0.389
1994 0.252 0.417
1995 0.368 0.556
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
118
1996 0.451 0.622
1997 0.421 0.584
1998 0.373 0.586
1999 0.872 1.211
2000 0.413 0.594
2001 0.404 0.642
2002 0.576 0.786
2003 0.447 0.586
2004 0.803 1.110
2005 0.370 0.525
2006 0.338 0.461
2007 0.848 1.049
2008 0.687 0.860
2009 0.464 0.780
___________________________________________________________________
Stream Protection Duration
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.9438 1.2112
2 0.8720 1.1522
3 0.8481 1.1097
4 0.8035 1.0495
5 0.7004 0.9020
6 0.6872 0.8820
7 0.6455 0.8601
8 0.6199 0.8394
9 0.5812 0.8391
10 0.5755 0.8289
11 0.5671 0.8245
12 0.5405 0.8187
13 0.5394 0.7907
14 0.5348 0.7859
15 0.5243 0.7796
16 0.5238 0.7332
17 0.4676 0.7282
18 0.4640 0.7141
19 0.4583 0.6888
20 0.4579 0.6672
21 0.4524 0.6552
22 0.4508 0.6415
23 0.4475 0.6309
24 0.4457 0.6308
25 0.4350 0.6247
26 0.4241 0.6222
27 0.4234 0.6173
28 0.4214 0.6169
29 0.4204 0.6107
30 0.4128 0.5942
31 0.4036 0.5927
32 0.3966 0.5863
33 0.3837 0.5857
34 0.3781 0.5841
35 0.3762 0.5600
36 0.3734 0.5557
37 0.3712 0.5549
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
119
38 0.3704 0.5511
39 0.3677 0.5408
40 0.3668 0.5396
41 0.3643 0.5249
42 0.3641 0.5144
43 0.3606 0.5058
44 0.3595 0.5047
45 0.3383 0.4986
46 0.3358 0.4985
47 0.3345 0.4951
48 0.3308 0.4950
49 0.3256 0.4926
50 0.3187 0.4920
51 0.3087 0.4746
52 0.3060 0.4668
53 0.3032 0.4610
54 0.3023 0.4579
55 0.2910 0.4571
56 0.2879 0.4544
57 0.2822 0.4299
58 0.2662 0.4242
59 0.2523 0.4174
60 0.2496 0.4085
61 0.2485 0.3894
___________________________________________________________________
Stream Protection Duration
POC #1
The Facility FAILED
Facility FAILED duration standard for 1+ flows.
Flow(cfs) Predev Mit Percentage Pass/Fail
0.2057 1600 6004 375 Fail
0.2123 1430 5458 381 Fail
0.2189 1293 5024 388 Fail
0.2255 1154 4575 396 Fail
0.2321 1034 4171 403 Fail
0.2387 933 3841 411 Fail
0.2453 839 3523 419 Fail
0.2519 763 3290 431 Fail
0.2585 701 3022 431 Fail
0.2651 636 2787 438 Fail
0.2717 586 2586 441 Fail
0.2783 533 2383 447 Fail
0.2849 500 2220 444 Fail
0.2914 456 2032 445 Fail
0.2980 421 1865 442 Fail
0.3046 387 1730 447 Fail
0.3112 360 1606 446 Fail
0.3178 338 1467 434 Fail
0.3244 318 1354 425 Fail
0.3310 296 1268 428 Fail
0.3376 273 1183 433 Fail
0.3442 257 1080 420 Fail
0.3508 237 1006 424 Fail
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
120
0.3574 219 941 429 Fail
0.3640 207 890 429 Fail
0.3706 187 828 442 Fail
0.3772 172 777 451 Fail
0.3838 159 739 464 Fail
0.3903 151 676 447 Fail
0.3969 143 637 445 Fail
0.4035 132 599 453 Fail
0.4101 125 563 450 Fail
0.4167 118 536 454 Fail
0.4233 109 496 455 Fail
0.4299 105 469 446 Fail
0.4365 101 447 442 Fail
0.4431 98 420 428 Fail
0.4497 91 396 435 Fail
0.4563 84 379 451 Fail
0.4629 80 357 446 Fail
0.4695 72 337 468 Fail
0.4761 71 318 447 Fail
0.4827 70 299 427 Fail
0.4893 65 280 430 Fail
0.4958 63 266 422 Fail
0.5024 61 254 416 Fail
0.5090 57 235 412 Fail
0.5156 56 225 401 Fail
0.5222 54 218 403 Fail
0.5288 50 203 406 Fail
0.5354 43 191 444 Fail
0.5420 40 182 455 Fail
0.5486 38 172 452 Fail
0.5552 35 164 468 Fail
0.5618 33 155 469 Fail
0.5684 32 151 471 Fail
0.5750 30 145 483 Fail
0.5816 29 141 486 Fail
0.5882 27 130 481 Fail
0.5947 25 122 488 Fail
0.6013 24 113 470 Fail
0.6079 23 110 478 Fail
0.6145 22 106 481 Fail
0.6211 20 101 505 Fail
0.6277 20 97 485 Fail
0.6343 18 89 494 Fail
0.6409 17 87 511 Fail
0.6475 15 84 560 Fail
0.6541 15 83 553 Fail
0.6607 15 79 526 Fail
0.6673 14 76 542 Fail
0.6739 13 71 546 Fail
0.6805 11 69 627 Fail
0.6871 11 64 581 Fail
0.6936 10 63 630 Fail
0.7002 10 61 610 Fail
0.7068 7 61 871 Fail
0.7134 7 59 842 Fail
0.7200 7 55 785 Fail
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
121
0.7266 7 53 757 Fail
0.7332 7 52 742 Fail
0.7398 7 47 671 Fail
0.7464 7 45 642 Fail
0.7530 7 45 642 Fail
0.7596 7 42 600 Fail
0.7662 6 41 683 Fail
0.7728 5 39 780 Fail
0.7794 5 36 720 Fail
0.7860 5 33 660 Fail
0.7926 5 31 620 Fail
0.7991 5 31 620 Fail
0.8057 3 30 1000 Fail
0.8123 3 29 966 Fail
0.8189 3 26 866 Fail
0.8255 3 21 700 Fail
0.8321 3 19 633 Fail
0.8387 3 18 600 Fail
0.8453 3 15 500 Fail
0.8519 2 14 700 Fail
0.8585 2 14 700 Fail
_____________________________________________________
The development has an increase in flow durations
from 1/2 Predeveloped 2 year flow to the 2 year flow
or more than a 10% increase from the 2 year to the 50
year flow.
The development has an increase in flow durations for
more than 50% of the flows for the range of the
duration analysis.
___________________________________________________________________
Water Quality BMP Flow and Volume for POC #1
On-line facility volume: 0.1341 acre-feet
On-line facility target flow: 0.1686 cfs.
Adjusted for 15 min: 0.1686 cfs.
Off-line facility target flow: 0.0955 cfs.
Adjusted for 15 min: 0.0955 cfs.
___________________________________________________________________
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
Storm Capture 4 POC N 160.76 N 0.00
Total Volume Infiltrated 160.76 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.
