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HomeMy WebLinkAboutRS_TIR_240513_v4FES Project 20069 TOC
Stormwater Site Plan/Report
Grant Place Townhomes
1600 Grant Avenue S
Renton, WA 98055
Jurisdiction: City of Renton
Permit #: PR23-000126, LUA23-000283, C23006099
Parcel #202305-9052
For: Siki Chang
Skyline Properties, Inc
50 116th AVE SE, Ste 120
Bellevue, WA, 98004
Prepared: April 3, 2023
Revised: 5/13/2024
Prepared by: R. Elliott, E.I.T.
FES Project #20069
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INREENOT R46937
5/13/2024
SURFACE WATER UTILITY
JFarah 09/03/2024
DEVELOPMENT ENGINEERING
NJanders 09/16/2024
FES Project 20069 Page 2
TABLE OF CONTENTS
1.0 PROJECT OVERVIEW ................................................................................................ 3
Technical Information Report (TIR) Worksheet ........................................................... 4
Vicinity Map ................................................................................................................ 9
2.0 CONDITIONS AND REQUIREMENTS SUMMARY ................................................... 10
2.1 Analysis of the Nine (9) Core Requirements ....................................................... 11
2.2 Analysis of the Special Requirements ................................................................. 13
2.3 Conditions of Approval ........................................................................................ 13
3.0 OFFSITE ANALYSIS ................................................................................................. 14
3.1 Task 1: Define and Map the Study Area. ............................................................. 14
3.2 Task 2: Review All Available Information on the Study Area ............................... 14
3.3 Task 3: Field Inspect the Study Area ................................................................... 15
3.4 Task 4: Describe the Drainage System ............................................................... 15
4.0 FLOW CONTROL, LOW IMPACT DEVELOPMENT (LID) AND WATER QUALITY
FACILITY ANALYSIS AND DESIGN ...................................................................... 18
4.1 VAULT ANALYSIS .............................................................................................. 20
Existing Conditions ................................................................................................... 22
4.2 WATER QUALITY SYSTEM ............................................................................... 23
Proposed Conditions ................................................................................................. 24
5.0 CONVEYANCE SYSTEM ANALYSIS AND DESIGN................................................. 25
5.1 Uniform Flow Analysis Method ............................................................................ 25
5.2 Backflow Analysis Method .................................................................................. 26
5.3 Grate Inlet Capacity Analysis .............................................................................. 29
7.0 OTHER PERMITS ...................................................................................................... 35
8.0 CSWPP ANALYSIS AND DESIGN ............................................................................ 36
9.0 BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
................................................................................................................................ 37
10.0 OPERATIONS AND MAINTENANCE MANUAL ........................................................ 38
Appendix A: Pacific Engineering Downstream Analysis ............................................... 53
Appendix B: Geotechnical Report ................................................................................... 54
Appendix C: As-Built Survey Drawings ........................................................................... 55
Appendix D: Flow Control and Water Quality Calculations ........................................... 56
Appendix E: StormFilter Details....................................................................................... 57
FES Project no. 20069 Page 3
1.0 PROJECT OVERVIEW
This project proposes the construction of eight townhouse buildings on a single 92,828 sf (2.131
ac) parcel (no. 202305-9052) located at 1600 Grant Ave. S, Renton, WA 98055. This project is
the continuation of an expired plat (civil permit no. U16004475); currently, the site is partially
developed with several constructed buildings, building foundations, utilities, and rough-graded
alley.
Stormwater onsite is collected by the onsite storm system and conveyed into a combined
detention/wetvault, which discharges through a Contech StormFilter manhole and into the
municipal storm system within Grant Ave. Low Impact Development (LID) BMPs are generally
infeasible onsite due to unsuitable soils, high/perched groundwater, and the amount of completed
construction onsite. A letter from a licensed geotechnical engineer has been added to the 2005
geotechnical investigation to confirm site conditions and to approve construction to continue as
proposed.
The City of Renton has amended the 2021 King County Stormwater Design Manual (KCSWDM)
to create the 2022 City of Renton Surface Water Design Manual (CoRSWDM), which serves as
the governing document for stormwater management within the city. This report shall serve to
comply with the updated requirements of this manual and the Renton Municipal Code.
FES Project no. 20069 Page 4
Technical Information Report (TIR) Worksheet
FES Project no. 20069 Page 5
FES Project no. 20069 Page 6
FES Project no. 20069 Page 7
FES Project no. 20069 Page 8
FES Project no. 20069 Page 9
Vicinity Map
Scale: NTS
PROJECT
SITE
FES Project no. 20069 Page 10
2.0 CONDITIONS AND REQUIREMENTS SUMMARY
Per KCSWDM Section 1.1, Figure 1.1.2.A: Flow Chart for Determining Type of Drainage Review
Required, this project is required to comply with Full Drainage Review per Section 1.1.2.4:
Therefore, this project must comply with all nine core requirements in Section 1.2 and all five
special requirements in Section 1.3.
FES Project no. 20069 Page 11
2.1 Analysis of the Nine (9) Core Requirements
2.1.1 Core Requirement #1: Discharge at the Natural Location
This project is a continuation of an expired permit, with a previously-designed stormwater
system onsite discharging from the site into the municipal storm system through the
existing manhole in Grant Ave. This project proposes discharge through this system.
Therefore, the existing drainage pattern is maintained under the developed condition. See
Section 3.4 of this report.
FES Project no. 20069 Page 12
2.1.2 Core Requirement #2: Offsite Analysis
See Section 3.0: Offsite Analysis.
2.1.3 Core Requirement #3: Flow Control
Per CORMaps and the CoRSWDM, this project is required to provide flow control, and
must implement the Flow Control Duration Standard matching forested site conditions.
Therefore, the existing/predeveloped condition shall be modeled as forest. See Section
4.0: Flow Control, Low Impact Development (LID), and Water Quality Facility Analysis and
Design.
2.1.4 Core Requirement #4: Conveyance System
Conveyance shall be primarily through 12” CMP pipe; see Section 5.0: Conveyance
System Analysis and Design.
2.1.5 Core Requirement #5: Erosion and Sediment Control
A Temporary Erosion and Sediment Control (TESC) plan is included separately as a part
of this submittal.
2.1.6 Core Requirement #6: Maintenance and Operations
Maintenance and operations instructions and a sample log of maintenance activities are
provided in Section 10.0 of this report.
2.1.7 Core Requirement #7: Financial Guarantees and Liability
Bond quantity analysis will be provided separately at final approval.
2.1.8 Core Requirement #8: Water Quality
Because this project proposes the development of a multifamily project, Enhanced Basic
Water Quality is required per CoRSWDM Section 1.2.8.1(A). Water quality will be provided
by a two-facility treatment train consisting of a combined detention/wet vault and a
ConTech Stormfilter with ZPG filters. See Section 4.2: Water Quality System.
2.1.9 Core Requirement #9: Flow Control BMPs
This project was evaluated per CoRSWDM Section 1.2.9.2.2: Large Lot BMP
Requirements:
1. Full dispersion: Dispersion is not feasible on this project due to insufficient
vegetated flowpath.
2. Full infiltration of roof runoff: Infiltration is not feasible on this project due to
unsuitable soils and high/perched groundwater.
3. Where (1) and (2) are infeasible, the following BMPs must be evaluated for
feasibility:
a. Full infiltration: Infiltration is not feasible on this project due to unsuitable
soils and high/perched groundwater.
b. Limited infiltration: Infiltration is not feasible on this project due to
unsuitable soils and high/perched groundwater.
c. Bioretention: Bioretention is not feasible due to unsuitable soils and
high/perched groundwater.
d. Permeable Pavement: Permeable pavement is not feasible due to
unsuitable soils and high/perched groundwater and slopes greater than 5%.
FES Project no. 20069 Page 13
4. All target surfaces not mitigated by Requirements (1), (2), and (3) above must
be mitigated to the maximum extent feasible using Basic Dispersion.
Dispersion is not feasible due to insufficient vegetated flow path.
5. For projects that will result in an impervious surface coverage on the buildable
portion of the site/lot of less than 45%, flow control BMPs must be applied to
50% of target impervious surfaces. There are no feasible flow control BMPs from
requirements (1), (2), (3), and (4) above. Native Growth Retention Credit shall be
applied to the proposed 2,595 square-foot native growth protection area (NGPA).
6. The soil moisture holding capacity of new pervious surfaces must be
protected in accordance with the soil amendment BMP as detailed in Appendix
C, Section C.2.13. Disturbed soil shall be amended with compost.
7. Any proposed connection of roof downspouts to the local drainage system
must be via a perforated pipe connection as detailed in Appendix C, Section
C.2.11. Roof drain connections shall be composed of perforated pipe.
2.2 Analysis of the Special Requirements
2.2.1 Special Requirement No. 1: Other Adopted Area-Specific Requirements.
• Critical Drainage Areas (CDAs): There are no CDAs adopted in King County at this time.
• Master Drainage Plans (MDPs): This project is not a part of an MDP.
• Basin Plans (BPs): This project is subject to the City of Renton Shoreline Master Program.
• Salmon Conservation Plans (SCPs): This project is subject to the requirements of the
WRIA 9 Salmon Habitat Plan.
• Stormwater Compliance Plans (SWCPs): This project is subject to the provisions of the
2022 King County Stormwater Management Program Plan (SWMP).
• Lake Management Plans (LMPs): No known LMPs apply to this project.
• Hazard Mitigation Plan: This project is subject to the requirements of the King County
FHMP and the City of Renton’s Hazard Mitigation Plan.
• Shared Facility Drainage Plans (SFDPs): This project is not subject to shared facility
drainage requirements.
2.2.2 Special Requirement No. 2: Flood Hazard Area Delineation
There are no flood hazards on or adjacent to the site; see Section 3.2 of this report.
2.2.3 Special Requirement No. 3: Flood Protection Facilities
N/A
2.2.4 Special Requirement No. 4: Source Control
N/A
2.2.5 Special Requirement No. 5: Oil Control
N/A
2.2.6 Special Requirement No. 6: Aquifer Protection Area
N/A
2.3 Conditions of Approval
Reserved.
FES Project no. 20069 Page 14
3.0 OFFSITE ANALYSIS
3.1 Task 1: Define and Map the Study Area.
See the Downstream Map at the end of this section. A level 1 downstream analysis was
performed by pacific engineering design, llc, and is attached to this report as appendix
A.
3.2 Task 2: Review All Available Information on the Study Area
King County iMap was used to review the site and the area approximately ½ mile
downstream:
Category Project Site Within ¼ mi.
downstream
Environmentally Sensitive Areas
Tributary basin (2005 CAO) Lower Lower
Potential landslide hazard areas No No
Potential landslide hazard areas 50-foot buffer No No
Landslide hazards, incorporated KC No No
Potential steep slope hazard areas No No
Basin condition (2005 CAO) Low Low
Shoreline condition (2005 CAO) N/A N/A
Erosion hazard (1990 SAO) Yes No
Seismic hazard (1990 SAO) No No
Coal Mine hazard (1990 SAO) Yes Yes
Stream (1990 SAO) No Unclassified
Wetland (1990 SAO) No No
Sensitive area notice on title No No
Chinook distribution No No
Wildlife network No No
Channel migration hazard areas No No
Flooding info
River gages N/A N/A
Flood photos N/A N/A
River miles from flood patrol map book N/A N/A
River facilities N/A N/A
Flood phases N/A N/A
Elevation certificates N/A N/A
Letter of Map Amendment and Revisions N/A N/A
FEMA cross-sections N/A N/A
FEMA FIRM panels 53033C0979G 53033C0979G
FEMA floodway N/A N/A
FEMA 100-year floodplain N/A N/A
FEMA 500-year floodplain N/A N/A
FEMA area with reduced risk due to levee No No
Regulatory floodplain No No
King County sea level rise risk area No No
Groundwater
Groundwater sources N/A N/A
Groundwater quality sampling sites No No
Groundwater management areas South King County South King County
Areas susceptible to groundwater contamination Low Low
Critical aquifer recharge area No No
Sole source aquifer No No
Wellhead protection areas – one year time of travel No No
Wellhead protection areas – five years time of travel No No
Wellhead protection areas – ten years time of travel Yes Yes
Water service area City of Renton City of Renton
FES Project no. 20069 Page 15
Category Project Site Within ¼ mi.
downstream
Hydrography and Hydrology
Hydrogauges N/A N/A
Lake buoy N/A N/A
Lakes and large rivers N/A N/A
Streams N/A N/A
Drainage basin Black River Black River
Water resource inventory areas Duwamish-Green (09) Duwamish-Green (09)
River Corridor Mapping
Historical Landslides No No
Fans and debris flows No No
Rock fall No No
Deep-seated landslide No No
Shallow debris slides No No
Noxious weeds No No
Stormwater Services
Stormwater Facilities N/A N/A
Drainage studies N/A N/A
Neighborhood drainage projects N/A N/A
Surface water engineering projects N/A N/A
Drainage complaints N/A N/A
Surface Water Design Manual
Flow control N/A N/A
Water quality N/A N/A
The City of Renton’s GIS resources were also reviewed:
Category Project Site Within ¼ mi. downstream
Coalmines Severity: Moderate Severity: Moderate
Erosion Hazard Severity: High Severity: High
Flood N/A N/A
Landslide Hazard Severity: Moderate Severity: Moderate
Regulated Slopes >15%, ≤25% >15%, ≤25%, >25%, ≤40%
Seismic Hazard Areas No No
Seismic Faults Yes Yes
Regulated Shoreline N/A N/A
Wetlands N/A N/A
Wellhead Protection Area N/A N/A
Streams (classified) N/A Thunder Hills Creek
Classification Type: Np – Non-Fish
Water Feature Type: Stream
3.3 Task 3: Field Inspect the Study Area
A site visit was performed by Dean A. Furr of Furr Engineering Services to confirm the findings of
the downstream analysis performed by Pacific Engineering. See Appendix A: Pacific Engineering
Downstream Analysis.
3.4 Task 4: Describe the Drainage System
Site drainage is collected into a vault, which discharges into the municipal storm system in Grant
Ave. Water is discharged through a 15-inch culvert across Grant Ave, then sheet-flows northwest
along a vegetated path. See the downstream map and table at the end of this section.
ABC
D
PROJECT
SITE
ph 206.890.8291
4715 142nd Pl. SW #B,
Edmonds, WA 98026
GRANT PLACE TOWNHOMESDOWNSTREAM MAPRCE
4/1/2024
20069
DOWNSTREAM FLOWPATH
N
STORM STRUCTURE
FES Project no. 20069 Page 17
Downstream Table
Symbol Drainage Component Type,
Name, and Size
Drainage Component
Description Slope
Distance
from site
discharge
Existing
Problems Potential Problems Observations of Field Inspector, Resource
Reviewer, or Resident
See map
Type: sheet flow, swale, stream,
channel, pipe, pond
Size: diameter, surface area
Drainage basin, vegetation,
cover, depth, type of sensitive
area, volume
% ¼ mi =
1,320 ft
Constrictions, under capacity, ponding, overtopping,
flooding, habitat or organism destruction, scouring,
bank sloughing, sedimentation, incision, other erosion
Tributary area, likelihood of problem, overflow
pathways, potential impacts.
A Site discharge — — N/A — Onsite SWPPP measures in place during
construction.
A→B 12” CMP conveyance 28 N/A N/A
B Type 2 storm drain manhole 28 N/A N/A
B→C 15” CMP culvert 96 N/A N/A
C Culvert outlet 96 N/A Damage from wildlife, overgrowth by
vegetation
C→D Sheet flow 1,320 N/A N/A
D Terminus of downstream analysis 1,320 N/A —
FES Project no. 20069 Page 18
4.0 FLOW CONTROL, LOW IMPACT DEVELOPMENT (LID) AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
This project is a continuation of an expired plat and is currently partially-constructed. Refer to civil
permit no. U16004475 for previous site conditions. See the existing Conditions Exhibit at the end
of this section.
Table 1, below, shows a breakdown of proposed project subbasins:
SUBBASINS sf ac
ONSITE 90,186 2.070
ONSITE BYPASS 2,739 0.063
FRONTAGE 2,547 0.058
UPSTREAM BACKYARDS 9,583 0.220
Table 1: Project subbasin breakdown.
The proposed conditions are summarized in the tables below:
ONSITE
WWHM LANDUSE TYPE DESCRIPTION sf ac
BASIN TOTAL DISTURBED AREA 90,186 2.070
IMPERVIOUS TOTAL IMPERVIOUS 63,597 1.460
PGHS 25,756 0.591
ROADS/MOD ROAD 23,330 0.536
DRIVEWAYS/FLAT VAULT ACCESS 2,426 0.056
NON-PGHS 37,841 0.870
ROOF TOPS/FLAT TOWNHOUSE ROOFS 28,171 0.647
SIDEWALKS/FLAT SIDEWALKS 8,562 0.197
SIDEWALKS/FLAT RETAINING WALLS 1,108 0.025
C, LAWN, MOD PERVIOUS (LS) 23,994 0.551
C, FOREST, MOD NGPA 2,595 0.060
Table 2: Proposed onsite conditions area breakdown.
ONSITE BYPASS
WWHM LANDUSE TYPE DESCRIPTION sf ac
BASIN TOTAL DISTURBED AREA 2,739 0.063
IMPERVIOUS TOTAL IMPERVIOUS 1,683 0.039
PGHS 1,310 0.030
ROADS/MOD ROAD 1,310 0.030
NON-PGHS 373 373
SIDEWALKS/MOD SIDEWALKS 373 0.009
C, LAWN, MOD PERVIOUS (LS) 1,056 0.024
Table 3: Proposed onsite bypass area breakdown.
FES Project no. 20069 Page 19
FRONTAGE
WWHM LANDUSE TYPE DESCRIPTION sf ac
BASIN TOTAL DISTURBED AREA 2,547 0.058
IMPERVIOUS TOTAL IMPERVIOUS 1,554 0.036
PGHS 716 0.016
ROADS/FLAT ROAD 716 0.016
NON-PGHS 838 0.019
SIDEWALKS/FLAT SIDEWALKS 838 0.019
C, LAWN, MOD PERVIOUS (LS) 993 0.023
Table 4: Proposed offsite frontage area breakdown.
UPSTREAM
WWHM LANDUSE TYPE DESCRIPTION sf ac
C, LAWN, MOD PERVIOUS (LS) 9,583 0.220
Table 5: Upstream tributary area breakdown.
See the Developed Conditions Exhibit at the end of this section.