___________________________________________________________________
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
122
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. 2005-2023; All Rights Reserved.
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
123
A.8 SSA Reports
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
124
2-Year Storm Event
Pipes:
Element Description From (Inlet) To (Outlet) Length Inlet Outlet Average Peak Travel Max
ID Node Node Invert Invert Slope Flow Time Flow
Depth /
Elevation Elevation Total
Depth
Ratio
(ft) (ft) (ft) (%) (cfs) (min)
{Storm-Buick-
GMC}.Pipe - (34) (Sto
rm-Buick-GMC)
8" DIP CB51 (Storm-
Buick-GMC)
BIOPOD UND
ERGROUND B
IOFILTER - 4X
4 (Storm-
Buick-GMC)
16.94 19.66 19.48 1.0600 0.09 0.14 0.19
{Storm-Buick-
GMC}.Pipe - (35) (Sto
rm-Buick-GMC)
12" DIP BIOPOD UND
ERGROUND
BIOFILTER - 4
X4 (Storm-
Buick-GMC)
Structure - (42
) (Storm-
Buick-GMC)
58.88 18.98 18.69 0.4900 0.09 0.65 0.13
{Storm-Buick-
GMC}.Pipe - (36) (Sto
rm-Buick-GMC)
6" PVC
SDR35
RDCO01 (Sto
rm-Buick-
GMC)
RDCO02 (Stor
m-Buick-GMC)
45.69 20.59 20.30 0.6300 0.02 0.66 0.16
{Storm-Buick-
GMC}.Pipe - (37) (Sto
rm-Buick-GMC)
6" PVC
SDR35
RDCO02 (Sto
rm-Buick-
GMC)
CB51 (Storm-
Buick-GMC)
29.78 20.30 19.66 2.1500 0.05 0.32 0.21
{Storm-Buick-
GMC}.Pipe - (38) (Sto
rm-Buick-GMC)
6" PVC
SDR35
RDCO03 (Sto
rm-Buick-
GMC)
RDCO02 (Stor
m-Buick-GMC)
46.32 20.93 20.30 1.3600 0.02 0.58 0.15
{Storm-
Cadillac}.ByPass
12" DIP LIFT STATION
(Storm-
Cadillac)
CB-B (Storm-
Cadillac)
10.99 21.00 20.14 7.8500 0.00 0.03
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
125
{Storm-
Cadillac}.Pipe - (100)
(Storm-Cadillac)
12" DIP CB11 (Storm-
Cadillac)
CB-E (Storm-
Cadillac)
27.97 19.35 18.88 1.6800 0.07 0.27 0.15
{Storm-
Cadillac}.Pipe - (101)
(Storm-Cadillac)
12" DIP CB02 (Storm-
Cadillac)
CB03 (Storm-
Cadillac)
39.59 19.62 19.23 0.9800 0.04 0.63 0.10
{Storm-
Cadillac}.Pipe - (103)
(Storm-Cadillac)
12" DIP CB01 (Storm-
Cadillac)
CB02 (Storm-
Cadillac)
69.37 20.30 19.62 0.9800 0.03 0.96 0.07
{Storm-
Cadillac}.Pipe - (114)
(Storm-Cadillac)
4" DIP DDCVA PUM
P STATION (S
torm-
Cadillac)
CB02 (Storm-
Cadillac)
30.44 20.67 20.67 0.0000 0.00 0.00
{Storm-
Cadillac}.Pipe - (115)
(Storm-Cadillac)
6" PVC
SDR35
DDCV ASSEM
BLY (Storm-
Cadillac)
DDCVA PUMP
STATION (Sto
rm-Cadillac)
4.83 16.30 16.23 1.4700 0.00 0.00
{Storm-
Cadillac}.Pipe - (128)
(Storm-Cadillac)
12" CPP Structure - (1
50) (Storm-
Cadillac)
Structure - (82
) (Storm-
Cadillac)
59.35 20.02 19.23 1.3300 0.07 1.48 0.19
{Storm-
Cadillac}.Pipe - (16) (
Storm-Cadillac)
12" CPEP CB10 (Storm-
Cadillac)
CB08 (Storm-
Cadillac)
120.85 17.91 16.73 0.9800 0.08 2.96 0.21
{Storm-
Cadillac}.Pipe - (17) (
1) (Storm-Cadillac)
12" CPEP PRETREATME
NT (Storm-
Cadillac)
BIOPOD UND
ERGROUND B
IOFILTER - 6X
4 (Storm-
Cadillac)
8.00 16.69 16.65 0.5000 0.34 0.07 0.27
{Storm-
Cadillac}.Pipe - (17) (
Storm-Cadillac)
12" CPEP CB08 (Storm-
Cadillac)
PRETREATME
NT (Storm-
Cadillac)
8.00 16.73 16.69 0.5000 0.34 0.08 0.31
{Storm-
Cadillac}.Pipe - (18) (
Storm-Cadillac)
12" CPEP BIOPOD UND
ERGROUND
BIOFILTER - 6
X4 (Storm-
Cadillac)
STORAGE(Sto
rm-Cadillac)
37.00 16.15 15.97 0.4900 0.34 0.29 0.25
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
126
{Storm-
Cadillac}.Pipe - (20) (
Storm-Cadillac)
12" CPEP STORAGE(St
orm-Cadillac)
LIFT STATION(
Storm-
Cadillac)
14.97 10.03 9.82 1.4000 0.48 0.12 1.00
{Storm-
Cadillac}.Pipe - (22) (
Storm-Cadillac)
4" DIP VALVE VAUL
T (Storm-
Cadillac)
FM Angle (Sto
rm-Cadillac)
105.50 20.21 20.31 -0.0900 0.26 0.42 1.00
{Storm-
Cadillac}.Pipe - (23) (
Storm-Cadillac)
6" DIP FM Angle (St
orm-Cadillac)
CB-C (Storm-
Cadillac)
46.10 20.31 20.42 -0.2500 0.25 0.48 0.75
{Storm-
Cadillac}.Pipe - (24) (
Storm-Cadillac)
12" DIP CB03 (Storm-
Cadillac)
CB04 (Storm-
Cadillac)
110.97 19.23 18.14 0.9800 0.11 1.01 0.13
{Storm-
Cadillac}.Pipe - (25) (
Storm-Cadillac)
12" CPEP CB04 (Storm-
Cadillac)
CB05 (Storm-
Cadillac)
51.69 18.14 17.50 1.2400 0.16 0.42 0.15
{Storm-
Cadillac}.Pipe - (26) (
Storm-Cadillac)
12" CPEP CB05 (Storm-
Cadillac)
CB06 (Storm-
Cadillac)
90.63 17.50 17.05 0.5000 0.16 0.87 0.17
{Storm-
Cadillac}.Pipe - (27) (