WWHM 2012 was used to model the site using the inputs in Table 6, below:
WWHM INPUTS AC
PREDEVELOPED - TOTAL 2.192
C, FOREST, FLAT 0.135
C, FOREST, MOD 1.304
C, FOREST, STEEP 0.752
PREDEVELOPED - UPSTREAM 0.220
C, LAWN, MOD 0.220
DEVELOPED - ONSITE 2.070
C, FOREST, MOD 0.060
C, LAWN, MOD 0.551
ROADS/MOD 0.536
ROOF TOPS/FLAT 0.647
DRIVEWAYS/FLAT 0.056
SIDEWALKS/MOD 0.222
DEVELOPED - BYPASS 0.063
C, LAWN, MOD 0.024
ROADS/MOD 0.030
SIDEWALKS/MOD 0.009
DEVELOPED - FRONTAGE 0.058
C, LAWN, MOD 0.023
ROADS/FLAT 0.016
SIDEWALKS/FLAT 0.019
DEVELOPED - UPSTREAM 0.220
C, LAWN, MOD 0.220
Table 6: WWHM inputs.
The existing (historic) condition is modelled as forest, using hydrologic soil group C. Run-on from
the upstream area and from the frontage improvements to Grant Ave. are considered bypass.
FES Project no. 20069 Page 20
4.1 VAULT ANALYSIS
An onsite storm system, designed by others, has been installed. This system was analyzed in
order to determine the system’s available capacity and to design storm drainage meeting the flow
control and water quality requirements. Table 7, below, summarizes the as-built data analysis,
and the available live and dead storage:
(a) Vault length (ft) 90.08
(b) Vault width (ft): 40.8
(c) Vault area (sf): 3,764
(d) Water quality outlet ie: 290.87
(e) Min. freeboard (ft): 0.5
(f) Min. sediment storage (ft): 0.5
Vault
access
(g) Inside roof
elevation
(h) Floor
elevation
(i) Vault
depth (ft)
(j) Dead storage
depth (ft)
(k) Dead storage
volume (cf)
1 299.71 286.55 13.16 3.82 15,874
2 299.52 286.44 13.08 3.93 16,278
3 299.73 286.21 13.52 4.16 17,123
4 299.71 285.28 14.43 5.09 20,540
5 299.72 285.58 14.14 4.79 19,438
6 299.73 284.92 14.81 5.45 21,863
7 299.71 284.91 14.80 5.46 21,900
8 299.67 284.89 14.78 5.48 21,973
Avg. 299.69 285.60 14.09 4.77 17,535
(m) High water surface elevation: 299.05
(n) Live storage depth (ft): 8.15
(o) Live storage volume (cf): 29,960
Table 7: as-built storage volume calculations.
Values in the table were calculated as follows:
(a) Vault length (ft): As-built vault length.
(b) Vault width (ft): As-built vault width.
(c) Vault area (cf): (a)*(b)
(d) Water quality outlet ie: As-built outlet invert elevation.
(e) Min. freeboard (ft): Minimum required freeboard per CoRSWDM.
(f) Min. sediment storage (ft): Minimum required sediment depth per CoRSWDM.
(g) Inside roof elevation: As-built inside roof elevation.
(h) Floor elevation: As-built floor elevation.
(i) Vault depth (ft): (g) - (h)
(j) Dead storage depth (ft): (d) - (h) - (f)
(k) Dead storage volume (cf): (i)*(c)
(m) High water surface elevation: [minimum (g)] - (d)
(n) Live storage depth (ft): (m) – (d)
(o) Live storage volume (cf): (n)*(c)
Therefore, the existing combined detention/wetvault provides an approximate live storage volume
of 29,960 cf and an average dead storage volume of 17,535 cf.
The proposed detention vault system and outlet riser were modeled in WWHM using the following
parameters:
FES Project no. 20069 Page 21
PROPOSED VAULT SYSTEM
Riser height (ft) 8.15
Width (ft) 90.06
Length (ft) 40.80
Volume (cf) 29,960
Riser diameter (in) 18
Riser type Notched
Notch type Rectangular
Notch height (ft) 1.900
Notch width (ft) 0.010
Orifice diameter (in) at 0 ft elevation 0.910
Orifice diameter (in) at 4 ft elevation 0.980
Table 8: WWHM design parameters.
This vault system shall be sufficient to provide the required level of flow control; see Appendix D:
Flow Control and Water Quality Calculations.
Frontage section and by-pass basin were included as by-pass mitigation as per City of Renton
Storm water manual section 1.2.3.2(E): flow control facility was sized to compensate for the by-
pass areas and inflow from lawn areas above.
Resulted flow frequencies are provided in table 9.
RETURN PERIOD
FLOW FREQUENCY (CFS)
501,
Historical
701,
Unmitigated
801,
Mitigated
2-YEAR 0.0908 0.6917 0.0561
5-YEAR 0.1519 0.9015 0.0840
10-YEAR 0.1965 1.0506 0.1060
25-YEAR 0.2563 1.2508 0.1383
50-YEAR 0.3029 1.4090 0.1658
100-YEAR 0.3509 1.5750 0.1964
Δ100-YEAR 1.2241
Table 9: Historic and Developed flow rates
TO BE USED IN
BACKFLOW
ANALYSIS, TO
SIMILATE VAULT
OVERFLOW
ph 206.890.8291
4715 142nd Pl. SW #B,
Edmonds, WA 98026
GRANT PLACE TOWNHOMESFIGURE XXXX: EXISTING CONDITIONS EXHIBITRCE
3/17/2023
20069
ROOF
ASPHALT (ONSITE)
CONCRETE (ONSITE)
GRAVEL
ASPHALT (OFFSITE)
CONCRETE (OFFSITE)
LEGEND
N
PROPERTY BOUNDARY
DISTURBED AREA
FLAT SLOPE, <5%
MODERATE SLOPE, 5-15%
STEEP SLOPE, >15%
FES Project no. 20069 Page 23
4.2 WATER QUALITY SYSTEM
Enhanced Basic Level Water Quality will be provided by a treatment train of a combined
wet/detention vault and a Stormfilter unit.
WWHM was used to calculate the required water quality volume of 0.2144 ac•ft (9,339 cf); see
Appendix D: Flow Control and Water Quality Calculations. The existing vault provides 17,534 cf
dead storage (see Table 7); therefore, the existing vault shall be sufficient to provide the
required water quality volume for the first stage of the treatment train.
The second stage of the treatment train shall consist of a ConTech StormFilter manhole. This
product is approved for General Use Level for Basic Treatment by the Washington State
Department of Ecology, using either PhosphoSorb or ZPG media. See Appendix E: StormFilter
Details. See table 10 for calculations.
WATER QUALITY DESIGN DATA
Effective Cartridge Height (inches) 12 18 27
Cartridge Flow Rate (gpm/cartridge) 5 7.5 11.3
Cartridge Flow Rate (cfs/cartridge) 0.0134 0.0167 0.0302
WQ flow rate (cfs) 0.0266
Peak flow rate (cfs) (see section 5.1) 0.1153
Required number of cartridges 9 7 4
Provided capacity (cfs) 0.1206 0.1169 0.1208
Table 10: Water quality design
ph 206.890.8291
4715 142nd Pl. SW #B,
Edmonds, WA 98026
RCE
4/1/2024
20069 GRANT PLACE TOWNHOMESDEVELOPED CONDITIONS EXHIBITROOF
ASPHALT
CONCRETE
GRASSCRETE
LEGEND
N
PROPERTY BOUNDARY
SUBBASIN BOUNDARY
OFFSITE
SUBBASIN
ONSITE SUBBASIN
ONSITE BYPASS SUBBASIN
FES Project no. 20069 Page 25
5.0 CONVEYANCE SYSTEM ANALYSIS AND DESIGN
5.1 Uniform Flow Analysis Method
The constructed stormwater conveyance system onsite consists typically of 12” corrugated storm
pipe and was analyzed using Manning’s equation in order to ensure sufficient capacity.
𝑄=1.49
𝑛∗𝐴∗𝑅
ଶ
ଷ ∗𝑆ଵ
ଶ
where
𝑛= Manning’s coefficient = 0.012
𝑄= flow
𝐴= area
𝑅 = hydraulic radius
𝑆= pipe slope
The most constrained pipe in the system shall be considered; see Appendix C: As-Built Survey
drawings. Given:
𝐴= 0.785 sf
𝑅 = 4”
𝑆= 0.041
𝑄=1.49
0.012 ∗ 0.785 ∗(0.25)ଶ
ଷ ∗(0.041)ଵ
ଶ = 7.842 𝑐𝑓𝑠(5.1)
at 100% pipe capacity, and 4.705 cfs at 60% capacity. Given 100-year peak flows of 1.5750 cfs,
each component of the conveyance system is sufficient to convey peak flows at 60% capacity.
Additionally, discharge from the vault must be considered, based upon the most constrained pipe:
𝑄=1.49
0.012 ∗ 0.785 ∗(0.25)
ଶ
ଷ ∗(0.002)
ଵ
ଶ = 1.669 𝑐𝑓𝑠(5.2)
at 100% pipe capacity, and 1.002 cfs at 60% capacity. Therefore, all pipes downstream of the
vault shall have sufficient capacity to convey the peak flows of 0.1964 cfs.
Peak flow to the water quality facility shall consist of peak theoretical flow that can pass through
the orifices on the riser. There are two orifices with thin wall 𝐶ௗ = 0.61.
Orifice 1: Dia. 0.91” at elevation 0.0’ (8.15’ of static head)
𝐴ଵ =𝜋𝑟ଶ = 3.14 ⋅
0.91"
12 ⋅ 2
= 0.0045𝑠𝑓
𝑄ଵ, =𝐶ௗ𝐴ଵඥ2𝑔𝐻= 0.61⋅ 0.0045 ⋅√2 ⋅ 32.17 ⋅ 8.15 = 0.0631 𝑐𝑓𝑠
(5.3)
Orifice 2: Dia. 0.98” at elevation 4.0’ (4.15’ of static head)
𝐴ଶ =𝜋𝑟ଶ = 3.14 ⋅
0.98"
12 ⋅ 2
= 0.0052𝑠𝑓
𝑄ଶ, =𝐶ௗ𝐴ଶඥ2𝑔𝐻= 0.61⋅ 0.0052 ⋅√2 ⋅ 32.17 ⋅ 4.15 = 0.0522 𝑐𝑓𝑠
(5.4)
Total: 𝑄 = 0.0631+ 0.0522 = 0.1153 𝑐𝑓𝑠
FES Project no. 20069 Page 26
6” ROOF DRAIN ANALISYS
Peak 100 years flow from buildings 8, 7 and 6 according to WWHM will be 0.0698 CFS, and 6”
PVC pipe capacity at 100% is 2.35 CFS, and 1.58 CFS at 60% capacity. Therefore, roof drain
conveyance system is sufficient to convey peak flows at 60% capacity.
𝑄=1.49
𝑛∗𝐴∗𝑅
ଶ
ଷ ∗𝑆ଵ
ଶ =1.49
0.012 ∗ 0.196 ∗(0.125)ଶ
ଷ ∗(0.15)ଵ
ଶ = 2.35 𝑐𝑓𝑠
Where: 𝑛= 0.012 − Manning’s coefficient, 𝑄− peak flow, 𝐴= 0.196 𝑆𝐹− area, 𝑅 = 1.5" hydraulic
radius, 𝑆= 0.15 pipe slope.
5.2 Backflow Analysis Method
Backflow analysis was performed for 100 years flow, for each catch basin as per City of Renton
Storm water manual section 4.2.1.2. Flows for each catch basin were calculated with WWHM
2012. Sub-basin division is summarized in table 11. Results are presented in the table 12. Exhibit
with WWHM Printouts is presented at Appendix D.
For the pipe section between the vault and existing street SDMH-1 100 years maximum
unmitigated flow of Q=1.5750 CFS was used.
For the route between the vault and existing street SDMH-1 via storm filter manhole maximum
possible water quality flow of Q=0.1153 CFS was utilized.
# Surface area, AC Q100, CFS TOTAL DRIVEWAY SIDEWALK ROOF PERVIOUS
CB1 0.000 0.000 0.000 0.000 0.000 0.0000
CB2 0.058 0.018 0.017 0.000 0.023 0.0373
CB3 0.335 0.201 0.006 0.090 0.038 0.2603
CB4 0.177 0.028 0.028 0.000 0.121 0.0940
CB6 0.209 0.062 0.000 0.146 0.001 0.1693
CB7 0.042 0.002 0.016 0.000 0.024 0.0231
CB8 0.085 0.051 0.013 0.000 0.021 0.0638
CB9 0.096 0.045 0.002 0.005 0.044 0.0611
CB10 0.095 0.053 0.000 0.027 0.015 0.0748
CB11 0.094 0.051 0.000 0.027 0.015 0.0733
CB12 0.024 0.021 0.001 0.000 0.002 0.0209
CB13 0.121 0.024 0.035 0.000 0.063 0.0700
CB15 0.164 0.000 0.030 0.072 0.063 0.0990
CB16 0.158 0.000 0.035 0.066 0.057 0.0964
CB17 0.144 0.000 0.028 0.066 0.050 0.0886
CB18 0.033 0.000 0.007 0.000 0.025 0.0164
Table 11: Sub-Basins per each catch basin.
CB1CB2CB15CB3CB4CB16CB17CB18CB7CB6CB13CB12CB11CB10CB9CB8BY-PASSYARD DRAINSDIRECTLY TOTHE VAULTTIGHTLINE TO CB3TIGHTLINE TO CB3TIGHTLINE TO CB3DISTANCE BETWEEN CATCH BASINS 381'30'FLAT DWFLAT DW5.4%6.9%8.8%14.9%15.0%8.5%9.1%6.1%7.5%2.9%3.1%14.2%4.1%15.0%ph 206.890.82914715 142nd Pl. SW #B,Edmonds, WA 98026NMFE5/13/202420069GRANT PLACE TOWNHOMES
BACKFLOW ANALISYS EXHIBITROOFASPHALTCONCRETELEGEND
FES Project no. 20069 Page 28
Backflow Analysis Table
JOB NAME: Grant Place Townhomes PREPARED BY: Feliks Matveev
JOB NUMBER: 20069 DESIGN STORM: 100 YEAR
FROM
CB TO CB FLOW,
CFS
PIPE
LENGTH
(FEET)
PIPE
DIA.
(IN)
MANN-
ING'S n
VALUE
OUTLET
ELEV.
(FEET)
INLET
ELEV.
(FEET)
PIPE
AREA
(SQ FT)
FLOW
VELO-
CITY
(FT/SEC)
VELO-
CITY
HEAD
(FEET)
TAIL-
WATER
ELEV.
(FEET)
FRIC-
TION
LOSS
(FEET)
ENTRANCE
HGL ELEV.
(FEET)
ENTRANCE
HEAD
LOSS
(FEET)
EXIT
HEAD
LOSS
(FEET)
OUTLET
CONTROL
ELEV.
(FEET)
INLET
CONTROL
ELEV.
(FEET)
APP-
ROACH
VELO-
CITY
HEAD
(FEET)
BEND
HEAD
LOSS
(FEET)
JUNC-
TION
HEAD
LOSS
(FEET)
HEAD-
WATER
ELEV.
(FEET)
RIM
EL
VLT A7 CB8 0.56 23 12 0.012 288.61 300.63 0.79 0.71 0.01 299.02 0.00 301.63 0.00 0.01 301.64 301.63 0.01 0.01 0.00 301.65 303.51
CB8 CB9 0.49 80 12 0.012 300.63 312.18 0.79 0.63 0.01 301.65 0.01 313.18 0.00 0.01 313.19 313.18 0.00 0.00 0.00 313.18 315.61
CB9 CB10 0.43 85 12 0.012 312.18 315.99 0.79 0.55 0.00 313.18 0.01 316.99 0.00 0.00 317.00 316.99 0.00 0.00 0.00 316.99 319.95
CB10 CB11 0.36 102 12 0.012 315.99 323.97 0.79 0.45 0.00 316.99 0.01 324.97 0.00 0.00 324.97 324.97 0.00 0.00 0.00 324.97 327.12
CB11 CB12 0.28 105 12 0.012 323.97 332.19 0.79 0.36 0.00 324.97 0.01 333.19 0.00 0.00 333.19 333.19 0.00 0.00 0.00 333.19 335.03
CB12 CB13 0.26 42 12 0.012 332.19 336.82 0.79 0.33 0.00 333.19 0.00 337.82 0.00 0.00 337.82 337.82 0.00 0.00 0.00 337.82 340.50
CB13 CB6 0.19 52 12 0.012 336.82 341.04 0.79 0.24 0.00 337.82 0.00 342.04 0.00 0.00 342.04 342.04 0.00 0.00 0.00 342.04 345.11
CB6 CB7 0.02 102 12 0.012 341.04 349.02 0.79 0.03 0.00 342.04 0.00 350.02 0.00 0.00 350.02 350.02 0.00 0.00 0.00 350.02 354.83
VLT A1 CB15 0.39 31 12 0.012 289.21 312.67 0.79 0.50 0.00 299.02 0.00 313.67 0.00 0.00 313.68 313.67 0.00 0.00 0.00 313.67 317.65
CB15 CB16 0.30 101 12 0.012 312.67 323.03 0.79 0.38 0.00 313.67 0.01 324.03 0.00 0.00 324.03 324.03 0.00 0.00 0.00 324.03 325.13
CB15 CB17 0.20 101 12 0.012 312.67 332.34 0.79 0.25 0.00 324.03 0.00 333.34 0.00 0.00 333.34 333.34 0.00 0.00 0.00 333.34 334.47
CB17 CB18 0.11 106 12 0.012 332.34 337.59 0.79 0.14 0.00 333.34 0.00 338.59 0.00 0.00 338.59 338.59 0.00 0.00 0.00 338.59 341.06
CB18 CB4 0.09 55 12 0.012 337.59 337.92 0.79 0.12 0.00 324.03 0.00 338.92 0.00 0.00 338.92 338.92 0.00 0.00 0.00 338.92 340.59
VLT A2 CB1 0.30 33 12 0.012 288.98 302.54 0.79 0.38 0.00 299.02 0.00 303.54 0.00 0.00 303.54 303.54 0.00 0.00 0.00 303.54 307.04
CB1 CB2 0.30 14 12 0.012 302.54 304.50 0.79 0.38 0.00 303.54 0.00 305.50 0.00 0.00 305.50 305.50 0.00 0.00 0.00 305.50 307.00
CB2 CB3 0.26 12 12 0.012 304.50 306.00 0.79 0.33 0.00 305.50 0.00 307.00 0.00 0.00 307.00 307.00 0.00 0.00 0.00 307.00 308.85
VLT1 SFMH1 0.115 48 12 0.012 286.61 288.17 0.79 0.15 0.00 287.61 0.00 289.17 0.00 0.00 289.17 289.17 0.00 0.00 0.00 289.17 294.51
SFMH1 CB14 0.115 16 12 0.012 288.17 288.52 0.79 0.15 0.00 289.17 0.00 289.52 0.00 0.00 289.52 289.52 0.00 0.00 0.00 289.52 295.72
CB14 SDMH1 0.115 28 12 0.012 290.82 290.87 0.79 0.15 289.52 0.00 291.87 0.00 0.00 291.87 291.87 0.00 0.00 0.00 291.87 300.40
VLT1 CB14 1.575 48 12 0.012 286.61 288.37 0.79 0.15 0.00 287.61 0.00 289.37 0.00 0.00 289.37 289.37 0.00 0.00 0.00 289.40 294.51
CB14 SDMH1 1.575 34 12 0.012 288.37 295.37 0.79 0.15 0.00 289.40 0.00 296.57 0.00 0.00 296.57 296.57 0.00 0.00 0.00 296.69 297.70
Table 12: Backwater analysis calculation.