Storm-Cadillac)
12" CPEP CB06 (Storm-
Cadillac)
CB07 (Storm-
Cadillac)
43.12 17.05 16.83 0.5000 0.16 0.58 0.21
{Storm-
Cadillac}.Pipe - (28) (
Storm-Cadillac)
12" CPEP CB07 (Storm-
Cadillac)
CB08 (Storm-
Cadillac)
21.03 16.83 16.73 0.5000 0.26 0.26 0.29
{Storm-
Cadillac}.Pipe - (34) (
Storm-Cadillac)
12" CPEP CB09 (Storm-
Cadillac)
CB10 (Storm-
Cadillac)
53.43 18.43 17.91 0.9800 0.04 0.75 0.09
{Storm-
Cadillac}.Pipe - (4) (1)
(Storm-Cadillac)
12" DIP CB-B (Storm-
Cadillac)
CB-C (Storm-
Cadillac)
23.55 20.15 19.99 0.6700 0.01 2.07 0.13
{Storm-
Cadillac}.Pipe - (5) (St
orm-Cadillac)
12" DIP CB-C (Storm-
Cadillac)
CB-D (Storm-
Cadillac)
102.92 19.99 19.30 0.6700 0.25 0.66 0.21
{Storm-
Cadillac}.Pipe - (6) (1)
(Storm-Cadillac)
12" DIP CB-E (Storm-
Cadillac)
CB-F (Storm-
Cadillac)
39.25 18.88 18.62 0.6700 0.30 0.29 0.23
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
127
{Storm-
Cadillac}.Pipe - (6) (St
orm-Cadillac)
12" DIP CB-D (Storm-
Cadillac)
CB-E (Storm-
Cadillac)
62.19 19.30 18.88 0.6700 0.25 0.49 0.22
{Storm-
Cadillac}.Pipe - (71) (
Storm-Cadillac)
12" CPP CB11 (Storm-
Cadillac)
Structure - (82
) (Storm-
Cadillac)
77.18 19.35 19.23 0.1600 0.07 1.89 0.18
{Storm-
Cadillac}.Pipe - (80) (
Storm-Cadillac)
15" CPP CB-F (Storm-
Cadillac)
Structure - (92
) (Storm-
Cadillac)
153.33 18.46 17.10 0.8900 0.30 1.01 0.15
Junctions:
Element Description Invert Ground/
Rim
Peak Peak Maximum Maximum Minimum Average Total
ID Elevation (Max) Inflow Lateral HGL Surcharge Freeboard HGL Time
Elevation Inflow Elevation Depth Attained Elevation Flooded
Attained Attained Attained
(ft) (ft) (cfs) (cfs) (ft) (ft) (ft) (ft) (minutes)
BIOPOD UNDERGRO
UND BIOFILTER - 4X
4 (Storm-Buick-GMC)
18.98 23.02 0.09 0.00 19.11 0.00 3.90 19.03 0.00
BIOPOD UNDERGRO
UND BIOFILTER - 6X
4 (Storm-Cadillac)
TYPE 1 16.15 22.65 0.34 0.00 16.43 0.00 6.22 16.25 0.00
CB01 (Storm-
Cadillac)
TYPE 1 20.30 22.50 0.03 0.03 20.36 0.00 2.14 20.33 0.00
CB02 (Storm-
Cadillac)
TYPE 1 19.62 22.18 0.04 0.01 19.70 0.00 2.49 19.65 0.00
CB03 (Storm-
Cadillac)
TYPE 1 17.76 21.62 0.11 0.07 19.35 0.00 2.27 19.13 0.00
CB04 (Storm-
Cadillac)
TYPE 1 17.44 22.83 0.16 0.05 18.28 0.00 4.55 18.11 0.00
CB05 (Storm-
Cadillac)
TYPE 1 15.91 22.31 0.16 0.00 17.67 0.00 4.63 17.33 0.00
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
128
CB06 (Storm-
Cadillac)
TYPE 2-48" 17.05 22.21 0.16 0.00 17.21 0.00 5.00 17.11 0.00
CB07 (Storm-
Cadillac)
TYPE 2-48" 16.83 22.93 0.26 0.11 17.10 0.00 5.84 16.91 0.00
CB08 (Storm-
Cadillac)
TYPE 2-48" 14.93 22.94 0.34 0.00 17.05 0.00 5.88 16.61 0.00
CB09 (Storm-
Cadillac)
TYPE 1 17.21 21.53 0.04 0.04 18.51 0.00 3.02 18.28 0.00
CB10 (Storm-
Cadillac)
TYPE 1 17.40 21.88 0.08 0.04 18.01 0.00 3.86 17.88 0.00
CB11 (Storm-
Cadillac)
TYPE 1 19.35 23.21 0.07 0.00 19.44 0.00 3.77 19.38 0.00
CB51 (Storm-Buick-
GMC)
TYPE 1 19.66 22.85 0.09 0.04 19.79 0.00 3.06 19.71 0.00
CB-B (Storm-
Cadillac)
TYPE 1 20.14 22.80 0.01 0.00 20.20 0.00 2.60 20.15 0.00
CB-C (Storm-Cadillac) TYPE 2-54" 19.99 22.80 0.26 0.00 20.20 0.00 2.61 20.05 0.00
CB-D (Storm-
Cadillac)
TYPE 1 19.30 22.35 0.25 0.00 19.51 0.00 2.84 19.36 0.00
CB-E (Storm-Cadillac) TYPE 1 18.88 22.86 0.30 0.00 19.12 0.00 3.75 18.97 0.00
CB-F (Storm-Cadillac) TYPE 1 18.46 22.59 0.30 0.00 18.65 0.00 3.93 18.53 0.00
DDCV ASSEMBLY (St
orm-Cadillac)
TYPE 1 16.30 23.32 0.00 0.00 16.30 0.00 7.02 16.30 0.00
DDCVA PUMP STATI
ON (Storm-Cadillac)
TYPE 1 15.75 23.25 0.00 0.00 15.75 0.00 7.49 15.75 0.00
FM Angle (Storm-
Cadillac)
Null
Structure
20.31 2500.00 0.26 0.00 20.82 0.00 2479.18 20.49 0.00
PRETREATMENT (Sto
rm-Cadillac)
TYPE 2-48" 16.69 22.79 0.34 0.00 16.99 0.00 5.81 16.79 0.00
RDCO01 (Storm-
Buick-GMC)
6" CO 20.59 24.00 0.02 0.02 20.67 0.00 3.33 20.62 0.00
RDCO02 (Storm-
Buick-GMC)
6" CO 20.30 23.96 0.05 0.00 20.38 0.00 3.58 20.33 0.00
RDCO03 (Storm-
Buick-GMC)
6" CO 20.93 23.96 0.02 0.02 21.00 0.00 2.97 20.95 0.00
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
129
Structure - (150) (Sto
rm-Cadillac)
TYPE 1 20.02 21.30 0.07 0.07 20.11 0.00 1.19 20.06 0.00
Structure - (82) (Stor
m-Cadillac)
TYPE 1 19.23 21.72 0.07 0.00 19.52 0.00 2.20 19.39 0.00
VALVE VAULT (Stor