100 YR UNMITIGATED FLOW
SEE SECTION 4.1
MAX WQ FACILITY FLOW
SEE SECTION 5.1
FES Project no. 20069 Page 29
5.3 Grate Inlet Capacity Analysis
To prove that no spills or the by-passes will happen to the Grant Ave from private road we’ve
calculated grates inflow rates with following assumptions:
1. Per RSWDM 4.2.1.2 Installed vanity grates are assumed to be 95% open to account for
possible debris accumulation.
2. Grates will accept the run-off from private road approximately 400 FL long, adjacent
planters, sidewalk, and parking spaces. Roof runoff will be dispersed via splash block and
sheet flow on the pavement.
3. Slopes are up to 15% on the road and up to 30% on the lawn. Cross slope is 2%/.
4. Linear drain will cut off all the remaining and by-passed runoff at the site entrance.
100-year storm flow was obtained with WWHM modeling for the backflow analysis on per catch
basin basis and will be used as peak load. See WWHM report for individual catch basins in
appendix D. In general, we can notice that the peak load will be on the CB-3 from the gutter flow
along the south property line. And there is a possibility that some flow will bypass this grate. Peak
100-yr flow is:
𝑄=0.2603 𝑐𝑟𝑒
City of Renton Stormwater manual in section 4.2.1.2 [page 4-20] specifies Washington State
Department of Transportation (WSDOT) Hydraulics Manual as a reference for the grate’s inflow
capacity calculation. According to WSDOTHM Chapter 5-4.1 [page 5-7] grates on the slope need
to be calculated as per Urban Drainage Desing by FHA [FHWA-HIF-24-006 or HES-22].
We’ll use FHWA-HIF-24-006 section 5.3.1 [HES-22, page 47] to calculate the standard city of
Renton 12” concrete gutter capacity, figure 1.
Figure 1: Gutter as per city of Renton standard details
FES Project no. 20069 Page 30
As gutter slope is the same as pavement slope, we’ll utilize HES-22 equation 5.2 to calculate
water spread capacity:
𝑄=(𝑄𝑛
𝐾𝑢𝑄𝑤1.67𝑄𝐿0.5)
0.375
=(0.2603 ⋅0.014
0.56 ⋅0.021.67 ⋅0.150.5)
0.375
=2.50 𝑒𝑟 (5.4)
Where:
𝑛=0.014 – Manning’s n for the float finished concrete gutter as per HES-22 table 5.3
𝐾𝑢=0.56 – unit conversion constant for CU
𝑄𝑤=2%=0.02 – cross slope
𝑄𝐿=15%=0.15 – longitude slope
Now we can calculate the flow speed at the gutter using HES-22 equation 5.3.
𝑉=2𝐾𝑢
𝑛𝑄𝑤0.67𝑄𝐿0.5𝑄0.67 =2 ⋅0.56
0.014 0.020.67 ⋅0.150.5 ⋅2.50.67 =4.17 𝑒𝑟
𝑟𝑒𝑐(5.5)
City of Renton Standard detail 204.20 specifies vaned grate dimensions as 24” long and 20” wide
for the cast iron detail to cover catch basin, figure 2.
Figure 2: Vaned grate as per city of Renton standard details
FES Project no. 20069 Page 31
We’ll use HES-22 section 7.2.1 [page 92] to estimate the 20”x24” cast iron vaned grate
interception capacity.
Let’s calculate frontal flow to total gutter ration as per equation 7.3:
𝐸0 =𝑄𝑤
𝑄=1 −(1 −(𝑉
𝑄)
2.67
)=1 −(1 −(1.66
2.50)
2.67
)=0.9453 (5.6)
Where:
𝑉=1.66 𝑒𝑟 – grate inlet width perpendicular to the gutter as per standard detail.
We can calculate the frontal flow efficiency with equation 7.5:
𝑄𝑑=1 −𝐾𝑢(𝑉−𝑉0)=1 −0.09(4.17 −6)=1.165 →𝑄𝑑=1 (5.7)
Where:
𝑉=6 𝑒𝑟/𝑟 – splash-over velocity as per HES-22, figure 7.8, see figure 3.
𝐾𝑢=0.09 – unit conversion constant for CU
Figure 3: Splash-over velocities as per HES-22
We can calculate the ratio of side flow intercepted with HES-22 equation 7.6:
FES Project no. 20069 Page 32
𝑄𝑠=1
(1 +𝐾𝑢𝑉1.8
𝑄𝑤𝐾2.3 )
=1
(1 +0.15 ⋅4.171.8
0.02 ⋅22.3 )
=0.0333 (5.8)
Total grate inlet efficiency is expressed as per HES-22 equation 7.7:
𝐸=𝑄𝑑𝐸0 +𝑄𝑠(1 −𝐸0)=1 ⋅0.9453 +0.0333(1 −0.9453)=0.9471 (5.9)
Therefore, the flow that will by-pass CB-3 is:
𝑄𝑎𝑝=𝑄(1 −𝐸)=0.2603(1 −0.9471)=0.0138 𝑐𝑒𝑟(5.10)
As per city of Renton standard detail 101.1, figure 4, there is a 1/2" recess around the inlet grate.
“For locally depressed inlets, the quantity of flow reaching the inlet depends on the upstream
gutter section geometry and not the locally depressed section geometry.” [HEC-22, Section 7.2,
page 92]
Figure 4: Grate and gutter relative positions
By-pass flow will be added to CB-2 10 ft downstream of CB-3.
𝑄𝐵𝐵2
𝑑𝑢𝑘𝑘=𝑄𝐵𝐵2 +𝑄𝑎𝑝=0.0373 +0.0138 =0.0510 𝑐𝑒𝑟(5.11)
Flow spread will be equal to:
FES Project no. 20069 Page 33
𝑄=(𝑄𝑛
𝐾𝑢𝑄𝑤1.67𝑄𝐿0.5)
0.375
=(0.0510 ⋅0.014
0.56 ⋅0.021.67 ⋅0.150.5)
0.375
=1.359 𝑒𝑟<𝑉=1.66 𝑒𝑟(5.12)
Flow speed will be equal to:
𝑉=2𝐾𝑢
𝑛𝑄𝑤0.67𝑄𝐿0.5𝑄0.67 =2 ⋅0.56
0.014 0.020.67 ⋅0.150.5 ⋅1.3590.67 =2.77 𝑒𝑟
𝑟𝑒𝑐<𝑉0 =6 𝑒𝑟
𝑟𝑒𝑐(5.13)
Flow speed is lower than critical speed of 6 ft\sec. that equates to frontal interception efficiency
of 𝑄𝑑=1. Therefore CB-2 grate won’t have splash over effect and will have enough capacity to
intercept all the runoff and avoid flooding Grant AVE.
Our proposal to mitigate the possibility of flooding Grant Ave can be describe as the following:
1. Install CB-3 at the southwestern corner of the parcel, at the gutter, edges of the structure
to be no less than 10’ from ex. water main, 5’ from the edge of existing sewer pipe and
with CB-4 390 LF upstream. CB-3 will serve as a main intake point for the sheet flow from
the Southern part of the private Grant circle. The intake capacity of this single CB is
enough to intercept 95% of the flow.
2. Install CB-2 at the curb, 10 FL downstream of CB-3. CB-2 grate has enough capacity to
intercept flow that bypass CB-3.
3. Adjacent to CB-2 install 12” linear drain across Grant circle, 30 LF, perpendicular to the
street alignment. The northern end of linear drain will be elevated higher, and the southern
end will follow proposed slope of the street at 2% to CB-2. As the peak flow spread to CB-
2 is less than CD-2 grate width, such linear drain is utilized only to collect occasional runoff
from the pavement upstream.
Reticuline grate of 12” wide will have a splash over speed of 2 ft\sec (HES-22, fig.3). Even
with a peak flow of 𝑄𝐵𝐵2 =0.0373 𝑐𝑒𝑟 distributed over the 30 FL of linear drain length, with
peak speed of 2 ft\s, the resulting runoff water layer thickness will be:
𝑄=𝐻𝐾𝑉→𝐻=𝑄
𝐾𝑉=0.0373
30 ⋅2 =0.0006𝑒𝑟=0.00005=1
2000"≈0 (5.14)
Therefore, the proposed linear drain has enough capacity to intercept the flow upstream
as there is not enough flow to result substantial water layer at high speed to splash over
the grate.
4. CB-1 remains at the existing location albeit rim elevation will be adjusted to the proposed
grading. Due to location at local high point, it won’t intercept any flow.
5. CB-4 will be installed upstream and will be connected to the drainage system that runs at
the middle of the parcel.
FES Project no. 20069 Page 34
6.0 SPECIAL REPORTS AND STUDIES
Geotechnical Engineering Evaluation prepared by Nelson Geotechnical Associates,
dated June 10, 2005. Attached to this report as Appendix B.
FES Project no. 20069 Page 35
7.0 OTHER PERMITS
Development: PR23-000126
Land Use: LUA23-000283
Utility construction permit: U16004475 (for previous work, now expired)
C23006099
Building (Multi-family)
Building (retaining walls >4ft height)
NPDES: WAR304993, expires 12/31/2025
FES Project no. 20069 Page 36
8.0 CSWPP ANALYSIS AND DESIGN
A Stormwater Pollution and Prevention Plan (SWPPP) is submitted separately per the Department
of Ecology. The requirements of the KCSWDM are satisfied as follows:
1. Clearing limits. Clearing limits are delineated on the Temporary Erosion and Sediment Control Plan
and shall be marked onsite with high-visibility fencing.
2. Cover measures. Temporary and permanent cover measures shall be provided to protect disturbed
areas, e.g., plastic covering, hydroseeding, etc.
3. Perimeter protection. Silt fencing shall be used to filter sediment downstream of disturbed areas.
4. Traffic area stabilization. A stabilized construction entrance has been constructed.
5. Sediment retention: The proposed vault is being used to collect sediment during construction. Silt
fencing shall provide sediment retention at the perimeter of the site.
6. Surface water collection. The proposed vault shall be used to collect surface water.
7. Dewatering control. Dewatering is not anticipated as a part of this project.
8. Dust control. Dust control shall be provided by sprinkling, if required.
9. Flow control. Flow control shall be provided by the proposed vault.
10. Control pollutants: The following BMPs shall be employed to control pollutants, per KCSWDM D.2.2:
• Concrete handling
• Concrete washout area
• Sawcutting and surfacing pollution prevention
• Material delivery, storage, and containment
• pH control for high pH water
• Maintain protective BMPs
• Manage the project
11. Protect existing and proposed flow control BMPs. This project does not include existing or proposed
flow control BMPs requiring protection.
12. Maintain BMPs. Maintenance of BMPs shall be the responsibility of the Certified Erosion and
Sediment Control Lead (CESCL), to be appointed by the contractor.
13. Manage the project. Coordination and timing of site development activities relative to ESC concerns
shall be the responsibility of the CESCL.
During the wet season (October 1 to April 30) any site with exposed soils shall be subject to the "Wet
Season Requirements" contained in the ESC Standards. In addition to the ESC cover measures, these
provisions include covering any newly-seeded areas with mulch and seeding as much disturbed area as
possible during the first week of October to provide grass cover for the wet season.
Prior to obtaining final construction approval, the site shall be stabilized, structural ESC measures (such
as silt fences and sediment traps) shall be removed, and drainage facilities shall be cleaned as specified in
the ESC Standards.
FES Project no. 20069 Page 37
9.0 BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
Submitted separately.
FES Project no. 20069 Page 38
10.0 OPERATIONS AND MAINTENANCE MANUAL
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APPENDIX A: PACIFIC ENGINEERING DOWNSTREAM ANALYSIS
FES Project no. 20069 Page 54
APPENDIX B: GEOTECHNICAL REPORT
Cobalt Geosciences, LLC
P.O. Box 82243
Kenmore, Washington 98028
www.cobaltgeo.com (206) 331-1097
March 3, 2023
Satwant Singh
pmvrsingh@gmail.com
RE: Permit Renewal
Proposed Townhomes
1600 Grant Avenue South
Renton, Washington
In accordance with your authorization, Cobalt Geosciences, LLC has prepared this letter to
discuss permit renewal.
We note that much of the planned construction is nearly completed. It is our opinion that the
construction can continue per plan. Based on our observations at the site and observations
during periodic site visits during grading, we recommend routing runoff from impervious
surfaces to the detention system.
Infiltration systems are not feasible at this site due to several factors. These include the presence
of glacial till soils which are nearly impermeable and act as an aquitard; location and elevations of
new buildings (possible intrusion behind walls and into buildings); presence of shallow perched
groundwater in many areas (zero to minimal clearance above groundwater); presence of newer
structural fills over the native soils (not suitable to infiltrate into fills), and slope magnitudes
generally in excess of 15 percent in most locations.
We anticipate that final landscaping and any additional planned grading/construction will occur
per the approved plans during the upcoming dry grading season.
Sincerely,
Cobalt Geosciences, LLC
Phil Haberman, PE, LG, LEG 3/3/2023
Principal
PH/sc
FES Project no. 20069 Page 55
APPENDIX C: AS-BUILT SURVEY DRAWINGS
TYEE
SURVEYORS
WWHM2012
PROJECT REPORT
VAULT
20069 - exist. vault 3/19/2024 4:35:04 PM Page 2
General Model Information
WWHM2012 Project Name:20069 - exist. vault
Site Name:Grant Avenue Townhomes
Site Address:1600 Grant Ave S
City:Renton, WA
Report Date:3/19/2024
Gage:Seatac
Data Start:1948/10/01
Data End:2009/09/30
Timestep:15 Minute
Precip Scale:1.000
Version Date:2023/01/27
Version:4.2.19
POC Thresholds
Low Flow Threshold for POC1:50 Percent of the 2 Year
High Flow Threshold for POC1:50 Year
20069 - exist. vault 3/19/2024 4:35:04 PM Page 3
Landuse Basin Data
Predeveloped Land Use
predeveloped
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Forest, Mod 1.304
C, Forest, Flat 0.135
C, Forest, Steep 0.752
Pervious Total 2.191
Impervious Land Use acre
Impervious Total 0
Basin Total 2.191
20069 - exist. vault 3/19/2024 4:35:04 PM Page 4
Basin 2
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.22
Pervious Total 0.22
Impervious Land Use acre
Impervious Total 0
Basin Total 0.22
20069 - exist. vault 3/19/2024 4:35:04 PM Page 5
Mitigated Land Use
ONSITE
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Forest, Mod 0.06
C, Lawn, Mod 0.551
Pervious Total 0.611
Impervious Land Use acre
ROADS MOD 0.536
ROOF TOPS FLAT 0.647
ROADS FLAT 0.056
SIDEWALKS MOD 0.222
Impervious Total 1.461
Basin Total 2.072
20069 - exist. vault 3/19/2024 4:35:04 PM Page 6
FRONTAGE
Bypass:Yes
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.023
Pervious Total 0.023
Impervious Land Use acre
ROADS FLAT 0.016
SIDEWALKS FLAT 0.019
Impervious Total 0.035
Basin Total 0.058
20069 - exist. vault 3/19/2024 4:35:04 PM Page 7
UPSTREAM
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.22
Pervious Total 0.22
Impervious Land Use acre
Impervious Total 0
Basin Total 0.22
20069 - exist. vault 3/19/2024 4:35:04 PM Page 8
BYPASS
Bypass:Yes
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.024
Pervious Total 0.024
Impervious Land Use acre
ROADS MOD 0.03
SIDEWALKS MOD 0.009
Impervious Total 0.039
Basin Total 0.063
20069 - exist. vault 3/19/2024 4:35:04 PM Page 10
Mitigated Routing
Vault 1
Width:40.8 ft.
Length:90.06 ft.
Depth:9.15 ft.
Discharge Structure
Riser Height:8.15 ft.
Riser Diameter:18 in.
Notch Type:Rectangular
Notch Width:0.010 ft.
Notch Height:1.900 ft.
Orifice 1 Diameter:0.900 in.Elevation:0 ft.
Orifice 2 Diameter:0.980 in.Elevation:4 ft.