m-Cadillac)
TYPE 1 20.21 2500.00 0.28 0.00 26.93 0.00 2473.07 20.66 0.00
Subbasins:
Element Description Area Drainage Weighted Total Total Peak Time
ID Node ID Curve Precipitation Runoff Runoff of
Number Concentration
(acres) (inches) (inches) (cfs) (days hh:mm:ss)
BuickEastParking 0.15 Structure - (150) (Storm-Cadillac) 97.80 2.00 1.75 0.07 0 00:05:00
Buick-Frontage 0.14 Structure - (42) (Storm-Buick-GMC) 90.81 2.00 1.15 0.04 0 00:05:00
BuickNorthRoof 0.05 RDCO01 (Storm-Buick-GMC) 98.00 2.00 1.77 0.02 0 00:05:00
Buick-Parking 0.12 CB51 (Storm-Buick-GMC) 94.60 2.00 1.44 0.04 0 00:05:00
BuickSouthRoof 0.05 RDCO03 (Storm-Buick-GMC) 98.00 2.00 1.77 0.02 0 00:05:00
CadillacFrontage 0.04 Structure - (92) (Storm-Cadillac) 98.00 2.00 1.76 0.02 0 00:05:00
CB01 0.06 CB01 (Storm-Cadillac) 98.00 2.00 1.77 0.03 0 00:05:00
CB02 0.03 CB02 (Storm-Cadillac) 93.91 2.00 1.35 0.01 0 00:05:00
CB03 0.13 CB03 (Storm-Cadillac) 97.49 2.00 1.72 0.06 0 00:05:00
CB04 0.12 CB04 (Storm-Cadillac) 95.75 2.00 1.55 0.05 0 00:05:00
CB07 0.25 CB07 (Storm-Cadillac) 96.31 2.00 1.60 0.11 0 00:05:00
CB09 0.10 CB09 (Storm-Cadillac) 95.96 2.00 1.57 0.04 0 00:05:00
CB10 0.09 CB10 (Storm-Cadillac) 96.03 2.00 1.57 0.04 0 00:05:00
CBF 0.01 CB-F (Storm-Cadillac) 98.00 2.00 0.41 0.00 0 00:05:00
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
130
Roof 0.36 STORAGE(Storm-Cadillac) 98.00 2.00 1.77 0.17 0 00:05:00
SW Corner 0.02 Structure - (92) (Storm-Cadillac) 98.00 2.00 1.48 0.01 0 00:05:00
Trash 0.01 CB03 (Storm-Cadillac) 98.00 2.00 0.91 0.01 0 00:05:00
10-Year Storm Event
Pipes:
Element Description From (Inlet) To (Outlet) Length Inlet Inlet Average Peak Travel Max
ID Node Node Invert Invert Slope Flow Time Flow
Depth /
Elevation Offset Total
Depth
Ratio
(ft) (ft) (ft) (%) (cfs) (min)
{Storm-Buick-
GMC}.Pipe - (34) (Sto
rm-Buick-GMC)
8" DIP CB51 (Storm-
Buick-GMC)
BIOPOD UND
ERGROUND B
IOFILTER - 4X
4 (Storm-
Buick-GMC)
16.94 19.66 0.00 1.0600 0.14 0.13 0.24
{Storm-Buick-
GMC}.Pipe - (35) (Sto
rm-Buick-GMC)
12" DIP BIOPOD UN
DERGROUN
D BIOFILTER
- 4X4 (Storm-
Buick-GMC)
Structure - (42
) (Storm-
Buick-GMC)
58.88 18.98 0.00 0.4900 0.14 0.58 0.16
{Storm-Buick-
GMC}.Pipe - (36) (Sto
rm-Buick-GMC)
6" PVC
SDR35
RDCO01 (Sto
rm-Buick-
GMC)
RDCO02 (Stor
m-Buick-GMC)
45.69 20.59 0.00 0.6300 0.03 0.59 0.19
{Storm-Buick-
GMC}.Pipe - (37) (Sto
rm-Buick-GMC)
6" PVC
SDR35
RDCO02 (Sto
rm-Buick-
GMC)
CB51 (Storm-
Buick-GMC)
29.78 20.30 0.00 2.1500 0.07 0.30 0.26
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
131
{Storm-Buick-
GMC}.Pipe - (38) (Sto
rm-Buick-GMC)
6" PVC
SDR35
RDCO03 (Sto
rm-Buick-
GMC)
RDCO02 (Stor
m-Buick-GMC)
46.32 20.93 0.00 1.3600 0.03 0.52 0.17
{Storm-
Cadillac}.ByPass
12" DIP LIFT STATIO
N(Storm-
Cadillac)
CB-B (Storm-
Cadillac)
10.99 21.00 11.18 7.8500 0.00 0.06
{Storm-
Cadillac}.Pipe - (100)
(Storm-Cadillac)
12" DIP CB11 (Storm-
Cadillac)
CB-E (Storm-
Cadillac)
27.97 19.35 0.00 1.6800 0.10 0.34 0.19
{Storm-
Cadillac}.Pipe - (101)
(Storm-Cadillac)
12" DIP CB02 (Storm-
Cadillac)
CB03 (Storm-
Cadillac)
39.59 19.62 0.00 0.9800 0.06 0.56 0.12
{Storm-
Cadillac}.Pipe - (103)
(Storm-Cadillac)
12" DIP CB01 (Storm-
Cadillac)
CB02 (Storm-
Cadillac)
69.37 20.30 0.00 0.9800 0.04 0.86 0.08
{Storm-
Cadillac}.Pipe - (114)
(Storm-Cadillac)
4" DIP DDCVA PUM
P STATION (S
torm-
Cadillac)
CB02 (Storm-
Cadillac)
30.44 20.67 4.91 0.0000 0.00 0.00
{Storm-
Cadillac}.Pipe - (115)
(Storm-Cadillac)
6" PVC
SDR35
DDCV ASSEM
BLY (Storm-
Cadillac)
DDCVA PUMP
STATION (Sto
rm-Cadillac)
4.83 16.30 0.00 1.4700 0.00 0.00
{Storm-
Cadillac}.Pipe - (128)
(Storm-Cadillac)
12" CPP Structure - (1
50) (Storm-
Cadillac)
Structure - (82
) (Storm-
Cadillac)
59.35 20.02 0.00 1.3300 0.10 1.24 0.21
{Storm-
Cadillac}.Pipe - (16) (
Storm-Cadillac)
12" CPEP CB10 (Storm-
Cadillac)
CB08 (Storm-
Cadillac)
120.85 17.91 0.51 0.9800 0.12 2.65 0.27
{Storm-
Cadillac}.Pipe - (17) (
1) (Storm-Cadillac)
12" CPEP PRETREATM
ENT (Storm-
Cadillac)
BIOPOD UND
ERGROUND B
IOFILTER - 6X
4 (Storm-
Cadillac)
8.00 16.69 0.00 0.5000 0.52 0.06 0.33
{Storm-
Cadillac}.Pipe - (17) (
Storm-Cadillac)
12" CPEP CB08 (Storm-
Cadillac)
PRETREATME
NT (Storm-
Cadillac)
8.00 16.73 1.80 0.5000 0.52 0.07 0.39
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
132
{Storm-
Cadillac}.Pipe - (18) (
Storm-Cadillac)
12" CPEP BIOPOD UN
DERGROUN
D BIOFILTER
- 6X4 (Storm-
Cadillac)
STORAGE(Sto
rm-Cadillac)
37.00 16.15 0.00 0.4900 0.52 0.26 0.32
{Storm-
Cadillac}.Pipe - (20) (
Storm-Cadillac)
12" CPEP STORAGE(St
orm-Cadillac)
LIFT STATION
(Storm-
Cadillac)
14.97 10.03 0.06 1.4000 0.47 0.10 1.00
{Storm-
Cadillac}.Pipe - (22) (
Storm-Cadillac)
4" DIP VALVE VAUL
T (Storm-
Cadillac)
FM Angle (Sto
rm-Cadillac)
105.50 20.21 0.00 -0.0900 0.39 0.39 1.00
{Storm-
Cadillac}.Pipe - (23) (
Storm-Cadillac)
6" DIP FM Angle (St
orm-Cadillac)
CB-C (Storm-
Cadillac)
46.10 20.31 0.00 -0.2500 0.40 0.33 0.82
{Storm-
Cadillac}.Pipe - (24) (
Storm-Cadillac)
12" DIP CB03 (Storm-
Cadillac)
CB04 (Storm-
Cadillac)
110.97 19.23 1.47 0.9800 0.16 0.91 0.16
{Storm-
Cadillac}.Pipe - (25) (
Storm-Cadillac)
12" CPEP CB04 (Storm-
Cadillac)
CB05 (Storm-
Cadillac)
51.69 18.14 0.70 1.2400 0.23 0.38 0.19
{Storm-
Cadillac}.Pipe - (26) (
Storm-Cadillac)
12" CPEP CB05 (Storm-
Cadillac)
CB06 (Storm-
Cadillac)
90.63 17.50 1.59 0.5000 0.23 0.77 0.21
{Storm-
Cadillac}.Pipe - (27) (
Storm-Cadillac)
12" CPEP CB06 (Storm-
Cadillac)
CB07 (Storm-
Cadillac)
43.12 17.05 0.00 0.5000 0.23 0.55 0.28
{Storm-
Cadillac}.Pipe - (28) (
Storm-Cadillac)
12" CPEP CB07 (Storm-
Cadillac)
CB08 (Storm-
Cadillac)
21.03 16.83 0.00 0.5000 0.40 0.25 0.38
{Storm-
Cadillac}.Pipe - (34) (
Storm-Cadillac)
12" CPEP CB09 (Storm-
Cadillac)
CB10 (Storm-
Cadillac)
53.43 18.43 1.22 0.9800 0.06 0.66 0.11
{Storm-
Cadillac}.Pipe - (4) (1
) (Storm-Cadillac)
12" DIP CB-B (Storm-
Cadillac)
CB-C (Storm-
Cadillac)
23.55 20.15 0.01 0.6700 0.03 1.03 0.18
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TECHNICAL INFORMATION REPORT
133
{Storm-
Cadillac}.Pipe - (5) (S
torm-Cadillac)
12" DIP CB-C (Storm-
Cadillac)
CB-D (Storm-
Cadillac)
102.92 19.99 0.00 0.6700 0.40 0.66 0.26
{Storm-
Cadillac}.Pipe - (6) (1
) (Storm-Cadillac)
12" DIP CB-E (Storm-
Cadillac)
CB-F (Storm-
Cadillac)
39.25 18.88 0.00 0.6700 0.46 0.26 0.28
{Storm-
Cadillac}.Pipe - (6) (S
torm-Cadillac)
12" DIP CB-D (Storm-
Cadillac)
CB-E (Storm-
Cadillac)
62.19 19.30 0.00 0.6700 0.40 0.46 0.28
{Storm-
Cadillac}.Pipe - (71) (
Storm-Cadillac)
12" CPP CB11 (Storm-
Cadillac)
Structure - (82
) (Storm-
Cadillac)
77.18 19.35 0.00 0.1600 0.10 1.59 0.21
{Storm-
Cadillac}.Pipe - (80) (
Storm-Cadillac)
15" CPP CB-F (Storm-
Cadillac)
Structure - (92
) (Storm-
Cadillac)
153.33 18.46 0.00 0.8900 0.46 0.89 0.19
Junctions:
Element Description Invert Ground/
Rim
Peak Peak Maximum Maximum Minimum Average Total
ID Elevation (Max) Inflow Lateral HGL Surcharge Freeboard HGL Time
Elevation Inflow Elevation Depth Attained Elevation Flooded
Attained Attained Attained
(ft) (ft) (cfs) (cfs) (ft) (ft) (ft) (ft) (minutes)
BIOPOD UNDERGRO
UND BIOFILTER - 4X
4 (Storm-Buick-GMC)
18.98 23.02 0.14 0.00 19.14 0.00 3.87 19.04 0.00
BIOPOD UNDERGRO
UND BIOFILTER - 6X
4 (Storm-Cadillac)
TYPE 1 16.15 22.65 0.52 0.00 16.50 0.00 6.15 16.27 0.00
CB01 (Storm-
Cadillac)
TYPE 1 20.30 22.50 0.04 0.04 20.38 0.00 2.12 20.33 0.00
CB02 (Storm-
Cadillac)
TYPE 1 19.62 22.18 0.06 0.02 19.71 0.00 2.47 19.66 0.00
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
134
CB03 (Storm-
Cadillac)
TYPE 1 17.76 21.62 0.16 0.10 19.38 0.00 2.24 19.18 0.00
CB04 (Storm-
Cadillac)
TYPE 1 17.44 22.83 0.23 0.08 18.31 0.00 4.52 18.14 0.00
CB05 (Storm-
Cadillac)
TYPE 1 15.91 22.31 0.23 0.00 17.71 0.00 4.59 17.41 0.00
CB06 (Storm-
Cadillac)
TYPE 2-48" 17.05 22.21 0.23 0.00 17.25 0.00 4.96 17.12 0.00
CB07 (Storm-
Cadillac)
TYPE 2-48" 16.83 22.93 0.40 0.16 17.18 0.00 5.75 16.93 0.00
CB08 (Storm-
Cadillac)
TYPE 2-48" 14.93 22.94 0.52 0.00 17.14 0.00 5.80 16.69 0.00
CB09 (Storm-
Cadillac)
TYPE 1 17.21 21.53 0.06 0.06 18.52 0.00 3.00 18.33 0.00
CB10 (Storm-
Cadillac)
TYPE 1 17.40 21.88 0.12 0.06 18.04 0.00 3.84 17.91 0.00
CB11 (Storm-
Cadillac)
TYPE 1 19.35 23.21 0.10 0.00 19.45 0.00 3.75 19.39 0.00
CB51 (Storm-Buick-
GMC)
TYPE 1 19.66 22.85 0.14 0.07 19.82 0.00 3.03 19.72 0.00
CB-B (Storm-
Cadillac)
TYPE 1 20.14 22.80 0.03 0.00 20.25 0.00 2.55 20.17 0.00