Element Flows To:
Outlet 1 Outlet 2
Vault Hydraulic Table
Stage(feet)Area(ac.)Volume(ac-ft.)Discharge(cfs)Infilt(cfs)
0.0000 0.084 0.000 0.000 0.000
0.1017 0.084 0.008 0.007 0.000
0.2033 0.084 0.017 0.009 0.000
0.3050 0.084 0.025 0.012 0.000
0.4067 0.084 0.034 0.014 0.000
0.5083 0.084 0.042 0.015 0.000
0.6100 0.084 0.051 0.017 0.000
0.7117 0.084 0.060 0.018 0.000
0.8133 0.084 0.068 0.019 0.000
0.9150 0.084 0.077 0.021 0.000
1.0167 0.084 0.085 0.022 0.000
1.1183 0.084 0.094 0.023 0.000
1.2200 0.084 0.102 0.024 0.000
1.3217 0.084 0.111 0.025 0.000
1.4233 0.084 0.120 0.026 0.000
1.5250 0.084 0.128 0.027 0.000
1.6267 0.084 0.137 0.028 0.000
1.7283 0.084 0.145 0.028 0.000
1.8300 0.084 0.154 0.029 0.000
1.9317 0.084 0.162 0.030 0.000
2.0333 0.084 0.171 0.031 0.000
2.1350 0.084 0.180 0.032 0.000
2.2367 0.084 0.188 0.032 0.000
2.3383 0.084 0.197 0.033 0.000
2.4400 0.084 0.205 0.034 0.000
2.5417 0.084 0.214 0.035 0.000
2.6433 0.084 0.223 0.035 0.000
2.7450 0.084 0.231 0.036 0.000
2.8467 0.084 0.240 0.037 0.000
2.9483 0.084 0.248 0.037 0.000
3.0500 0.084 0.257 0.038 0.000
3.1517 0.084 0.265 0.039 0.000
3.2533 0.084 0.274 0.039 0.000
3.3550 0.084 0.283 0.040 0.000
3.4567 0.084 0.291 0.040 0.000
3.5583 0.084 0.300 0.041 0.000
20069 - exist. vault 3/19/2024 4:35:04 PM Page 11
3.6600 0.084 0.308 0.042 0.000
3.7617 0.084 0.317 0.042 0.000
3.8633 0.084 0.325 0.043 0.000
3.9650 0.084 0.334 0.043 0.000
4.0667 0.084 0.343 0.051 0.000
4.1683 0.084 0.351 0.055 0.000
4.2700 0.084 0.360 0.059 0.000
4.3717 0.084 0.368 0.061 0.000
4.4733 0.084 0.377 0.064 0.000
4.5750 0.084 0.385 0.066 0.000
4.6767 0.084 0.394 0.069 0.000
4.7783 0.084 0.403 0.071 0.000
4.8800 0.084 0.411 0.073 0.000
4.9817 0.084 0.420 0.074 0.000
5.0833 0.084 0.428 0.076 0.000
5.1850 0.084 0.437 0.078 0.000
5.2867 0.084 0.445 0.080 0.000
5.3883 0.084 0.454 0.081 0.000
5.4900 0.084 0.463 0.083 0.000
5.5917 0.084 0.471 0.084 0.000
5.6933 0.084 0.480 0.086 0.000
5.7950 0.084 0.488 0.087 0.000
5.8967 0.084 0.497 0.089 0.000
5.9983 0.084 0.506 0.090 0.000
6.1000 0.084 0.514 0.092 0.000
6.2017 0.084 0.523 0.093 0.000
6.3033 0.084 0.531 0.095 0.000
6.4050 0.084 0.540 0.098 0.000
6.5067 0.084 0.548 0.101 0.000
6.6083 0.084 0.557 0.105 0.000
6.7100 0.084 0.566 0.109 0.000
6.8117 0.084 0.574 0.113 0.000
6.9133 0.084 0.583 0.117 0.000
7.0150 0.084 0.591 0.122 0.000
7.1167 0.084 0.600 0.126 0.000
7.2183 0.084 0.608 0.131 0.000
7.3200 0.084 0.617 0.136 0.000
7.4217 0.084 0.626 0.141 0.000
7.5233 0.084 0.634 0.147 0.000
7.6250 0.084 0.643 0.153 0.000
7.7267 0.084 0.651 0.174 0.000
7.8283 0.084 0.660 0.182 0.000
7.9300 0.084 0.668 0.190 0.000
8.0317 0.084 0.677 0.198 0.000
8.1333 0.084 0.686 0.206 0.000
8.2350 0.084 0.694 0.602 0.000
8.3367 0.084 0.703 1.479 0.000
8.4383 0.084 0.711 2.579 0.000
8.5400 0.084 0.720 3.734 0.000
8.6417 0.084 0.729 4.776 0.000
8.7433 0.084 0.737 5.573 0.000
8.8450 0.084 0.746 6.088 0.000
8.9467 0.084 0.754 6.541 0.000
9.0483 0.084 0.763 6.933 0.000
9.1500 0.084 0.771 7.304 0.000
9.2517 0.084 0.780 7.656 0.000
9.3533 0.000 0.000 7.993 0.000
20069 - exist. vault 3/19/2024 4:35:04 PM Page 13
Analysis Results
POC 1
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #1
Total Pervious Area:2.411
Total Impervious Area:0
Mitigated Landuse Totals for POC #1
Total Pervious Area:0.878
Total Impervious Area:1.535
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.090822
5 year 0.151934
10 year 0.19652
25 year 0.256341
50 year 0.302924
100 year 0.350919
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.070413
5 year 0.09562
10 year 0.114486
25 year 0.140929
50 year 0.162608
100 year 0.186062
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.127 0.073
1950 0.140 0.074
1951 0.177 0.128
1952 0.060 0.049
1953 0.048 0.052
1954 0.068 0.052
1955 0.118 0.059
1956 0.097 0.086
1957 0.097 0.070
1958 0.083 0.056
20069 - exist. vault 3/19/2024 4:35:35 PM Page 14
1959 0.069 0.051
1960 0.137 0.117
1961 0.068 0.071
1962 0.046 0.046
1963 0.064 0.059
1964 0.093 0.058
1965 0.071 0.073
1966 0.055 0.052
1967 0.157 0.076
1968 0.086 0.072
1969 0.080 0.062
1970 0.067 0.059
1971 0.084 0.071
1972 0.141 0.097
1973 0.064 0.063
1974 0.081 0.065
1975 0.117 0.072
1976 0.080 0.061
1977 0.024 0.056
1978 0.066 0.061
1979 0.036 0.060
1980 0.198 0.099
1981 0.053 0.063
1982 0.149 0.129
1983 0.094 0.061
1984 0.059 0.050
1985 0.034 0.059
1986 0.148 0.090
1987 0.135 0.109
1988 0.054 0.050
1989 0.035 0.050
1990 0.355 0.137
1991 0.205 0.110
1992 0.077 0.059
1993 0.066 0.047
1994 0.025 0.044
1995 0.088 0.062
1996 0.224 0.128
1997 0.169 0.126
1998 0.060 0.065
1999 0.219 0.095
2000 0.067 0.062
2001 0.014 0.063
2002 0.087 0.094
2003 0.130 0.070
2004 0.144 0.134
2005 0.101 0.063
2006 0.103 0.068
2007 0.285 0.192
2008 0.305 0.152
2009 0.148 0.097
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.3554 0.1919
2 0.3048 0.1517
3 0.2848 0.1365
20069 - exist. vault 3/19/2024 4:35:35 PM Page 15
4 0.2244 0.1335
5 0.2193 0.1291
6 0.2047 0.1283
7 0.1978 0.1277
8 0.1774 0.1257
9 0.1687 0.1173
10 0.1572 0.1095
11 0.1490 0.1087
12 0.1479 0.0986
13 0.1476 0.0974
14 0.1441 0.0974
15 0.1410 0.0947
16 0.1402 0.0938
17 0.1372 0.0902
18 0.1354 0.0860
19 0.1302 0.0760
20 0.1270 0.0735
21 0.1180 0.0734
22 0.1169 0.0733
23 0.1034 0.0721
24 0.1013 0.0718
25 0.0974 0.0714
26 0.0966 0.0708
27 0.0944 0.0704
28 0.0926 0.0695
29 0.0880 0.0679
30 0.0867 0.0653
31 0.0859 0.0646
32 0.0844 0.0635
33 0.0830 0.0634
34 0.0814 0.0634
35 0.0804 0.0629
36 0.0803 0.0620
37 0.0769 0.0616
38 0.0705 0.0616
39 0.0693 0.0613
40 0.0684 0.0609
41 0.0679 0.0607
42 0.0671 0.0598
43 0.0668 0.0595
44 0.0660 0.0593
45 0.0659 0.0593
46 0.0641 0.0586
47 0.0637 0.0585
48 0.0605 0.0579
49 0.0604 0.0565
50 0.0586 0.0557
51 0.0546 0.0525
52 0.0538 0.0520
53 0.0526 0.0519
54 0.0477 0.0514
55 0.0458 0.0504
56 0.0356 0.0501
57 0.0347 0.0499
58 0.0336 0.0487
59 0.0249 0.0472
60 0.0237 0.0462
61 0.0135 0.0438
20069 - exist. vault 3/19/2024 4:35:35 PM Page 17
Duration Flows
The Facility PASSED
Flow(cfs)Predev Mit Percentage Pass/Fail
0.0454 12820 11995 93 Pass
0.0480 11360 9794 86 Pass
0.0506 10029 8519 84 Pass
0.0532 8851 7649 86 Pass
0.0558 7880 6883 87 Pass
0.0584 7043 6254 88 Pass
0.0610 6286 5732 91 Pass
0.0636 5685 5272 92 Pass
0.0662 5093 4836 94 Pass
0.0688 4599 4402 95 Pass
0.0714 4156 4004 96 Pass
0.0740 3779 3625 95 Pass
0.0766 3433 3292 95 Pass
0.0792 3144 2954 93 Pass
0.0818 2868 2603 90 Pass
0.0844 2629 2224 84 Pass
0.0870 2368 1898 80 Pass
0.0896 2145 1602 74 Pass
0.0922 1931 1339 69 Pass
0.0948 1735 1085 62 Pass
0.0974 1567 878 56 Pass
0.1000 1418 730 51 Pass
0.1026 1259 627 49 Pass
0.1052 1128 531 47 Pass
0.1078 1052 466 44 Pass
0.1104 983 418 42 Pass
0.1130 918 377 41 Pass
0.1156 860 339 39 Pass
0.1182 800 296 37 Pass
0.1208 739 241 32 Pass
0.1234 668 201 30 Pass
0.1260 618 166 26 Pass
0.1286 559 128 22 Pass
0.1312 492 109 22 Pass
0.1338 439 84 19 Pass
0.1365 389 73 18 Pass
0.1391 340 64 18 Pass
0.1417 304 57 18 Pass
0.1443 259 52 20 Pass
0.1469 230 48 20 Pass
0.1495 197 45 22 Pass
0.1521 173 42 24 Pass
0.1547 149 39 26 Pass
0.1573 134 38 28 Pass
0.1599 116 32 27 Pass
0.1625 98 27 27 Pass
0.1651 87 26 29 Pass
0.1677 74 24 32 Pass
0.1703 64 22 34 Pass
0.1729 56 21 37 Pass
0.1755 48 18 37 Pass
0.1781 45 18 40 Pass
0.1807 41 17 41 Pass
20069 - exist. vault 3/19/2024 4:35:35 PM Page 18
0.1833 40 14 35 Pass
0.1859 36 11 30 Pass
0.1885 32 6 18 Pass
0.1911 30 2 6 Pass
0.1937 24 0 0 Pass
0.1963 23 0 0 Pass
0.1989 17 0 0 Pass
0.2015 14 0 0 Pass
0.2041 12 0 0 Pass
0.2067 9 0 0 Pass
0.2093 9 0 0 Pass
0.2119 9 0 0 Pass
0.2145 9 0 0 Pass
0.2171 8 0 0 Pass
0.2197 7 0 0 Pass
0.2223 7 0 0 Pass
0.2249 6 0 0 Pass
0.2275 6 0 0 Pass
0.2301 6 0 0 Pass
0.2327 6 0 0 Pass
0.2353 6 0 0 Pass
0.2379 6 0 0 Pass
0.2405 6 0 0 Pass
0.2431 5 0 0 Pass
0.2457 5 0 0 Pass
0.2483 5 0 0 Pass
0.2509 5 0 0 Pass
0.2535 5 0 0 Pass
0.2561 5 0 0 Pass
0.2587 5 0 0 Pass
0.2613 5 0 0 Pass
0.2639 4 0 0 Pass
0.2665 4 0 0 Pass
0.2691 4 0 0 Pass
0.2717 4 0 0 Pass
0.2743 4 0 0 Pass
0.2769 4 0 0 Pass
0.2795 4 0 0 Pass
0.2821 4 0 0 Pass
0.2847 4 0 0 Pass
0.2873 3 0 0 Pass
0.2899 3 0 0 Pass
0.2925 3 0 0 Pass
0.2951 2 0 0 Pass
0.2977 2 0 0 Pass
0.3003 2 0 0 Pass
0.3029 2 0 0 Pass
20069 - exist. vault 3/19/2024 4:35:35 PM Page 19
Water Quality
Water Quality BMP Flow and Volume for POC #1
On-line facility volume:0.0795 acre-feet
On-line facility target flow:0.0407 cfs.
Adjusted for 15 min:0.0407 cfs.
Off-line facility target flow:0.0266 cfs.
Adjusted for 15 min:0.0266 cfs.
20069 - exist. vault 3/19/2024 4:35:44 PM Page 21
Model Default Modifications
Total of 0 changes have been made.
PERLND Changes
No PERLND changes have been made.
IMPLND Changes
No IMPLND changes have been made.
20069 - exist. vault 3/19/2024 4:35:44 PM Page 22
Appendix
Predeveloped Schematic
20069 - exist. vault 3/19/2024 4:35:45 PM Page 23
Mitigated Schematic
WWHM2012
PROJECT REPORT
INDIVIDUAL CB
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 2
General Model Information
WWHM2012 Project Name:INDIVIDUAL-CB
Site Name:Grant Place TH
Site Address:1600 Grabt Ave S
City:Renton
Report Date:4/1/2024
Gage:Seatac
Data Start:1948/10/01
Data End:2009/09/30
Timestep:15 Minute
Precip Scale:1.000
Version Date:2023/01/27
Version:4.2.19
POC Thresholds
Low Flow Threshold for POC2:50 Percent of the 2 Year
High Flow Threshold for POC2:50 Year
Low Flow Threshold for POC3:50 Percent of the 2 Year
High Flow Threshold for POC3:50 Year
Low Flow Threshold for POC4:50 Percent of the 2 Year
High Flow Threshold for POC4:50 Year
Low Flow Threshold for POC5:50 Percent of the 2 Year
High Flow Threshold for POC5:50 Year
Low Flow Threshold for POC6:50 Percent of the 2 Year
High Flow Threshold for POC6:50 Year
Low Flow Threshold for POC7:50 Percent of the 2 Year
High Flow Threshold for POC7:50 Year
Low Flow Threshold for POC8:50 Percent of the 2 Year
High Flow Threshold for POC8:50 Year
Low Flow Threshold for POC9:50 Percent of the 2 Year
High Flow Threshold for POC9:50 Year
Low Flow Threshold for POC10:50 Percent of the 2 Year
High Flow Threshold for POC10:50 Year
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 3
Low Flow Threshold for POC11:50 Percent of the 2 Year
High Flow Threshold for POC11:50 Year
Low Flow Threshold for POC12:50 Percent of the 2 Year
High Flow Threshold for POC12:50 Year
Low Flow Threshold for POC13:50 Percent of the 2 Year
High Flow Threshold for POC13:50 Year
Low Flow Threshold for POC14:50 Percent of the 2 Year
High Flow Threshold for POC14:50 Year
Low Flow Threshold for POC15:50 Percent of the 2 Year
High Flow Threshold for POC15:50 Year
Low Flow Threshold for POC16:50 Percent of the 2 Year
High Flow Threshold for POC16:50 Year
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 19
Mitigated Land Use
CB2
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.023
Pervious Total 0.023
Impervious Land Use acre
ROADS MOD 0.018
SIDEWALKS FLAT 0.017
Impervious Total 0.035
Basin Total 0.058
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 20
CB3
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.038
Pervious Total 0.038
Impervious Land Use acre
ROADS FLAT 0.054
ROADS MOD 0.147
ROOF TOPS FLAT 0.09
SIDEWALKS FLAT 0.006
Impervious Total 0.297
Basin Total 0.335
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 21
CB4
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.121
Pervious Total 0.121
Impervious Land Use acre
ROADS MOD 0.028
SIDEWALKS FLAT 0.028
Impervious Total 0.056
Basin Total 0.177
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 22
CB6
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.001
Pervious Total 0.001
Impervious Land Use acre
ROADS MOD 0.062
ROOF TOPS FLAT 0.146
Impervious Total 0.208
Basin Total 0.209
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 23
CB18
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.025
Pervious Total 0.025
Impervious Land Use acre
SIDEWALKS FLAT 0.008
Impervious Total 0.008
Basin Total 0.033
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 24
CB7
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.024
Pervious Total 0.024
Impervious Land Use acre
ROADS MOD 0.002
SIDEWALKS FLAT 0.016
Impervious Total 0.018
Basin Total 0.042
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 25
CB8
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.021
Pervious Total 0.021
Impervious Land Use acre
ROADS MOD 0.051
SIDEWALKS FLAT 0.013
Impervious Total 0.064
Basin Total 0.085
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 26
CB9
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.044
Pervious Total 0.044
Impervious Land Use acre
ROADS MOD 0.045
ROOF TOPS FLAT 0.005
SIDEWALKS FLAT 0.002
Impervious Total 0.052
Basin Total 0.096
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 27
CB10
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.015
Pervious Total 0.015
Impervious Land Use acre
ROADS MOD 0.053
ROOF TOPS FLAT 0.027
Impervious Total 0.08
Basin Total 0.095
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 28
CB11
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.016
Pervious Total 0.016
Impervious Land Use acre
ROADS MOD 0.051
ROOF TOPS FLAT 0.027
Impervious Total 0.078
Basin Total 0.094
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 29
CB12
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.002
Pervious Total 0.002
Impervious Land Use acre
ROADS MOD 0.021
SIDEWALKS FLAT 0.001
Impervious Total 0.022
Basin Total 0.024
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 30
CB13
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.062
Pervious Total 0.062
Impervious Land Use acre
ROADS MOD 0.024
SIDEWALKS FLAT 0.035
Impervious Total 0.059
Basin Total 0.121
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 31
CB15
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.062
Pervious Total 0.062
Impervious Land Use acre
ROOF TOPS FLAT 0.072
SIDEWALKS FLAT 0.03
Impervious Total 0.102
Basin Total 0.164
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 32
CB16
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.057
Pervious Total 0.057
Impervious Land Use acre
ROOF TOPS FLAT 0.066
SIDEWALKS FLAT 0.035
Impervious Total 0.101
Basin Total 0.158
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 33
CB17
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Mod 0.05
Pervious Total 0.05
Impervious Land Use acre
ROOF TOPS FLAT 0.066
SIDEWALKS FLAT 0.028
Impervious Total 0.094
Basin Total 0.144
INDIVIDUAL-CB 4/1/2024 12:20:46 PM Page 37
POC 2
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #2
Total Pervious Area:0.058
Total Impervious Area:0
Mitigated Landuse Totals for POC #2
Total Pervious Area:0.023
Total Impervious Area:0.035
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #2
Return Period Flow(cfs)
2 year 0.001705
5 year 0.002678
10 year 0.00323
25 year 0.003814
50 year 0.004175
100 year 0.004483
Flow Frequency Return Periods for Mitigated. POC #2
Return Period Flow(cfs)
2 year 0.016085
5 year 0.021093
10 year 0.024668
25 year 0.029491
50 year 0.033312
100 year 0.037335
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #2
Year Predeveloped Mitigated
1949 0.002 0.023
1950 0.002 0.020
1951 0.004 0.014
1952 0.001 0.010
1953 0.001 0.012
1954 0.001 0.013
1955 0.002 0.015
1956 0.002 0.014
1957 0.002 0.017
1958 0.002 0.013
1959 0.001 0.013
INDIVIDUAL-CB 4/1/2024 12:21:17 PM Page 38
1960 0.003 0.015
1961 0.001 0.014
1962 0.001 0.011
1963 0.001 0.014
1964 0.002 0.013
1965 0.001 0.017
1966 0.001 0.011
1967 0.002 0.020
1968 0.001 0.024
1969 0.001 0.016
1970 0.001 0.015
1971 0.001 0.018
1972 0.003 0.020
1973 0.001 0.010
1974 0.001 0.018
1975 0.002 0.017
1976 0.001 0.014
1977 0.000 0.013
1978 0.001 0.017
1979 0.001 0.022
1980 0.003 0.026
1981 0.001 0.016
1982 0.002 0.024
1983 0.002 0.018
1984 0.001 0.011
1985 0.001 0.016
1986 0.003 0.014
1987 0.003 0.020
1988 0.001 0.012
1989 0.001 0.018
1990 0.005 0.034
1991 0.003 0.027
1992 0.001 0.012
1993 0.001 0.012
1994 0.000 0.011
1995 0.002 0.014
1996 0.004 0.019
1997 0.003 0.016
1998 0.001 0.015
1999 0.003 0.035
2000 0.001 0.016
2001 0.000 0.017
2002 0.001 0.021
2003 0.002 0.019
2004 0.002 0.033
2005 0.002 0.014
2006 0.002 0.013
2007 0.004 0.031
2008 0.005 0.025
2009 0.003 0.020
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #2
Rank Predeveloped Mitigated
1 0.0055 0.0347
2 0.0052 0.0337
3 0.0041 0.0326
4 0.0040 0.0310
INDIVIDUAL-CB 4/1/2024 12:21:17 PM Page 39
5 0.0038 0.0267
6 0.0033 0.0258
7 0.0033 0.0253
8 0.0031 0.0240
9 0.0030 0.0239
10 0.0028 0.0228
11 0.0027 0.0216
12 0.0026 0.0209
13 0.0026 0.0204
14 0.0025 0.0203
15 0.0024 0.0202
16 0.0023 0.0197
17 0.0023 0.0196
18 0.0021 0.0193
19 0.0020 0.0188
20 0.0020 0.0183
21 0.0019 0.0179
22 0.0019 0.0177
23 0.0019 0.0175
24 0.0018 0.0174
25 0.0018 0.0170
26 0.0017 0.0168
27 0.0017 0.0168
28 0.0017 0.0168
29 0.0016 0.0160
30 0.0015 0.0159
31 0.0015 0.0159
32 0.0015 0.0158
33 0.0014 0.0157
34 0.0014 0.0151
35 0.0014 0.0150
36 0.0014 0.0148
37 0.0014 0.0147
38 0.0014 0.0144
39 0.0013 0.0143
40 0.0013 0.0139
41 0.0013 0.0137
42 0.0013 0.0136
43 0.0012 0.0136
44 0.0012 0.0136
45 0.0012 0.0135
46 0.0012 0.0131
47 0.0012 0.0131
48 0.0012 0.0129
49 0.0011 0.0127
50 0.0011 0.0127
51 0.0011 0.0126
52 0.0010 0.0118
53 0.0010 0.0118
54 0.0009 0.0117
55 0.0008 0.0116
56 0.0007 0.0115
57 0.0007 0.0113
58 0.0007 0.0111
59 0.0004 0.0108
60 0.0002 0.0103
61 0.0002 0.0099
INDIVIDUAL-CB 4/1/2024 12:21:40 PM Page 45
POC 3
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #3
Total Pervious Area:0.335
Total Impervious Area:0
Mitigated Landuse Totals for POC #3
Total Pervious Area:0.038
Total Impervious Area:0.297
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #3
Return Period Flow(cfs)
2 year 0.009849
5 year 0.015469
10 year 0.018653
25 year 0.022027
50 year 0.024115
100 year 0.025891
Flow Frequency Return Periods for Mitigated. POC #3
Return Period Flow(cfs)
2 year 0.124521
5 year 0.158734
10 year 0.182143
25 year 0.212678
50 year 0.236162
100 year 0.260308
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #3
Year Predeveloped Mitigated
1949 0.010 0.164
1950 0.012 0.167
1951 0.022 0.099
1952 0.007 0.082
1953 0.006 0.096
1954 0.008 0.100
1955 0.014 0.118
1956 0.011 0.107
1957 0.009 0.124
1958 0.010 0.102
1959 0.008 0.107
INDIVIDUAL-CB 4/1/2024 12:22:10 PM Page 46
1960 0.015 0.108
1961 0.008 0.104
1962 0.005 0.092
1963 0.007 0.108
1964 0.009 0.105
1965 0.007 0.128
1966 0.006 0.087
1967 0.013 0.148
1968 0.008 0.184
1969 0.008 0.117
1970 0.007 0.116
1971 0.007 0.140
1972 0.016 0.138
1973 0.007 0.087
1974 0.008 0.130
1975 0.011 0.139
1976 0.008 0.102
1977 0.001 0.103
1978 0.007 0.140
1979 0.004 0.179
1980 0.015 0.179
1981 0.006 0.125
1982 0.012 0.179
1983 0.011 0.144
1984 0.007 0.089
1985 0.004 0.122
1986 0.017 0.107
1987 0.015 0.165
1988 0.006 0.100
1989 0.004 0.149
1990 0.032 0.221
1991 0.019 0.183
1992 0.007 0.089
1993 0.008 0.097
1994 0.003 0.091
1995 0.011 0.112
1996 0.023 0.135
1997 0.019 0.116
1998 0.004 0.118
1999 0.018 0.254
2000 0.008 0.120
2001 0.001 0.138
2002 0.008 0.151
2003 0.011 0.140
2004 0.014 0.241
2005 0.010 0.101
2006 0.012 0.093
2007 0.023 0.227
2008 0.030 0.174
2009 0.015 0.165
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #3
Rank Predeveloped Mitigated
1 0.0316 0.2537
2 0.0302 0.2413
3 0.0234 0.2271
4 0.0231 0.2210
INDIVIDUAL-CB 4/1/2024 12:22:10 PM Page 47
5 0.0217 0.1841
6 0.0193 0.1833
7 0.0190 0.1795
8 0.0181 0.1792
9 0.0171 0.1788
10 0.0162 0.1743
11 0.0153 0.1674
12 0.0151 0.1654
13 0.0148 0.1652
14 0.0147 0.1637
15 0.0138 0.1508
16 0.0135 0.1487
17 0.0134 0.1485
18 0.0121 0.1445
19 0.0118 0.1400
20 0.0117 0.1396
21 0.0110 0.1395
22 0.0108 0.1386
23 0.0108 0.1384
24 0.0106 0.1384
25 0.0105 0.1349
26 0.0099 0.1298
27 0.0098 0.1276
28 0.0097 0.1249
29 0.0093 0.1244
30 0.0087 0.1218
31 0.0085 0.1202
32 0.0084 0.1180
33 0.0084 0.1175
34 0.0083 0.1166
35 0.0083 0.1163
36 0.0082 0.1157
37 0.0080 0.1118
38 0.0078 0.1081
39 0.0076 0.1077
40 0.0076 0.1073
41 0.0073 0.1072
42 0.0073 0.1066
43 0.0072 0.1047
44 0.0071 0.1037
45 0.0068 0.1029
46 0.0068 0.1023
47 0.0067 0.1022
48 0.0067 0.1006
49 0.0065 0.1004
50 0.0064 0.1003
51 0.0061 0.0992
52 0.0060 0.0966
53 0.0055 0.0960
54 0.0051 0.0926
55 0.0044 0.0917
56 0.0041 0.0909
57 0.0039 0.0894
58 0.0039 0.0888
59 0.0026 0.0870
60 0.0014 0.0865
61 0.0009 0.0819
INDIVIDUAL-CB 4/1/2024 12:22:10 PM Page 53
POC 4
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #4
Total Pervious Area:0.177
Total Impervious Area:0
Mitigated Landuse Totals for POC #4
Total Pervious Area:0.121
Total Impervious Area:0.056
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #4
Return Period Flow(cfs)
2 year 0.005204
5 year 0.008173
10 year 0.009856
25 year 0.011638
50 year 0.012741
100 year 0.013679
Flow Frequency Return Periods for Mitigated. POC #4
Return Period Flow(cfs)
2 year 0.033077
5 year 0.046656
10 year 0.056696
25 year 0.07062
50 year 0.081917
100 year 0.094033
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #4
Year Predeveloped Mitigated
1949 0.005 0.052
1950 0.006 0.049
1951 0.011 0.030
1952 0.004 0.019
1953 0.003 0.020
1954 0.004 0.027
1955 0.007 0.029
1956 0.006 0.027
1957 0.005 0.037
1958 0.005 0.024
1959 0.004 0.020
INDIVIDUAL-CB 4/1/2024 12:22:40 PM Page 54
1960 0.008 0.033
1961 0.004 0.028
1962 0.003 0.020
1963 0.004 0.030
1964 0.005 0.026
1965 0.004 0.038
1966 0.003 0.022
1967 0.007 0.049
1968 0.004 0.048
1969 0.004 0.035
1970 0.004 0.031
1971 0.004 0.037
1972 0.009 0.046
1973 0.004 0.018
1974 0.004 0.038
1975 0.006 0.038
1976 0.004 0.029
1977 0.000 0.027
1978 0.004 0.033
1979 0.002 0.036
1980 0.008 0.062
1981 0.003 0.032
1982 0.006 0.055
1983 0.006 0.033
1984 0.003 0.023
1985 0.002 0.031
1986 0.009 0.030
1987 0.008 0.036
1988 0.003 0.019
1989 0.002 0.028
1990 0.017 0.089
1991 0.010 0.065
1992 0.004 0.025
1993 0.004 0.019
1994 0.001 0.017
1995 0.006 0.028
1996 0.012 0.046
1997 0.010 0.035
1998 0.002 0.030
1999 0.010 0.077
2000 0.004 0.033
2001 0.001 0.029
2002 0.004 0.048
2003 0.006 0.044
2004 0.007 0.070
2005 0.005 0.029
2006 0.006 0.029
2007 0.012 0.082
2008 0.016 0.062
2009 0.008 0.039
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #4
Rank Predeveloped Mitigated
1 0.0167 0.0888
2 0.0160 0.0819
3 0.0124 0.0770
4 0.0122 0.0703
INDIVIDUAL-CB 4/1/2024 12:22:40 PM Page 55
5 0.0115 0.0653
6 0.0102 0.0623
7 0.0100 0.0618
8 0.0096 0.0550
9 0.0090 0.0519
10 0.0085 0.0494
11 0.0081 0.0489
12 0.0080 0.0479
13 0.0078 0.0475
14 0.0077 0.0463
15 0.0073 0.0457
16 0.0072 0.0436
17 0.0071 0.0388
18 0.0064 0.0383
19 0.0062 0.0379
20 0.0062 0.0377
21 0.0058 0.0375
22 0.0057 0.0366
23 0.0057 0.0365
24 0.0056 0.0356
25 0.0056 0.0351
26 0.0052 0.0347
27 0.0052 0.0334
28 0.0051 0.0333
29 0.0049 0.0332
30 0.0046 0.0328
31 0.0045 0.0316
32 0.0044 0.0312
33 0.0044 0.0307
34 0.0044 0.0303
35 0.0044 0.0302
36 0.0043 0.0302
37 0.0042 0.0302
38 0.0041 0.0293
39 0.0040 0.0291
40 0.0040 0.0290
41 0.0039 0.0287
42 0.0039 0.0286
43 0.0038 0.0282
44 0.0037 0.0281
45 0.0036 0.0276
46 0.0036 0.0274
47 0.0036 0.0267
48 0.0035 0.0266
49 0.0034 0.0258
50 0.0034 0.0248
51 0.0032 0.0244
52 0.0031 0.0228
53 0.0029 0.0218
54 0.0027 0.0203
55 0.0023 0.0202
56 0.0022 0.0198
57 0.0021 0.0194
58 0.0020 0.0193
59 0.0014 0.0189
60 0.0007 0.0178
61 0.0005 0.0172
INDIVIDUAL-CB 4/1/2024 12:22:41 PM Page 61
POC 5
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #5
Total Pervious Area:0.209
Total Impervious Area:0
Mitigated Landuse Totals for POC #5
Total Pervious Area:0.001
Total Impervious Area:0.208
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #5
Return Period Flow(cfs)
2 year 0.006145
5 year 0.009651
10 year 0.011637
25 year 0.013742
50 year 0.015045
100 year 0.016153
Flow Frequency Return Periods for Mitigated. POC #5
Return Period Flow(cfs)
2 year 0.082829
5 year 0.104806
10 year 0.119757
25 year 0.139172
50 year 0.154046
100 year 0.169291
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #5
Year Predeveloped Mitigated
1949 0.006 0.107
1950 0.008 0.114
1951 0.014 0.066
1952 0.004 0.057
1953 0.003 0.065
1954 0.005 0.067
1955 0.008 0.078
1956 0.007 0.073
1957 0.005 0.083
1958 0.006 0.069
1959 0.005 0.072
INDIVIDUAL-CB 4/1/2024 12:23:11 PM Page 62
1960 0.009 0.070
1961 0.005 0.070
1962 0.003 0.062
1963 0.004 0.071
1964 0.006 0.070
1965 0.004 0.085
1966 0.004 0.057
1967 0.008 0.100
1968 0.005 0.120
1969 0.005 0.078
1970 0.004 0.077
1971 0.004 0.092
1972 0.010 0.092
1973 0.005 0.059
1974 0.005 0.085
1975 0.007 0.095
1976 0.005 0.067
1977 0.001 0.070
1978 0.004 0.092
1979 0.003 0.120
1980 0.010 0.111
1981 0.004 0.085
1982 0.007 0.120
1983 0.007 0.098
1984 0.004 0.061
1985 0.002 0.083
1986 0.011 0.073
1987 0.009 0.113
1988 0.004 0.069
1989 0.002 0.096
1990 0.020 0.143
1991 0.012 0.118
1992 0.005 0.061
1993 0.005 0.060
1994 0.002 0.060
1995 0.007 0.076
1996 0.014 0.086
1997 0.012 0.078
1998 0.003 0.080
1999 0.011 0.166
2000 0.005 0.080
2001 0.001 0.092
2002 0.005 0.101
2003 0.007 0.088
2004 0.009 0.157
2005 0.006 0.068
2006 0.007 0.061
2007 0.015 0.147
2008 0.019 0.114
2009 0.009 0.110
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #5
Rank Predeveloped Mitigated
1 0.0197 0.1658
2 0.0189 0.1571
3 0.0146 0.1472
4 0.0144 0.1432
INDIVIDUAL-CB 4/1/2024 12:23:11 PM Page 63
5 0.0135 0.1200
6 0.0120 0.1199
7 0.0119 0.1197
8 0.0113 0.1181
9 0.0107 0.1143
10 0.0101 0.1137
11 0.0095 0.1132
12 0.0094 0.1105
13 0.0093 0.1095
14 0.0091 0.1071
15 0.0086 0.1010
16 0.0084 0.0998
17 0.0084 0.0981
18 0.0075 0.0961
19 0.0073 0.0953
20 0.0073 0.0924
21 0.0068 0.0923
22 0.0067 0.0919
23 0.0067 0.0917
24 0.0066 0.0876
25 0.0066 0.0857
26 0.0062 0.0854
27 0.0061 0.0850
28 0.0060 0.0846
29 0.0058 0.0832
30 0.0054 0.0832
31 0.0053 0.0805
32 0.0052 0.0798
33 0.0052 0.0780
34 0.0052 0.0777
35 0.0052 0.0775
36 0.0051 0.0770
37 0.0050 0.0755
38 0.0049 0.0730
39 0.0048 0.0729
40 0.0048 0.0720
41 0.0046 0.0712
42 0.0046 0.0703
43 0.0045 0.0702
44 0.0044 0.0700
45 0.0043 0.0697
46 0.0043 0.0690
47 0.0042 0.0687
48 0.0042 0.0678
49 0.0041 0.0670
50 0.0040 0.0666
51 0.0038 0.0658
52 0.0037 0.0648
53 0.0034 0.0625
54 0.0032 0.0613
55 0.0027 0.0605
56 0.0026 0.0605
57 0.0024 0.0602
58 0.0024 0.0602
59 0.0016 0.0586
60 0.0009 0.0571
61 0.0006 0.0569
INDIVIDUAL-CB 4/1/2024 12:23:11 PM Page 69
POC 6
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #6
Total Pervious Area:0.33
Total Impervious Area:0
Mitigated Landuse Totals for POC #6
Total Pervious Area:0.025
Total Impervious Area:0.008
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #6
Return Period Flow(cfs)
2 year 0.009702
5 year 0.015238
10 year 0.018375
25 year 0.021698
50 year 0.023755
100 year 0.025504
Flow Frequency Return Periods for Mitigated. POC #6
Return Period Flow(cfs)
2 year 0.00518
5 year 0.007637
10 year 0.009475
25 year 0.012045
50 year 0.014142
100 year 0.0164
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #6
Year Predeveloped Mitigated
1949 0.010 0.009
1950 0.012 0.008
1951 0.021 0.005
1952 0.007 0.003
1953 0.005 0.003
1954 0.008 0.004
1955 0.013 0.004
1956 0.011 0.004
1957 0.009 0.006
1958 0.010 0.004
1959 0.008 0.003
INDIVIDUAL-CB 4/1/2024 12:23:41 PM Page 70
1960 0.014 0.005
1961 0.008 0.005
1962 0.005 0.003
1963 0.007 0.005
1964 0.009 0.004
1965 0.007 0.006
1966 0.006 0.003
1967 0.013 0.008
1968 0.008 0.007
1969 0.008 0.006
1970 0.007 0.005
1971 0.007 0.006
1972 0.016 0.008
1973 0.007 0.003
1974 0.008 0.006
1975 0.011 0.006
1976 0.008 0.004
1977 0.001 0.004
1978 0.007 0.005
1979 0.004 0.005
1980 0.015 0.010
1981 0.006 0.005
1982 0.012 0.009
1983 0.010 0.005
1984 0.006 0.004
1985 0.004 0.005
1986 0.017 0.005
1987 0.015 0.005
1988 0.006 0.003
1989 0.004 0.003
1990 0.031 0.016
1991 0.019 0.011
1992 0.007 0.004
1993 0.008 0.003
1994 0.003 0.002
1995 0.011 0.004
1996 0.023 0.008
1997 0.019 0.006
1998 0.004 0.005
1999 0.018 0.012
2000 0.008 0.005
2001 0.001 0.004
2002 0.008 0.008
2003 0.010 0.007
2004 0.014 0.011
2005 0.010 0.005
2006 0.011 0.005
2007 0.023 0.014
2008 0.030 0.011
2009 0.015 0.006
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #6
Rank Predeveloped Mitigated
1 0.0311 0.0158
2 0.0298 0.0145
3 0.0231 0.0125
4 0.0227 0.0111
INDIVIDUAL-CB 4/1/2024 12:23:41 PM Page 71
5 0.0214 0.0111
6 0.0190 0.0107
7 0.0187 0.0099
8 0.0178 0.0094
9 0.0168 0.0086
10 0.0159 0.0085
11 0.0151 0.0084
12 0.0149 0.0081
13 0.0146 0.0079
14 0.0144 0.0075
15 0.0136 0.0071
16 0.0133 0.0068
17 0.0132 0.0064
18 0.0119 0.0064
19 0.0116 0.0063
20 0.0115 0.0060
21 0.0108 0.0060
22 0.0106 0.0058