CB-C (Storm-
Cadillac)
TYPE 2-54" 19.99 22.80 0.40 0.00 20.25 0.00 2.55 20.08 0.00
CB-D (Storm-
Cadillac)
TYPE 1 19.30 22.35 0.40 0.00 19.56 0.00 2.79 19.39 0.00
CB-E (Storm-
Cadillac)
TYPE 1 18.88 22.86 0.46 0.00 19.18 0.00 3.69 19.01 0.00
CB-F (Storm-
Cadillac)
TYPE 1 18.46 22.59 0.46 0.00 18.70 0.00 3.89 18.56 0.00
DDCV ASSEMBLY (St
orm-Cadillac)
TYPE 1 16.30 23.32 0.00 0.00 16.30 0.00 7.02 16.30 0.00
DDCVA PUMP STATI
ON (Storm-Cadillac)
TYPE 1 15.75 23.25 0.00 0.00 15.75 0.00 7.49 15.75 0.00
FM Angle (Storm-
Cadillac)
Null
Structure
20.31 2500.00 0.39 0.00 21.19 0.00 2478.81 20.57 0.00
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TECHNICAL INFORMATION REPORT
135
PRETREATMENT (St
orm-Cadillac)
TYPE 2-48" 16.69 22.79 0.52 0.00 17.06 0.00 5.73 16.82 0.00
RDCO01 (Storm-
Buick-GMC)
6" CO 20.59 24.00 0.03 0.03 20.68 0.00 3.32 20.62 0.00
RDCO02 (Storm-
Buick-GMC)
6" CO 20.30 23.96 0.07 0.00 20.40 0.00 3.56 20.34 0.00
RDCO03 (Storm-
Buick-GMC)
6" CO 20.93 23.96 0.03 0.03 21.01 0.00 2.96 20.96 0.00
Structure - (150) (Sto
rm-Cadillac)
TYPE 1 20.02 21.30 0.10 0.10 20.13 0.00 1.17 20.06 0.00
Structure - (82) (Stor
m-Cadillac)
TYPE 1 19.23 21.72 0.10 0.00 19.56 0.00 2.16 19.41 0.00
VALVE VAULT (Stor
m-Cadillac)
TYPE 1 20.21 2500.00 0.39 0.00 26.92 0.00 2473.08 21.03 0.00
Subbasins:
Element Description Area Drainage Weighted Total Total Peak Time
ID Node ID Curve Precipitation Runoff Runoff of
Number Concentration
(acres) (inches) (inches) (cfs) (days hh:mm:ss)
BuickEastParking 0.15 Structure - (150) (Storm-Cadillac) 97.80 2.85 2.60 0.10 0 00:05:00
Buick-Frontage 0.14 Structure - (42) (Storm-Buick-GMC) 90.81 2.85 1.91 0.07 0 00:05:00
BuickNorthRoof 0.05 RDCO01 (Storm-Buick-GMC) 98.00 2.85 2.62 0.03 0 00:05:00
Buick-Parking 0.12 CB51 (Storm-Buick-GMC) 94.60 2.85 2.26 0.07 0 00:05:00
BuickSouthRoof 0.05 RDCO03 (Storm-Buick-GMC) 98.00 2.85 2.62 0.03 0 00:05:00
CadillacFrontage 0.04 Structure - (92) (Storm-Cadillac) 98.00 2.85 2.61 0.03 0 00:05:00
CB01 0.06 CB01 (Storm-Cadillac) 98.00 2.85 2.62 0.04 0 00:05:00
CB02 0.03 CB02 (Storm-Cadillac) 93.91 2.85 2.17 0.02 0 00:05:00
CB03 0.13 CB03 (Storm-Cadillac) 97.49 2.85 2.56 0.09 0 00:05:00
CB04 0.12 CB04 (Storm-Cadillac) 95.75 2.85 2.38 0.08 0 00:05:00
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136
CB07 0.25 CB07 (Storm-Cadillac) 96.31 2.85 2.44 0.16 0 00:05:00
CB09 0.10 CB09 (Storm-Cadillac) 95.96 2.85 2.40 0.06 0 00:05:00
CB10 0.09 CB10 (Storm-Cadillac) 96.03 2.85 2.41 0.06 0 00:05:00
CBF 0.01 CB-F (Storm-Cadillac) 98.00 2.85 0.97 0.00 0 00:05:00
Roof 0.36 STORAGE(Storm-Cadillac) 98.00 2.85 2.62 0.24 0 00:05:00
SW Corner 0.02 Structure - (92) (Storm-Cadillac) 98.00 2.85 2.58 0.01 0 00:05:00
Trash 0.01 CB03 (Storm-Cadillac) 98.00 2.85 2.12 0.01 0 00:05:00
100-Year Storm Event
Pipes:
Element Description From (Inlet) To (Outlet) Length Inlet Inlet Average Peak Travel Max
ID Node Node Invert Invert Slope Flow Time Flow
Depth /
Elevation Offset Total
Depth
Ratio
(ft) (ft) (ft) (%) (cfs) (min)
{Storm-Buick-
GMC}.Pipe - (34) (St
orm-Buick-GMC)
8" DIP CB51 (Storm-
Buick-GMC)
BIOPOD UND
ERGROUND B
IOFILTER - 4X
4 (Storm-
Buick-GMC)
16.94 19.66 0.00 1.0600 0.20 0.12 0.29
{Storm-Buick-
GMC}.Pipe - (35) (St
orm-Buick-GMC)
12" DIP BIOPOD UND
ERGROUND B
IOFILTER - 4X
4 (Storm-
Buick-GMC)
Structure - (42
) (Storm-
Buick-GMC)
58.88 18.98 0.00 0.4900 0.20 0.52 0.19
{Storm-Buick-
GMC}.Pipe - (36) (St
orm-Buick-GMC)
6" PVC
SDR35
RDCO01 (Stor
m-Buick-GMC)
RDCO02 (Stor
m-Buick-GMC)
45.69 20.59 0.00 0.6300 0.05 0.54 0.23
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
137
{Storm-Buick-
GMC}.Pipe - (37) (St
orm-Buick-GMC)
6" PVC
SDR35
RDCO02 (Stor
m-Buick-GMC)
CB51 (Storm-
Buick-GMC)
29.78 20.30 0.00 2.1500 0.10 0.28 0.32
{Storm-Buick-
GMC}.Pipe - (38) (St
orm-Buick-GMC)
6" PVC
SDR35
RDCO03 (Stor
m-Buick-GMC)
RDCO02 (Stor
m-Buick-GMC)
46.32 20.93 0.00 1.3600 0.05 0.47 0.21
{Storm-
Cadillac}.ByPass
12" DIP LIFT STATION(
Storm-
Cadillac)
CB-B (Storm-
Cadillac)
10.99 21.00 11.18 7.8500 0.00 0.09
{Storm-
Cadillac}.Pipe - (100)
(Storm-Cadillac)
12" DIP CB11 (Storm-
Cadillac)
CB-E (Storm-
Cadillac)
27.97 19.35 0.00 1.6800 0.15 0.34 0.24