23 0.0106 0.0058
24 0.0105 0.0057
25 0.0104 0.0053
26 0.0097 0.0053
27 0.0096 0.0052
28 0.0095 0.0050
29 0.0092 0.0050
30 0.0086 0.0050
31 0.0084 0.0049
32 0.0083 0.0049
33 0.0082 0.0049
34 0.0082 0.0049
35 0.0082 0.0049
36 0.0081 0.0048
37 0.0078 0.0047
38 0.0077 0.0047
39 0.0075 0.0046
40 0.0075 0.0046
41 0.0072 0.0045
42 0.0072 0.0043
43 0.0071 0.0043
44 0.0070 0.0042
45 0.0067 0.0042
46 0.0067 0.0040
47 0.0066 0.0039
48 0.0066 0.0039
49 0.0064 0.0038
50 0.0063 0.0036
51 0.0060 0.0036
52 0.0059 0.0032
53 0.0054 0.0032
54 0.0051 0.0030
55 0.0043 0.0030
56 0.0041 0.0029
57 0.0038 0.0027
58 0.0038 0.0027
59 0.0025 0.0026
60 0.0013 0.0026
61 0.0009 0.0022
INDIVIDUAL-CB 4/1/2024 12:23:41 PM Page 77
POC 7
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #7
Total Pervious Area:0.042
Total Impervious Area:0
Mitigated Landuse Totals for POC #7
Total Pervious Area:0.024
Total Impervious Area:0.018
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #7
Return Period Flow(cfs)
2 year 0.001235
5 year 0.001939
10 year 0.002339
25 year 0.002762
50 year 0.003023
100 year 0.003246
Flow Frequency Return Periods for Mitigated. POC #7
Return Period Flow(cfs)
2 year 0.008919
5 year 0.012193
10 year 0.014557
25 year 0.017774
50 year 0.020342
100 year 0.02306
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #7
Year Predeveloped Mitigated
1949 0.001 0.013
1950 0.002 0.012
1951 0.003 0.008
1952 0.001 0.005
1953 0.001 0.006
1954 0.001 0.007
1955 0.002 0.008
1956 0.001 0.008
1957 0.001 0.010
1958 0.001 0.007
1959 0.001 0.006
INDIVIDUAL-CB 4/1/2024 12:24:12 PM Page 78
1960 0.002 0.008
1961 0.001 0.008
1962 0.001 0.006
1963 0.001 0.008
1964 0.001 0.007
1965 0.001 0.010
1966 0.001 0.006
1967 0.002 0.012
1968 0.001 0.013
1969 0.001 0.009
1970 0.001 0.008
1971 0.001 0.010
1972 0.002 0.012
1973 0.001 0.005
1974 0.001 0.010
1975 0.001 0.010
1976 0.001 0.008
1977 0.000 0.007
1978 0.001 0.009
1979 0.001 0.011
1980 0.002 0.015
1981 0.001 0.009
1982 0.001 0.015
1983 0.001 0.009
1984 0.001 0.006
1985 0.000 0.009
1986 0.002 0.008
1987 0.002 0.011
1988 0.001 0.006
1989 0.000 0.008
1990 0.004 0.022
1991 0.002 0.016
1992 0.001 0.006
1993 0.001 0.005
1994 0.000 0.005
1995 0.001 0.008
1996 0.003 0.011
1997 0.002 0.009
1998 0.001 0.008
1999 0.002 0.020
2000 0.001 0.009
2001 0.000 0.008
2002 0.001 0.013
2003 0.001 0.011
2004 0.002 0.018
2005 0.001 0.008
2006 0.001 0.008
2007 0.003 0.020
2008 0.004 0.016
2009 0.002 0.010
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #7
Rank Predeveloped Mitigated
1 0.0040 0.0222
2 0.0038 0.0202
3 0.0029 0.0200
4 0.0029 0.0183
INDIVIDUAL-CB 4/1/2024 12:24:12 PM Page 79
5 0.0027 0.0164
6 0.0024 0.0159
7 0.0024 0.0147
8 0.0023 0.0145
9 0.0021 0.0135
10 0.0020 0.0127
11 0.0019 0.0126
12 0.0019 0.0125
13 0.0019 0.0123
14 0.0018 0.0122
15 0.0017 0.0109
16 0.0017 0.0107
17 0.0017 0.0106
18 0.0015 0.0106
19 0.0015 0.0103
20 0.0015 0.0101
21 0.0014 0.0101
22 0.0014 0.0100
23 0.0014 0.0099
24 0.0013 0.0099
25 0.0013 0.0094
26 0.0012 0.0094
27 0.0012 0.0093
28 0.0012 0.0091
29 0.0012 0.0089
30 0.0011 0.0089
31 0.0011 0.0085
32 0.0011 0.0085
33 0.0010 0.0084
34 0.0010 0.0083
35 0.0010 0.0081
36 0.0010 0.0080
37 0.0010 0.0080
38 0.0010 0.0080
39 0.0010 0.0079
40 0.0010 0.0079
41 0.0009 0.0078
42 0.0009 0.0077
43 0.0009 0.0077
44 0.0009 0.0076
45 0.0009 0.0075
46 0.0009 0.0075
47 0.0008 0.0073
48 0.0008 0.0070
49 0.0008 0.0069
50 0.0008 0.0069
51 0.0008 0.0065
52 0.0007 0.0065
53 0.0007 0.0060
54 0.0006 0.0059
55 0.0005 0.0059
56 0.0005 0.0059
57 0.0005 0.0058
58 0.0005 0.0054
59 0.0003 0.0051
60 0.0002 0.0051
61 0.0001 0.0050
INDIVIDUAL-CB 4/1/2024 12:24:12 PM Page 85
POC 8
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #8
Total Pervious Area:0.085
Total Impervious Area:0
Mitigated Landuse Totals for POC #8
Total Pervious Area:0.021
Total Impervious Area:0.064
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #8
Return Period Flow(cfs)
2 year 0.002499
5 year 0.003925
10 year 0.004733
25 year 0.005589
50 year 0.006119
100 year 0.006569
Flow Frequency Return Periods for Mitigated. POC #8
Return Period Flow(cfs)
2 year 0.028928
5 year 0.037322
10 year 0.043237
25 year 0.051137
50 year 0.057341
100 year 0.063826
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #8
Year Predeveloped Mitigated
1949 0.002 0.039
1950 0.003 0.037
1951 0.006 0.023
1952 0.002 0.018
1953 0.001 0.022
1954 0.002 0.023
1955 0.003 0.028
1956 0.003 0.024
1957 0.002 0.029
1958 0.002 0.023
1959 0.002 0.025
INDIVIDUAL-CB 4/1/2024 12:24:42 PM Page 86
1960 0.004 0.026
1961 0.002 0.024
1962 0.001 0.021
1963 0.002 0.026
1964 0.002 0.024
1965 0.002 0.029
1966 0.002 0.020
1967 0.003 0.035
1968 0.002 0.044
1969 0.002 0.027
1970 0.002 0.027
1971 0.002 0.033
1972 0.004 0.033
1973 0.002 0.020
1974 0.002 0.031
1975 0.003 0.031
1976 0.002 0.024
1977 0.000 0.024
1978 0.002 0.033
1979 0.001 0.041
1980 0.004 0.046
1981 0.002 0.028
1982 0.003 0.042
1983 0.003 0.033
1984 0.002 0.021
1985 0.001 0.027
1986 0.004 0.024
1987 0.004 0.037
1988 0.002 0.023
1989 0.001 0.036
1990 0.008 0.053
1991 0.005 0.044
1992 0.002 0.021
1993 0.002 0.024
1994 0.001 0.022
1995 0.003 0.025
1996 0.006 0.033
1997 0.005 0.027
1998 0.001 0.027
1999 0.005 0.060
2000 0.002 0.028
2001 0.000 0.032
2002 0.002 0.035
2003 0.003 0.035
2004 0.003 0.058
2005 0.003 0.023
2006 0.003 0.022
2007 0.006 0.055
2008 0.008 0.042
2009 0.004 0.039
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #8
Rank Predeveloped Mitigated
1 0.0080 0.0605
2 0.0077 0.0578
3 0.0059 0.0547
4 0.0059 0.0534
INDIVIDUAL-CB 4/1/2024 12:24:42 PM Page 87
5 0.0055 0.0458
6 0.0049 0.0445
7 0.0048 0.0441
8 0.0046 0.0417
9 0.0043 0.0415
10 0.0041 0.0410
11 0.0039 0.0390
12 0.0038 0.0385
13 0.0038 0.0375
14 0.0037 0.0369
15 0.0035 0.0359
16 0.0034 0.0350
17 0.0034 0.0349
18 0.0031 0.0349
19 0.0030 0.0333
20 0.0030 0.0332
21 0.0028 0.0331
22 0.0027 0.0327
23 0.0027 0.0326
24 0.0027 0.0321
25 0.0027 0.0309
26 0.0025 0.0307
27 0.0025 0.0295
28 0.0025 0.0287
29 0.0024 0.0283
30 0.0022 0.0277
31 0.0022 0.0275
32 0.0021 0.0273
33 0.0021 0.0270
34 0.0021 0.0270
35 0.0021 0.0269
36 0.0021 0.0268
37 0.0020 0.0259
38 0.0020 0.0255
39 0.0019 0.0255
40 0.0019 0.0246
41 0.0019 0.0244
42 0.0019 0.0244
43 0.0018 0.0244
44 0.0018 0.0242
45 0.0017 0.0240
46 0.0017 0.0240
47 0.0017 0.0239
48 0.0017 0.0235
49 0.0017 0.0233
50 0.0016 0.0232
51 0.0016 0.0230
52 0.0015 0.0226
53 0.0014 0.0219
54 0.0013 0.0217
55 0.0011 0.0217
56 0.0010 0.0215
57 0.0010 0.0209
58 0.0010 0.0206
59 0.0007 0.0204
60 0.0003 0.0199
61 0.0002 0.0180
INDIVIDUAL-CB 4/1/2024 12:24:42 PM Page 93
POC 9
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #9
Total Pervious Area:0.096
Total Impervious Area:0
Mitigated Landuse Totals for POC #9
Total Pervious Area:0.044
Total Impervious Area:0.052
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #9
Return Period Flow(cfs)
2 year 0.002822
5 year 0.004433
10 year 0.005345
25 year 0.006312
50 year 0.006911
100 year 0.007419
Flow Frequency Return Periods for Mitigated. POC #9
Return Period Flow(cfs)
2 year 0.025912
5 year 0.034151
10 year 0.040054
25 year 0.048043
50 year 0.05439
100 year 0.061087
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #9
Year Predeveloped Mitigated
1949 0.003 0.037
1950 0.003 0.033
1951 0.006 0.022
1952 0.002 0.016
1953 0.002 0.018
1954 0.002 0.021
1955 0.004 0.024
1956 0.003 0.021
1957 0.002 0.027
1958 0.003 0.020
1959 0.002 0.020
INDIVIDUAL-CB 4/1/2024 12:25:14 PM Page 94
1960 0.004 0.024
1961 0.002 0.022
1962 0.001 0.018
1963 0.002 0.023
1964 0.003 0.020
1965 0.002 0.027
1966 0.002 0.018
1967 0.004 0.034
1968 0.002 0.039
1969 0.002 0.025
1970 0.002 0.024
1971 0.002 0.029
1972 0.005 0.031
1973 0.002 0.016
1974 0.002 0.028
1975 0.003 0.027
1976 0.002 0.022
1977 0.000 0.022
1978 0.002 0.028
1979 0.001 0.034
1980 0.004 0.045
1981 0.002 0.025
1982 0.003 0.038
1983 0.003 0.028
1984 0.002 0.019
1985 0.001 0.024
1986 0.005 0.022
1987 0.004 0.031
1988 0.002 0.019
1989 0.001 0.030
1990 0.009 0.055
1991 0.005 0.044
1992 0.002 0.020
1993 0.002 0.021
1994 0.001 0.018
1995 0.003 0.022
1996 0.007 0.032
1997 0.006 0.025
1998 0.001 0.024
1999 0.005 0.056
2000 0.002 0.025
2001 0.000 0.027
2002 0.002 0.033
2003 0.003 0.033
2004 0.004 0.053
2005 0.003 0.021
2006 0.003 0.020
2007 0.007 0.051
2008 0.009 0.041
2009 0.004 0.032
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #9
Rank Predeveloped Mitigated
1 0.0090 0.0565
2 0.0087 0.0546
3 0.0067 0.0533
4 0.0066 0.0510
INDIVIDUAL-CB 4/1/2024 12:25:14 PM Page 95
5 0.0062 0.0446
6 0.0055 0.0437
7 0.0054 0.0409
8 0.0052 0.0395
9 0.0049 0.0380
10 0.0046 0.0369
11 0.0044 0.0344
12 0.0043 0.0339
13 0.0043 0.0330
14 0.0042 0.0328
15 0.0040 0.0325
16 0.0039 0.0320
17 0.0038 0.0316
18 0.0035 0.0312
19 0.0034 0.0311
20 0.0033 0.0298
21 0.0031 0.0294
22 0.0031 0.0285
23 0.0031 0.0279
24 0.0031 0.0278
25 0.0030 0.0274
26 0.0028 0.0271
27 0.0028 0.0270
28 0.0028 0.0266
29 0.0027 0.0251
30 0.0025 0.0251
31 0.0024 0.0250
32 0.0024 0.0250
33 0.0024 0.0243
34 0.0024 0.0242
35 0.0024 0.0242
36 0.0023 0.0242
37 0.0023 0.0241
38 0.0022 0.0233
39 0.0022 0.0223
40 0.0022 0.0223
41 0.0021 0.0222
42 0.0021 0.0219
43 0.0021 0.0217
44 0.0020 0.0215
45 0.0020 0.0212
46 0.0020 0.0211
47 0.0019 0.0209
48 0.0019 0.0207
49 0.0019 0.0204
50 0.0018 0.0204
51 0.0018 0.0203
52 0.0017 0.0201
53 0.0016 0.0196
54 0.0015 0.0189
55 0.0013 0.0185
56 0.0012 0.0183
57 0.0011 0.0181
58 0.0011 0.0181
59 0.0007 0.0175
60 0.0004 0.0164
61 0.0003 0.0158
INDIVIDUAL-CB 4/1/2024 12:25:14 PM Page 101
POC 10
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #10
Total Pervious Area:0.095
Total Impervious Area:0
Mitigated Landuse Totals for POC #10
Total Pervious Area:0.015
Total Impervious Area:0.08
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #10
Return Period Flow(cfs)
2 year 0.002793
5 year 0.004387
10 year 0.00529
25 year 0.006246
50 year 0.006839
100 year 0.007342
Flow Frequency Return Periods for Mitigated. POC #10
Return Period Flow(cfs)
2 year 0.03458
5 year 0.044335
10 year 0.051178
25 year 0.06028
50 year 0.067403
100 year 0.07483
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #10
Year Predeveloped Mitigated
1949 0.003 0.046
1950 0.003 0.046
1951 0.006 0.028
1952 0.002 0.022
1953 0.002 0.027
1954 0.002 0.028
1955 0.004 0.033
1956 0.003 0.029
1957 0.002 0.034
1958 0.003 0.028
1959 0.002 0.030
INDIVIDUAL-CB 4/1/2024 12:25:45 PM Page 102
1960 0.004 0.030
1961 0.002 0.029
1962 0.001 0.025
1963 0.002 0.030
1964 0.003 0.029
1965 0.002 0.035
1966 0.002 0.024
1967 0.004 0.041
1968 0.002 0.052
1969 0.002 0.032
1970 0.002 0.032
1971 0.002 0.039
1972 0.005 0.039
1973 0.002 0.024
1974 0.002 0.036
1975 0.003 0.038
1976 0.002 0.029
1977 0.000 0.028
1978 0.002 0.040
1979 0.001 0.050
1980 0.004 0.052
1981 0.002 0.034
1982 0.003 0.050
1983 0.003 0.040
1984 0.002 0.025
1985 0.001 0.033
1986 0.005 0.029
1987 0.004 0.045
1988 0.002 0.027
1989 0.001 0.043
1990 0.009 0.062
1991 0.005 0.052
1992 0.002 0.025
1993 0.002 0.028
1994 0.001 0.026
1995 0.003 0.031
1996 0.007 0.039
1997 0.005 0.032
1998 0.001 0.033
1999 0.005 0.071
2000 0.002 0.033
2001 0.000 0.039
2002 0.002 0.041
2003 0.003 0.040
2004 0.004 0.068
2005 0.003 0.028
2006 0.003 0.026
2007 0.007 0.064
2008 0.009 0.049
2009 0.004 0.047
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #10
Rank Predeveloped Mitigated
1 0.0090 0.0713
2 0.0086 0.0681
3 0.0066 0.0642
4 0.0065 0.0618
INDIVIDUAL-CB 4/1/2024 12:25:45 PM Page 103
5 0.0062 0.0523
6 0.0055 0.0522
7 0.0054 0.0517
8 0.0051 0.0498
9 0.0048 0.0497
10 0.0046 0.0487
11 0.0043 0.0465
12 0.0043 0.0459
13 0.0042 0.0459
14 0.0042 0.0453
15 0.0039 0.0427
16 0.0038 0.0415
17 0.0038 0.0410
18 0.0034 0.0403
19 0.0033 0.0398
20 0.0033 0.0397
21 0.0031 0.0390
22 0.0031 0.0388
23 0.0031 0.0387
24 0.0030 0.0387
25 0.0030 0.0379
26 0.0028 0.0365
27 0.0028 0.0352
28 0.0027 0.0344
29 0.0026 0.0343
30 0.0025 0.0333
31 0.0024 0.0332
32 0.0024 0.0329
33 0.0024 0.0326
34 0.0024 0.0322
35 0.0023 0.0322
36 0.0023 0.0322
37 0.0023 0.0308
38 0.0022 0.0304
39 0.0022 0.0303
40 0.0022 0.0299
41 0.0021 0.0293
42 0.0021 0.0292
43 0.0020 0.0291
44 0.0020 0.0291
45 0.0019 0.0289
46 0.0019 0.0285
47 0.0019 0.0284
48 0.0019 0.0283
49 0.0018 0.0279
50 0.0018 0.0276
51 0.0017 0.0276
52 0.0017 0.0274
53 0.0016 0.0266
54 0.0015 0.0260
55 0.0012 0.0258
56 0.0012 0.0253
57 0.0011 0.0252
58 0.0011 0.0249
59 0.0007 0.0243
60 0.0004 0.0242
61 0.0003 0.0221
INDIVIDUAL-CB 4/1/2024 12:25:45 PM Page 109
POC 11
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #11
Total Pervious Area:0.094
Total Impervious Area:0
Mitigated Landuse Totals for POC #11
Total Pervious Area:0.016
Total Impervious Area:0.078
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #11
Return Period Flow(cfs)
2 year 0.002764
5 year 0.00434
10 year 0.005234
25 year 0.006181
50 year 0.006767
100 year 0.007265
Flow Frequency Return Periods for Mitigated. POC #11
Return Period Flow(cfs)
2 year 0.033777
5 year 0.043338
10 year 0.050048
25 year 0.058979
50 year 0.065971
100 year 0.073262
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #11
Year Predeveloped Mitigated
1949 0.003 0.045
1950 0.003 0.045
1951 0.006 0.027
1952 0.002 0.022
1953 0.002 0.026
1954 0.002 0.027
1955 0.004 0.032
1956 0.003 0.029
1957 0.002 0.034
1958 0.003 0.028
1959 0.002 0.029
INDIVIDUAL-CB 4/1/2024 12:26:17 PM Page 110
1960 0.004 0.030
1961 0.002 0.028
1962 0.001 0.025
1963 0.002 0.030
1964 0.003 0.028
1965 0.002 0.034
1966 0.002 0.024
1967 0.004 0.040
1968 0.002 0.051
1969 0.002 0.032
1970 0.002 0.031
1971 0.002 0.038
1972 0.005 0.038
1973 0.002 0.024
1974 0.002 0.036
1975 0.003 0.037
1976 0.002 0.028
1977 0.000 0.028
1978 0.002 0.039
1979 0.001 0.049
1980 0.004 0.051
1981 0.002 0.034
1982 0.003 0.049
1983 0.003 0.039
1984 0.002 0.024
1985 0.001 0.033
1986 0.005 0.028
1987 0.004 0.044
1988 0.002 0.027
1989 0.001 0.042
1990 0.009 0.061
1991 0.005 0.051
1992 0.002 0.025
1993 0.002 0.028
1994 0.001 0.025
1995 0.003 0.030
1996 0.006 0.038
1997 0.005 0.032
1998 0.001 0.032
1999 0.005 0.070
2000 0.002 0.033
2001 0.000 0.038
2002 0.002 0.041
2003 0.003 0.039
2004 0.004 0.067
2005 0.003 0.027
2006 0.003 0.025
2007 0.007 0.063
2008 0.008 0.048
2009 0.004 0.045