{Storm-
Cadillac}.Pipe - (101)
(Storm-Cadillac)
12" DIP CB02 (Storm-
Cadillac)
CB03 (Storm-
Cadillac)
39.59 19.62 0.00 0.9800 0.09 0.50 0.14
{Storm-
Cadillac}.Pipe - (103)
(Storm-Cadillac)
12" DIP CB01 (Storm-
Cadillac)
CB02 (Storm-
Cadillac)
69.37 20.30 0.00 0.9800 0.06 0.78 0.10
{Storm-
Cadillac}.Pipe - (114)
(Storm-Cadillac)
4" DIP DDCVA PUMP
STATION (Sto
rm-Cadillac)
CB02 (Storm-
Cadillac)
30.44 20.67 4.91 0.0000 0.00 0.00
{Storm-
Cadillac}.Pipe - (115)
(Storm-Cadillac)
6" PVC
SDR35
DDCV ASSEM
BLY (Storm-
Cadillac)
DDCVA PUMP
STATION (Sto
rm-Cadillac)
4.83 16.30 0.00 1.4700 0.00 0.00
{Storm-
Cadillac}.Pipe - (128)
(Storm-Cadillac)
12" CPP Structure - (15
0) (Storm-
Cadillac)
Structure - (82
) (Storm-
Cadillac)
59.35 20.02 0.00 1.3300 0.15 1.06 0.25
{Storm-
Cadillac}.Pipe - (16) (
Storm-Cadillac)
12" CPEP CB10 (Storm-
Cadillac)
CB08 (Storm-
Cadillac)
120.85 17.91 0.51 0.9800 0.18 2.49 0.33
{Storm-
Cadillac}.Pipe - (17) (
1) (Storm-Cadillac)
12" CPEP PRETREATME
NT (Storm-
Cadillac)
BIOPOD UND
ERGROUND B
IOFILTER - 6X
4 (Storm-
Cadillac)
8.00 16.69 0.00 0.5000 0.76 0.05 0.40
BROTHERTON DEALERSHIP
TECHNICAL INFORMATION REPORT
138
{Storm-
Cadillac}.Pipe - (17) (
Storm-Cadillac)
12" CPEP CB08 (Storm-
Cadillac)
PRETREATME
NT (Storm-
Cadillac)
8.00 16.73 1.80 0.5000 0.76 0.07 0.48
{Storm-
Cadillac}.Pipe - (18) (
Storm-Cadillac)
12" CPEP BIOPOD UND
ERGROUND B
IOFILTER - 6X
4 (Storm-
Cadillac)
STORAGE(Sto
rm-Cadillac)
37.00 16.15 0.00 0.4900 0.76 0.24 0.52
{Storm-
Cadillac}.Pipe - (20) (
Storm-Cadillac)
12" CPEP STORAGE(Sto
rm-Cadillac)
LIFT STATION(
Storm-
Cadillac)
14.97 10.03 0.06 1.4000 0.70 0.09 1.00
{Storm-
Cadillac}.Pipe - (22) (
Storm-Cadillac)
4" DIP VALVE VAULT
(Storm-
Cadillac)
FM Angle (Sto
rm-Cadillac)
105.50 20.21 0.00 -0.0900 0.60 0.26 1.00
{Storm-
Cadillac}.Pipe - (23) (
Storm-Cadillac)
6" DIP FM Angle (Sto
rm-Cadillac)
CB-C (Storm-
Cadillac)
46.10 20.31 0.00 -0.2500 0.60 0.24 0.89
{Storm-
Cadillac}.Pipe - (24) (
Storm-Cadillac)
12" DIP CB03 (Storm-
Cadillac)
CB04 (Storm-
Cadillac)
110.97 19.23 1.47 0.9800 0.23 0.83 0.19
{Storm-
Cadillac}.Pipe - (25) (
Storm-Cadillac)
12" CPEP CB04 (Storm-
Cadillac)
CB05 (Storm-
Cadillac)
51.69 18.14 0.70 1.2400 0.34 0.34 0.22
{Storm-
Cadillac}.Pipe - (26) (
Storm-Cadillac)
12" CPEP CB05 (Storm-
Cadillac)
CB06 (Storm-
Cadillac)
90.63 17.50 1.59 0.5000 0.34 0.74 0.26
{Storm-
Cadillac}.Pipe - (27) (
Storm-Cadillac)
12" CPEP CB06 (Storm-
Cadillac)
CB07 (Storm-
Cadillac)
43.12 17.05 0.00 0.5000 0.34 0.54 0.36
{Storm-
Cadillac}.Pipe - (28) (
Storm-Cadillac)
12" CPEP CB07 (Storm-
Cadillac)
CB08 (Storm-
Cadillac)
21.03 16.83 0.00 0.5000 0.57 0.23 0.48
{Storm-
Cadillac}.Pipe - (34) (
Storm-Cadillac)
12" CPEP CB09 (Storm-
Cadillac)
CB10 (Storm-
Cadillac)
53.43 18.43 1.22 0.9800 0.09 0.59 0.13
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{Storm-
Cadillac}.Pipe - (4) (1
) (Storm-Cadillac)
12" DIP CB-B (Storm-
Cadillac)
CB-C (Storm-
Cadillac)
23.55 20.15 0.01 0.6700 0.05 0.64 0.25
{Storm-
Cadillac}.Pipe - (5) (S
torm-Cadillac)
12" DIP CB-C (Storm-
Cadillac)
CB-D (Storm-
Cadillac)
102.92 19.99 0.00 0.6700 0.60 0.62 0.33
{Storm-
Cadillac}.Pipe - (6) (1
) (Storm-Cadillac)
12" DIP CB-E (Storm-
Cadillac)
CB-F (Storm-
Cadillac)
39.25 18.88 0.00 0.6700 0.71 0.23 0.36
{Storm-
Cadillac}.Pipe - (6) (S
torm-Cadillac)
12" DIP CB-D (Storm-
Cadillac)
CB-E (Storm-
Cadillac)
62.19 19.30 0.00 0.6700 0.60 0.41 0.35
{Storm-
Cadillac}.Pipe - (71) (
Storm-Cadillac)
12" CPP CB11 (Storm-
Cadillac)
Structure - (82
) (Storm-
Cadillac)
77.18 19.35 0.00 0.1600 0.15 1.35 0.24
{Storm-
Cadillac}.Pipe - (80) (
Storm-Cadillac)
15" CPP CB-F (Storm-
Cadillac)
Structure - (92
) (Storm-
Cadillac)
153.33 18.46 0.00 0.8900 0.71 0.79 0.24
Junctions:
Element Description Invert Ground/
Rim
Peak Peak Maximum Maximum Minimum Average Total
ID Elevation (Max) Inflow Lateral HGL Surcharge Freeboard HGL Time
Elevation Inflow Elevation Depth Attained Elevation Flooded
Attained Attained Attained
(ft) (ft) (cfs) (cfs) (ft) (ft) (ft) (ft) (minutes)
BIOPOD UNDERGRO
UND BIOFILTER - 4X
4 (Storm-Buick-GMC)
18.98 23.02 0.20 0.00 19.18 0.00 3.84 19.06 0.00
BIOPOD UNDERGRO
UND BIOFILTER - 6X
4 (Storm-Cadillac)
TYPE 1 16.15 22.65 0.76 0.00 16.60 0.00 6.04 16.30 0.00
CB01 (Storm-
Cadillac)
TYPE 1 20.30 22.50 0.06 0.06 20.39 0.00 2.11 20.34 0.00
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CB02 (Storm-
Cadillac)
TYPE 1 19.62 22.18 0.09 0.03 19.73 0.00 2.45 19.66 0.00
CB03 (Storm-
Cadillac)
TYPE 1 17.76 21.62 0.23 0.14 19.40 0.00 2.21 19.21 0.00
CB04 (Storm-
Cadillac)
TYPE 1 17.44 22.83 0.34 0.11 18.35 0.00 4.48 18.17 0.00
CB05 (Storm-
Cadillac)
TYPE 1 15.91 22.31 0.34 0.00 17.75 0.00 4.55 17.46 0.00
CB06 (Storm-
Cadillac)
TYPE 2-48" 17.05 22.21 0.34 0.00 17.33 0.00 4.88 17.14 0.00
CB07 (Storm-
Cadillac)
TYPE 2-48" 16.83 22.93 0.57 0.24 17.29 0.00 5.65 16.96 0.00
CB08 (Storm-
Cadillac)
TYPE 2-48" 14.93 22.94 0.76 0.00 17.24 0.00 5.70 16.76 0.00
CB09 (Storm-
Cadillac)
TYPE 1 17.21 21.53 0.09 0.09 18.54 0.00 2.99 18.37 0.00
CB10 (Storm-
Cadillac)
TYPE 1 17.40 21.88 0.18 0.09 18.06 0.00 3.82 17.93 0.00
CB11 (Storm-
Cadillac)
TYPE 1 19.35 23.21 0.15 0.00 19.47 0.00 3.74 19.40 0.00
CB51 (Storm-Buick-
GMC)
TYPE 1 19.66 22.85 0.20 0.10 19.86 0.00 2.99 19.73 0.00
CB-B (Storm-
Cadillac)
TYPE 1 20.14 22.80 0.05 0.00 20.32 0.00 2.48 20.18 0.00
CB-C (Storm-
Cadillac)
TYPE 2-54" 19.99 22.80 0.62 0.00 20.32 0.00 2.49 20.11 0.00
CB-D (Storm-
Cadillac)
TYPE 1 19.30 22.35 0.60 0.00 19.63 0.00 2.72 19.42 0.00
CB-E (Storm-
Cadillac)
TYPE 1 18.88 22.86 0.71 0.00 19.26 0.00 3.60 19.04 0.00
CB-F (Storm-
Cadillac)
TYPE 1 18.46 22.59 0.71 0.01 18.76 0.00 3.83 18.59 0.00
DDCV ASSEMBLY (St
orm-Cadillac)
TYPE 1 16.30 23.32 0.00 0.00 16.30 0.00 7.02 16.30 0.00
DDCVA PUMP STATI
ON (Storm-Cadillac)
TYPE 1 15.75 23.25 0.00 0.00 15.75 0.00 7.49 15.75 0.00
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FM Angle (Storm-
Cadillac)
Null
Structure
20.31 2500.00 0.60 0.00 21.42 0.00 2478.58 20.65 0.00
PRETREATMENT (St
orm-Cadillac)
TYPE 2-48" 16.69 22.79 0.76 0.00 17.15 0.00 5.64 16.85 0.00
RDCO01 (Storm-
Buick-GMC)
6" CO 20.59 24.00 0.05 0.05 20.70 0.00 3.30 20.63 0.00
RDCO02 (Storm-
Buick-GMC)
6" CO 20.30 23.96 0.10 0.00 20.42 0.00 3.54 20.34 0.00
RDCO03 (Storm-
Buick-GMC)
6" CO 20.93 23.96 0.05 0.05 21.02 0.00 2.94 20.97 0.00
Structure - (150) (Sto
rm-Cadillac)
TYPE 1 20.02 21.30 0.15 0.15 20.15 0.00 1.15 20.07 0.00
Structure - (82) (Stor
m-Cadillac)
TYPE 1 19.23 21.72 0.15 0.00 19.60 0.00 2.12 19.43 0.00
VALVE VAULT (Stor
m-Cadillac)
TYPE 1 20.21 2500.00 0.60 0.00 27.09 0.00 2472.91 21.50 0.00
Subbasins:
Element Description Area Drainage Weighted Total Total Peak Time
ID Node ID Curve Precipitation Runoff Runoff of
Number Concentration
(acres) (inches) (inches) (cfs) (days hh:mm:ss)
BuickEastParking 0.15 Structure - (150) (Storm-Cadillac) 97.80 4.00 3.74 0.15 0 00:05:00
Buick-Frontage 0.14 Structure - (42) (Storm-Buick-GMC) 90.81 4.00 3.00 0.11 0 00:05:00
BuickNorthRoof 0.05 RDCO01 (Storm-Buick-GMC) 98.00 4.00 3.76 0.05 0 00:05:00
Buick-Parking 0.12 CB51 (Storm-Buick-GMC) 94.60 4.00 3.39 0.10 0 00:05:00
BuickSouthRoof 0.05 RDCO03 (Storm-Buick-GMC) 98.00 4.00 3.76 0.05 0 00:05:00
CadillacFrontage 0.04 Structure - (92) (Storm-Cadillac) 98.00 4.00 3.76 0.04 0 00:05:00
CB01 0.06 CB01 (Storm-Cadillac) 98.00 4.00 3.76 0.06 0 00:05:00
CB02 0.03 CB02 (Storm-Cadillac) 93.91 4.00 3.30 0.03 0 00:05:00
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CB03 0.13 CB03 (Storm-Cadillac) 97.49 4.00 3.71 0.13 0 00:05:00
CB04 0.12 CB04 (Storm-Cadillac) 95.75 4.00 3.51 0.11 0 00:05:00
CB07 0.25 CB07 (Storm-Cadillac) 96.31 4.00 3.57 0.24 0 00:05:00
CB09 0.10 CB09 (Storm-Cadillac) 95.96 4.00 3.54 0.09 0 00:05:00
CB10 0.09 CB10 (Storm-Cadillac) 96.03 4.00 3.54 0.09 0 00:05:00
CBF 0.01 CB-F (Storm-Cadillac) 98.00 4.00 1.97 0.01 0 00:05:00
Roof 0.36 STORAGE(Storm-Cadillac) 98.00 4.00 3.77 0.35 0 00:05:00
SW Corner 0.02 Structure - (92) (Storm-Cadillac) 98.00 4.00 3.75 0.02 0 00:05:00
Trash 0.01 CB03 (Storm-Cadillac) 98.00 4.00 3.68 0.01 0 00:05:00
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A.9 Water Quality GULDs
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160
A.10 Flygt NP 3085 SH Technical Information
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