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #11
Rank Predeveloped Mitigated
1 0.0089 0.0698
2 0.0085 0.0666
3 0.0066 0.0628
4 0.0065 0.0608
INDIVIDUAL-CB 4/1/2024 12:26:17 PM Page 111
5 0.0061 0.0512
6 0.0054 0.0509
7 0.0053 0.0507
8 0.0051 0.0486
9 0.0048 0.0485
10 0.0045 0.0478
11 0.0043 0.0453
12 0.0042 0.0449
13 0.0042 0.0448
14 0.0041 0.0442
15 0.0039 0.0415
16 0.0038 0.0407
17 0.0038 0.0401
18 0.0034 0.0394
19 0.0033 0.0388
20 0.0033 0.0387
21 0.0031 0.0381
22 0.0030 0.0379
23 0.0030 0.0378
24 0.0030 0.0377
25 0.0030 0.0370
26 0.0028 0.0357
27 0.0027 0.0345
28 0.0027 0.0337
29 0.0026 0.0335
30 0.0024 0.0325
31 0.0024 0.0325
32 0.0024 0.0321
33 0.0023 0.0318
34 0.0023 0.0316
35 0.0023 0.0315
36 0.0023 0.0315
37 0.0022 0.0301
38 0.0022 0.0297
39 0.0021 0.0296
40 0.0021 0.0291
41 0.0021 0.0287
42 0.0021 0.0284
43 0.0020 0.0284
44 0.0020 0.0284
45 0.0019 0.0282
46 0.0019 0.0277
47 0.0019 0.0276
48 0.0019 0.0276
49 0.0018 0.0273
50 0.0018 0.0271
51 0.0017 0.0270
52 0.0017 0.0267
53 0.0016 0.0259
54 0.0014 0.0253
55 0.0012 0.0252
56 0.0012 0.0247
57 0.0011 0.0246
58 0.0011 0.0243
59 0.0007 0.0237
60 0.0004 0.0236
61 0.0003 0.0216
INDIVIDUAL-CB 4/1/2024 12:26:17 PM Page 117
POC 12
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #12
Total Pervious Area:0.024
Total Impervious Area:0
Mitigated Landuse Totals for POC #12
Total Pervious Area:0.002
Total Impervious Area:0.022
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #12
Return Period Flow(cfs)
2 year 0.000706
5 year 0.001108
10 year 0.001336
25 year 0.001578
50 year 0.001728
100 year 0.001855
Flow Frequency Return Periods for Mitigated. POC #12
Return Period Flow(cfs)
2 year 0.009797
5 year 0.012512
10 year 0.01441
25 year 0.01693
50 year 0.018898
100 year 0.020945
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #12
Year Predeveloped Mitigated
1949 0.001 0.013
1950 0.001 0.013
1951 0.002 0.008
1952 0.000 0.006
1953 0.000 0.008
1954 0.001 0.008
1955 0.001 0.009
1956 0.001 0.009
1957 0.001 0.009
1958 0.001 0.008
1959 0.001 0.009
INDIVIDUAL-CB 4/1/2024 12:26:49 PM Page 118
1960 0.001 0.009
1961 0.001 0.008
1962 0.000 0.007
1963 0.001 0.009
1964 0.001 0.008
1965 0.000 0.010
1966 0.000 0.007
1967 0.001 0.011
1968 0.001 0.015
1969 0.001 0.009
1970 0.000 0.009
1971 0.001 0.011
1972 0.001 0.011
1973 0.001 0.007
1974 0.001 0.010
1975 0.001 0.011
1976 0.001 0.008
1977 0.000 0.008
1978 0.000 0.012
1979 0.000 0.014
1980 0.001 0.015
1981 0.000 0.009
1982 0.001 0.014
1983 0.001 0.011
1984 0.000 0.007
1985 0.000 0.009
1986 0.001 0.008
1987 0.001 0.013
1988 0.000 0.008
1989 0.000 0.013
1990 0.002 0.016
1991 0.001 0.014
1992 0.001 0.007
1993 0.001 0.009
1994 0.000 0.008
1995 0.001 0.009
1996 0.002 0.011
1997 0.001 0.009
1998 0.000 0.009
1999 0.001 0.020
2000 0.001 0.009
2001 0.000 0.011
2002 0.001 0.012
2003 0.001 0.012
2004 0.001 0.019
2005 0.001 0.007
2006 0.001 0.007
2007 0.002 0.018
2008 0.002 0.013
2009 0.001 0.014
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #12
Rank Predeveloped Mitigated
1 0.0023 0.0199
2 0.0022 0.0193
3 0.0017 0.0181
4 0.0017 0.0163
INDIVIDUAL-CB 4/1/2024 12:26:49 PM Page 119
5 0.0016 0.0152
6 0.0014 0.0151
7 0.0014 0.0144
8 0.0013 0.0142
9 0.0012 0.0137
10 0.0012 0.0136
11 0.0011 0.0131
12 0.0011 0.0130
13 0.0011 0.0129
14 0.0011 0.0127
15 0.0010 0.0126
16 0.0010 0.0119
17 0.0010 0.0117
18 0.0009 0.0117
19 0.0008 0.0114
20 0.0008 0.0112
21 0.0008 0.0111
22 0.0008 0.0111
23 0.0008 0.0110
24 0.0008 0.0110
25 0.0008 0.0107
26 0.0007 0.0102
27 0.0007 0.0097
28 0.0007 0.0095
29 0.0007 0.0094
30 0.0006 0.0094
31 0.0006 0.0092
32 0.0006 0.0092
33 0.0006 0.0092
34 0.0006 0.0090
35 0.0006 0.0089
36 0.0006 0.0089
37 0.0006 0.0088
38 0.0006 0.0087
39 0.0005 0.0087
40 0.0005 0.0086
41 0.0005 0.0085
42 0.0005 0.0085
43 0.0005 0.0084
44 0.0005 0.0083
45 0.0005 0.0082
46 0.0005 0.0082
47 0.0005 0.0081
48 0.0005 0.0081
49 0.0005 0.0080
50 0.0005 0.0079
51 0.0004 0.0079
52 0.0004 0.0076
53 0.0004 0.0075
54 0.0004 0.0074
55 0.0003 0.0073
56 0.0003 0.0072
57 0.0003 0.0071
58 0.0003 0.0070
59 0.0002 0.0070
60 0.0001 0.0070
61 0.0001 0.0063
INDIVIDUAL-CB 4/1/2024 12:26:49 PM Page 125
POC 13
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #13
Total Pervious Area:0.121
Total Impervious Area:0
Mitigated Landuse Totals for POC #13
Total Pervious Area:0.062
Total Impervious Area:0.059
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #13
Return Period Flow(cfs)
2 year 0.003558
5 year 0.005587
10 year 0.006737
25 year 0.007956
50 year 0.00871
100 year 0.009352
Flow Frequency Return Periods for Mitigated. POC #13
Return Period Flow(cfs)
2 year 0.028813
5 year 0.038588
10 year 0.045535
25 year 0.054871
50 year 0.062242
100 year 0.069978
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #13
Year Predeveloped Mitigated
1949 0.003 0.042
1950 0.004 0.038
1951 0.008 0.025
1952 0.002 0.017
1953 0.002 0.020
1954 0.003 0.023
1955 0.005 0.026
1956 0.004 0.024
1957 0.003 0.031
1958 0.004 0.023
1959 0.003 0.021
INDIVIDUAL-CB 4/1/2024 12:27:19 PM Page 126
1960 0.005 0.027
1961 0.003 0.025
1962 0.002 0.019
1963 0.003 0.026
1964 0.003 0.022
1965 0.002 0.032
1966 0.002 0.019
1967 0.005 0.038
1968 0.003 0.042
1969 0.003 0.029
1970 0.002 0.027
1971 0.003 0.033
1972 0.006 0.037
1973 0.003 0.017
1974 0.003 0.032
1975 0.004 0.032
1976 0.003 0.024
1977 0.000 0.023
1978 0.002 0.029
1979 0.001 0.036
1980 0.006 0.048
1981 0.002 0.029
1982 0.004 0.045
1983 0.004 0.031
1984 0.002 0.021
1985 0.001 0.028
1986 0.006 0.025
1987 0.005 0.035
1988 0.002 0.020
1989 0.001 0.029
1990 0.011 0.066
1991 0.007 0.051
1992 0.003 0.021
1993 0.003 0.019
1994 0.001 0.018
1995 0.004 0.025
1996 0.008 0.035
1997 0.007 0.029
1998 0.002 0.026
1999 0.007 0.064
2000 0.003 0.029
2001 0.000 0.028
2002 0.003 0.039
2003 0.004 0.035
2004 0.005 0.059
2005 0.004 0.025
2006 0.004 0.024
2007 0.008 0.061
2008 0.011 0.048
2009 0.005 0.032
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #13
Rank Predeveloped Mitigated
1 0.0114 0.0663
2 0.0109 0.0636
3 0.0085 0.0606
4 0.0083 0.0590
INDIVIDUAL-CB 4/1/2024 12:27:19 PM Page 127
5 0.0078 0.0507
6 0.0070 0.0485
7 0.0069 0.0479
8 0.0065 0.0446
9 0.0062 0.0422
10 0.0058 0.0420
11 0.0055 0.0390
12 0.0055 0.0382
13 0.0054 0.0382
14 0.0053 0.0371
15 0.0050 0.0362
16 0.0049 0.0352
17 0.0048 0.0348
18 0.0044 0.0347
19 0.0042 0.0327
20 0.0042 0.0323
21 0.0040 0.0321
22 0.0039 0.0317
23 0.0039 0.0315
24 0.0038 0.0309
25 0.0038 0.0309
26 0.0036 0.0293
27 0.0035 0.0291
28 0.0035 0.0288
29 0.0034 0.0288
30 0.0031 0.0285
31 0.0031 0.0285
32 0.0030 0.0284
33 0.0030 0.0281
34 0.0030 0.0270
35 0.0030 0.0270
36 0.0030 0.0263
37 0.0029 0.0258
38 0.0028 0.0255
39 0.0028 0.0254
40 0.0028 0.0252
41 0.0026 0.0251
42 0.0026 0.0249
43 0.0026 0.0246
44 0.0026 0.0244
45 0.0025 0.0244
46 0.0025 0.0236
47 0.0024 0.0234
48 0.0024 0.0232
49 0.0024 0.0225
50 0.0023 0.0220
51 0.0022 0.0211
52 0.0022 0.0210
53 0.0020 0.0205
54 0.0019 0.0198
55 0.0016 0.0196
56 0.0015 0.0195
57 0.0014 0.0195
58 0.0014 0.0188
59 0.0009 0.0175
60 0.0005 0.0174
61 0.0003 0.0170
INDIVIDUAL-CB 4/1/2024 12:27:19 PM Page 133
POC 14
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #14
Total Pervious Area:0.164
Total Impervious Area:0
Mitigated Landuse Totals for POC #14
Total Pervious Area:0.062
Total Impervious Area:0.102
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #14
Return Period Flow(cfs)
2 year 0.004822
5 year 0.007573
10 year 0.009132
25 year 0.010783
50 year 0.011805
100 year 0.012675
Flow Frequency Return Periods for Mitigated. POC #14
Return Period Flow(cfs)
2 year 0.043696
5 year 0.057195
10 year 0.066622
25 year 0.079116
50 year 0.088862
100 year 0.098993
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #14
Year Predeveloped Mitigated
1949 0.005 0.062
1950 0.006 0.056
1951 0.011 0.038
1952 0.003 0.029
1953 0.003 0.031
1954 0.004 0.036
1955 0.007 0.040
1956 0.005 0.039
1957 0.004 0.047
1958 0.005 0.035
1959 0.004 0.033
INDIVIDUAL-CB 4/1/2024 12:27:50 PM Page 134
1960 0.007 0.039
1961 0.004 0.039
1962 0.003 0.031
1963 0.003 0.038
1964 0.005 0.035
1965 0.003 0.049
1966 0.003 0.030
1967 0.007 0.055
1968 0.004 0.061
1969 0.004 0.044
1970 0.003 0.041
1971 0.004 0.049
1972 0.008 0.056
1973 0.004 0.027
1974 0.004 0.047
1975 0.005 0.048
1976 0.004 0.036
1977 0.000 0.034
1978 0.003 0.042
1979 0.002 0.057
1980 0.007 0.063
1981 0.003 0.045
1982 0.006 0.067
1983 0.005 0.049
1984 0.003 0.033
1985 0.002 0.045
1986 0.008 0.038
1987 0.007 0.057
1988 0.003 0.033
1989 0.002 0.041
1990 0.015 0.095
1991 0.009 0.072
1992 0.004 0.032
1993 0.004 0.027
1994 0.001 0.027
1995 0.005 0.040
1996 0.011 0.048
1997 0.009 0.044
1998 0.002 0.040
1999 0.009 0.093
2000 0.004 0.044
2001 0.001 0.044
2002 0.004 0.060
2003 0.005 0.048
2004 0.007 0.086
2005 0.005 0.039
2006 0.006 0.035
2007 0.011 0.085
2008 0.015 0.070
2009 0.007 0.050
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #14
Rank Predeveloped Mitigated
1 0.0155 0.0950
2 0.0148 0.0931
3 0.0115 0.0857
4 0.0113 0.0852
INDIVIDUAL-CB 4/1/2024 12:27:50 PM Page 135
5 0.0106 0.0721
6 0.0094 0.0704
7 0.0093 0.0671
8 0.0089 0.0632
9 0.0084 0.0618
10 0.0079 0.0612
11 0.0075 0.0597
12 0.0074 0.0569
13 0.0073 0.0566
14 0.0072 0.0563
15 0.0067 0.0556
16 0.0066 0.0546
17 0.0066 0.0505
18 0.0059 0.0494
19 0.0058 0.0493
20 0.0057 0.0490
21 0.0054 0.0478
22 0.0053 0.0477
23 0.0053 0.0477
24 0.0052 0.0472
25 0.0052 0.0466
26 0.0048 0.0451
27 0.0048 0.0450
28 0.0047 0.0444
29 0.0046 0.0444
30 0.0043 0.0442
31 0.0042 0.0438
32 0.0041 0.0424
33 0.0041 0.0412
34 0.0041 0.0411
35 0.0041 0.0402
36 0.0040 0.0396
37 0.0039 0.0396
38 0.0038 0.0391
39 0.0037 0.0390
40 0.0037 0.0389
41 0.0036 0.0387
42 0.0036 0.0384
43 0.0035 0.0381
44 0.0035 0.0378
45 0.0034 0.0358
46 0.0033 0.0356
47 0.0033 0.0352
48 0.0033 0.0351
49 0.0032 0.0351
50 0.0031 0.0338
51 0.0030 0.0330
52 0.0029 0.0329
53 0.0027 0.0327
54 0.0025 0.0325
55 0.0021 0.0314
56 0.0020 0.0311
57 0.0019 0.0300
58 0.0019 0.0287
59 0.0013 0.0275
60 0.0007 0.0270
61 0.0005 0.0268
INDIVIDUAL-CB 4/1/2024 12:27:50 PM Page 141
POC 15
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #15
Total Pervious Area:0.158
Total Impervious Area:0
Mitigated Landuse Totals for POC #15
Total Pervious Area:0.057
Total Impervious Area:0.101
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #15
Return Period Flow(cfs)
2 year 0.004645
5 year 0.007296
10 year 0.008798
25 year 0.010389
50 year 0.011374
100 year 0.012211
Flow Frequency Return Periods for Mitigated. POC #15
Return Period Flow(cfs)
2 year 0.042907
5 year 0.056008
10 year 0.065137
25 year 0.077217
50 year 0.086625
100 year 0.096394
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #15
Year Predeveloped Mitigated
1949 0.005 0.060
1950 0.006 0.056
1951 0.010 0.037
1952 0.003 0.028
1953 0.003 0.031
1954 0.004 0.035
1955 0.006 0.039
1956 0.005 0.038
1957 0.004 0.046
1958 0.005 0.035
1959 0.004 0.033
INDIVIDUAL-CB 4/1/2024 12:28:21 PM Page 142
1960 0.007 0.038
1961 0.004 0.038
1962 0.002 0.031
1963 0.003 0.038
1964 0.004 0.034
1965 0.003 0.048
1966 0.003 0.030
1967 0.006 0.053
1968 0.004 0.060
1969 0.004 0.044
1970 0.003 0.040
1971 0.003 0.048
1972 0.008 0.054
1973 0.003 0.027
1974 0.004 0.046
1975 0.005 0.047
1976 0.004 0.035
1977 0.000 0.033
1978 0.003 0.042
1979 0.002 0.056
1980 0.007 0.062
1981 0.003 0.044
1982 0.006 0.066
1983 0.005 0.049
1984 0.003 0.032
1985 0.002 0.044
1986 0.008 0.037
1987 0.007 0.056
1988 0.003 0.033
1989 0.002 0.041
1990 0.015 0.092
1991 0.009 0.070
1992 0.003 0.032
1993 0.004 0.026
1994 0.001 0.027
1995 0.005 0.039
1996 0.011 0.047
1997 0.009 0.043
1998 0.002 0.040
1999 0.009 0.091
2000 0.004 0.043
2001 0.001 0.043
2002 0.004 0.058
2003 0.005 0.047
2004 0.007 0.084
2005 0.005 0.038
2006 0.006 0.034
2007 0.011 0.083
2008 0.014 0.069
2009 0.007 0.050
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #15
Rank Predeveloped Mitigated
1 0.0149 0.0922
2 0.0143 0.0910
3 0.0111 0.0840
4 0.0109 0.0827
INDIVIDUAL-CB 4/1/2024 12:28:21 PM Page 143
5 0.0102 0.0702
6 0.0091 0.0686
7 0.0090 0.0656
8 0.0085 0.0616
9 0.0081 0.0604
10 0.0076 0.0600
11 0.0072 0.0583
12 0.0071 0.0562
13 0.0070 0.0559
14 0.0069 0.0556
15 0.0065 0.0543
16 0.0064 0.0532
17 0.0063 0.0500
18 0.0057 0.0487
19 0.0055 0.0484
20 0.0055 0.0480
21 0.0052 0.0468
22 0.0051 0.0465
23 0.0051 0.0465
24 0.0050 0.0462
25 0.0050 0.0457
26 0.0047 0.0443
27 0.0046 0.0443
28 0.0046 0.0435
29 0.0044 0.0435
30 0.0041 0.0433
31 0.0040 0.0433
32 0.0040 0.0418
33 0.0039 0.0408
34 0.0039 0.0403
35 0.0039 0.0396
36 0.0039 0.0390
37 0.0038 0.0389
38 0.0037 0.0383
39 0.0036 0.0383
40 0.0036 0.0382
41 0.0035 0.0379
42 0.0035 0.0377
43 0.0034 0.0373
44 0.0033 0.0370
45 0.0032 0.0352
46 0.0032 0.0349
47 0.0032 0.0345
48 0.0031 0.0345
49 0.0031 0.0344
50 0.0030 0.0332
51 0.0029 0.0327
52 0.0028 0.0326
53 0.0026 0.0322
54 0.0024 0.0319
55 0.0021 0.0310
56 0.0020 0.0308
57 0.0018 0.0296
58 0.0018 0.0284
59 0.0012 0.0272
60 0.0006 0.0268
61 0.0004 0.0265
INDIVIDUAL-CB 4/1/2024 12:28:21 PM Page 149
POC 16
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #16
Total Pervious Area:0.144
Total Impervious Area:0
Mitigated Landuse Totals for POC #16
Total Pervious Area:0.05
Total Impervious Area:0.094
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #16
Return Period Flow(cfs)
2 year 0.004234
5 year 0.006649
10 year 0.008018
25 year 0.009468
50 year 0.010366
100 year 0.011129
Flow Frequency Return Periods for Mitigated. POC #16
Return Period Flow(cfs)
2 year 0.039683
5 year 0.051692
10 year 0.060048
25 year 0.071089
50 year 0.079679
100 year 0.088591
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #16
Year Predeveloped Mitigated
1949 0.004 0.056
1950 0.005 0.052
1951 0.009 0.034
1952 0.003 0.026
1953 0.002 0.029
1954 0.004 0.033
1955 0.006 0.036
1956 0.005 0.035
1957 0.004 0.043
1958 0.004 0.032
1959 0.004 0.030
INDIVIDUAL-CB 4/1/2024 12:28:52 PM Page 150
1960 0.006 0.035
1961 0.004 0.035
1962 0.002 0.029
1963 0.003 0.035
1964 0.004 0.032
1965 0.003 0.044
1966 0.003 0.027
1967 0.006 0.049
1968 0.004 0.056
1969 0.004 0.040
1970 0.003 0.037
1971 0.003 0.045
1972 0.007 0.050
1973 0.003 0.025
1974 0.003 0.042
1975 0.005 0.043
1976 0.003 0.032
1977 0.000 0.031
1978 0.003 0.039
1979 0.002 0.052
1980 0.007 0.057
1981 0.003 0.041
1982 0.005 0.060
1983 0.005 0.045
1984 0.003 0.030
1985 0.002 0.041
1986 0.007 0.034
1987 0.006 0.052
1988 0.003 0.030
1989 0.002 0.038
1990 0.014 0.085
1991 0.008 0.065
1992 0.003 0.030
1993 0.003 0.025
1994 0.001 0.025
1995 0.005 0.036
1996 0.010 0.043
1997 0.008 0.040
1998 0.002 0.037
1999 0.008 0.084
2000 0.003 0.040
2001 0.001 0.040
2002 0.004 0.054
2003 0.005 0.043
2004 0.006 0.077
2005 0.004 0.035
2006 0.005 0.032
2007 0.010 0.076
2008 0.013 0.063
2009 0.006 0.046
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #16
Rank Predeveloped Mitigated
1 0.0136 0.0846
2 0.0130 0.0840
3 0.0101 0.0775
4 0.0099 0.0758
INDIVIDUAL-CB 4/1/2024 12:28:52 PM Page 151
5 0.0093 0.0645
6 0.0083 0.0630
7 0.0082 0.0604
8 0.0078 0.0567
9 0.0073 0.0557
10 0.0069 0.0555
11 0.0066 0.0538
12 0.0065 0.0522
13 0.0064 0.0519
14 0.0063 0.0517
15 0.0059 0.0500
16 0.0058 0.0489
17 0.0058 0.0465
18 0.0052 0.0452
19 0.0051 0.0447
20 0.0050 0.0443
21 0.0047 0.0432
22 0.0046 0.0429
23 0.0046 0.0428
24 0.0046 0.0427
25 0.0045 0.0421
26 0.0043 0.0410
27 0.0042 0.0410
28 0.0042 0.0402
29 0.0040 0.0402
30 0.0037 0.0401
31 0.0036 0.0401
32 0.0036 0.0387
33 0.0036 0.0379
34 0.0036 0.0373
35 0.0036 0.0368
36 0.0035 0.0361
37 0.0034 0.0361
38 0.0034 0.0354
39 0.0033 0.0354
40 0.0033 0.0353
41 0.0032 0.0350
42 0.0032 0.0348
43 0.0031 0.0345
44 0.0030 0.0341
45 0.0029 0.0325
46 0.0029 0.0323
47 0.0029 0.0320
48 0.0029 0.0319
49 0.0028 0.0318
50 0.0028 0.0307
51 0.0026 0.0304
52 0.0026 0.0303
53 0.0024 0.0298
54 0.0022 0.0296
55 0.0019 0.0287
56 0.0018 0.0286
57 0.0017 0.0274
58 0.0017 0.0264
59 0.0011 0.0253
60 0.0006 0.0249
61 0.0004 0.0245
INDIVIDUAL-CB 4/1/2024 12:28:52 PM Page 157
Model Default Modifications
Total of 0 changes have been made.
PERLND Changes
No PERLND changes have been made.
IMPLND Changes
No IMPLND changes have been made.
INDIVIDUAL-CB 4/1/2024 12:28:52 PM Page 159
Mitigated Schematic
INDIVIDUAL-CB 4/1/2024 12:28:53 PM Page 174
Mitigated HSPF Message File
INDIVIDUAL-CB 4/1/2024 12:28:53 PM Page 175
Disclaimer
Legal Notice
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. 2005-2024; All
Rights Reserved.
Clear Creek Solutions, Inc.
6200 Capitol Blvd. Ste F
Olympia, WA. 98501
Toll Free 1(866)943-0304
Local (360)943-0304
www.clearcreeksolutions.com
20069 - exist. vault 3/19/2024 4:35:45 PM Page 37
Disclaimer
Legal Notice
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. 2005-2024; All
Rights Reserved.
Clear Creek Solutions, Inc.
6200 Capitol Blvd. Ste F
Olympia, WA. 98501
Toll Free 1(866)943-0304
Local (360)943-0304
www.clearcreeksolutions.com
FES Project no. 20069 Page 57
APPENDIX E: STORMFILTER DETAILS
SFMH#1(W) 288.59LCPE12"(S) 290.82LCPE12"300.590.0167 CFS7 PSC18"0.0266 CFS0.1153 CFSZPG212"6"
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 1
April 2017
GENERAL USE LEVEL DESIGNATION FOR BASIC (TSS) TREATMENT
For
CONTECH Engineered Solutions
Stormwater Management StormFilter®
With ZPG Media at 1 gpm/sq ft media surface area
Ecology’s Decision:
Based on the CONTECH Engineered Solutions’ (CONTECH) application
submissions, Ecology hereby issues a General Use Level Designation (GULD) for the
Stormwater Management StormFilter® (StormFilter):
1. As a basic stormwater treatment practice for total suspended solids (TSS)
removal,
Using ZPG™ media (zeolite/perlite/granular activated carbon), with the size
distribution described below,
Sized at a hydraulic loading rate of 1 gpm/ft2 of media surface area, per
Table 1, and
Internal bypassing needs to be consistent with the design guidelines in
CONTECH’s current product design manual.
Table 1. StormFilter Design Flow Rates per Cartridge
2. Ecology approves StormFilter systems containing ZPG™ media for treatment at
the hydraulic loading rates shown in Table 1, and sized based on the water
quality design flow rate for an off-line system when using an external bypass
vault or a treatment vault with an internal bypass. Contech designs their
StormFilter systems to maintain treatment of the water quality design flow while
routing excess flows around the treatment chamber during periods of peak
bypass. The water quality design flow rates are calculated using the following
procedures:
Western Washington: For treatment installed upstream of detention or
retention, the water quality design flow rate is the peak 15-minute flow rate
as calculated using the latest version of the Western Washington Hydrology
Model or other Ecology-approved continuous runoff model.
Effective Cartridge Height (inches) 12 18 27
Cartridge Flow Rate (gpm/cartridge) 5 7.5 11.3
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 2
Eastern Washington: For treatment installed upstream of detention or
retention, the water quality design flow rate is the peak 15-minute flow rate
as calculated using one of the three methods described in Chapter 2.2.5 of the
Stormwater Management Manual for Eastern Washington (SWMMEW) or
local manual.
Entire State: For treatment installed downstream of detention, the water
quality design flow rate is the full 2-year release rate of the detention facility.
3. This designation has no expiration date, but Ecology may amend or revoke it.
Ecology’s Conditions of Use:
The StormFilter with ZPG media shall comply with the following conditions:
1. Design, install, operate, and maintain the StormFilter with ZPG media in
accordance with applicable Contech Engineered Solutions manuals,
documents, and the Ecology Decision.
2. Install StormFilter systems to bypass flows exceeding the water quality
treatment rate. Additionally, high flows will not re-suspend captured
sediments. Design StormFilter systems in accordance with the performance
goals in Ecology's most recent Stormwater Manual and CONTECH’s
Product Design Manual Version 4.1 (April 2006), or most current version,
unless otherwise specified.
3. Owners must follow the design, pretreatment, land use application, and
maintenance criteria in CONTECH’s Design Manual.
4. Pretreatment of TSS and oil and grease may be necessary, and designers
shall provide pre-treatment in accordance with the most current versions of
the CONTECH’s Product Design Manual (April 2006) or the applicable
Ecology Stormwater Manual. Design pre-treatment using the performance
criteria and pretreatment practices provided on Ecology’s “Evaluation of
Emerging Stormwater Treatment Technologies” website.
5. Maintenance: The required maintenance interval for stormwater treatment
devices is often dependent upon the degree of pollutant loading from a
particular drainage basin. Therefore, Ecology does not endorse or
recommend a “one size fits all” maintenance cycle for a particular model/size
of manufactured filter treatment device.
Typically, CONTECH designs StormFilter systems for a target filter
media replacement interval of 12 months. Maintenance includes
removing accumulated sediment from the vault, and replacing spent
cartridges with recharged cartridges.
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Indications of the need for maintenance include effluent flow decreasing
to below the design flow rate, as indicated by the scumline above the
shoulder of the cartridge.
Owners/operators must inspect StormFilter with ZPG media for a
minimum of twelve months from the start of post-construction operation
to determine site-specific maintenance schedules and requirements. You
must conduct inspections monthly during the wet season, and every other
month during the dry season. (According to the SWMMWW, the wet
season in western Washington is October 1 to April 30. According to
SWMMEW, the wet season in eastern Washington is October 1 to June
30). After the first year of operation, owners/operators must conduct
inspections based on the findings during the first year of inspections.
Conduct inspections by qualified personnel, follow manufacturer’s
guidelines, and use methods capable of determining either a decrease in
treated effluent flowrate and/or a decrease in pollutant removal ability.
When inspections are performed, the following findings typically serve as
maintenance triggers:
Accumulated vault sediment depths exceed an average of 2 inches, or
Accumulated sediment depths on the tops of the cartridges exceed an
average of 0.5 inches, or
Standing water remains in the vault between rain events, or
Bypass occurs during storms smaller than the design storm.
Note: If excessive floatables (trash and debris) are present, perform a
minor maintenance consisting of gross solids removal, not cartridge
replacement.
6. CONTECH shall maintain readily available reports listed under
“Application Documents” (above) as public, as well as the documentation
submitted with its previous conditional use designation application.
CONTECH shall provide links to this information from its corporate
website, and make this information available upon request, at no cost and in
a timely manner.
7. ZPG™ media used shall conform with the following specifications:
Each cartridge contains a total of approximately 2.6 cubic feet of media.
The ZPG™ cartridge consists of an outer layer of perlite that is
approximately 1.3 cubic feet in volume and an inner layer, consisting of a
mixture of 90% zeolite and 10% granular activated carbon, which is
approximately 1.3 cubic feet in volume.
Perlite Media: Perlite media shall be made of natural siliceous volcanic
rock free of any debris or foreign matter. The expanded perlite shall
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 4
have a bulk density ranging from 6.5 to 8.5 lbs per cubic foot and particle
sizes ranging from 0.09” (#8 mesh) to 0.38” (3/8” mesh).
Zeolite Media: Zeolite media shall be made of naturally occurring
clinoptilolite. The zeolite media shall have a bulk density ranging from
44 to 50 lbs per cubic foot and particle sizes ranging from 0.13” (#6 mesh)
to 0.19” (#4 mesh). Additionally, the cation exchange capacity (CEC) of
zeolite shall range from approximately 1.0 to 2.2 meq/g.
Granular Activated Carbon: Granular activated carbon (GAC) shall be
made of lignite coal that has been steam-activated. The GAC media shall
have a bulk density ranging from 28 to 31 lbs per cubic foot and particle
sizes ranging from a 0.09” (#8 mesh) to 0.19” (#4 mesh).
Approved Alternate Configurations
Peak Diversion StormFilter
1. The Peak Diversion StormFilter allows for off-line bypass within the StormFilter
structure. Design capture flows and peak flows enter the inlet bay which contains an
internal weir. The internal weir allows design flows to enter the cartridge bay through
a transfer hole located at the bottom of the inlet bay while the unit routs higher flows
around the cartridge bay.
2. To select the size of the Peak Diversion StormFilter unit, the designer must determine
the number of cartridges required and size of the standard StormFilter using the site-
specific water quality design flow and the StormFilter Design Flow Rates per
Cartridge as described above.
3. New owners may not install the Peak Diversion StormFilter at an elevation or in a
location where backwatering may occur.
Applicant: Contech Engineered Solutions
Applicant’s Address: 11835 NE Glenn Widing Dr.
Portland, OR 97220
Application Documents:
The applicant’s master report, titled, “The Stormwater Management StormFilter
Basic Treatment Application for General Use Level Designation in Washington”,
Stormwater Management, Inc., November 1, 2004, includes the following reports:
(Public) Evaluation of the Stormwater Management StormFilter Treatment
System: Data Validation Report and Summary of the Technical Evaluation
Engineering Report (TEER) by Stormwater Management Inc., October 29, 2004
Ecology’s technology assessment protocol requires the applicant to hire an
independent consultant to complete the following work:
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 5
1. Complete the data validation report.
2. Prepare a TEER summary, including a testing summary and conclusions
compared with the supplier’s performance claims.
3. Provide a recommendation of the appropriate technology use level.
4. Work with Ecology to post recommend relevant information on Ecology’s
website.
5. Provide additional testing recommendations, if needed.”
6. This report, authored by Dr. Gary Minton, Ph. D., P.E., Resource Planning
Associates, satisfies the Ecology requirement.
(Public) “Performance of the Stormwater Management StormFilter Relative to the
Washington State Department of Ecology Performance Goals for Basic
Treatment,” is a summary of StormFilter performance that strictly adheres to the
criteria listed in the Guidance for Evaluating Emerging Stormwater Treatment
Technologies, Technology Assessment Protocol – Ecology (TAPE).
“Heritage Marketplace Field Evaluation: Stormwater Management StormFilter
with ZPG™ Media,” is a report showing all of the information collected at Site A
as stated in the SMI Quality Assurance Project Plan (QAPP). This document
contains detailed information regarding each storm event collected at this site, and
it provided a detailed overview of the data and project.
“Lake Stevens Field Evaluation: Stormwater Management StormFilter with
ZPG™ Media,” is a report that corresponds to Site E as stated in the SMI QAPP.
This document contains detailed information regarding each storm collected at
this site, and includes a detailed overview of the data and project.
(Public) “Evaluation of the Stormwater Management StormFilter for the removal
of SIL-CO-SIL 106, a standardized silica product: ZPG™ at 7.5 GPM” is a report
that describes laboratory testing at full design flow.
“Factors Other Than Treatment Performance.”
“State of Washington Installations.”
“Peak Diversion StormFilter” is a technical document demonstrating the Peak
Diversion StormFilter system complies with the Stormwater Management Manual
for Western Washington Volume V Section 4.5.1.
Above-listed documents noted as “public” are available by contacting CONTECH.
Applicant's Use Level Request:
That Ecology grant a General Use Level Designation for Basic Treatment for the
StormFilter using ZPG™ media (zeolite/perlite/granular activated carbon) at a hydraulic
loading rate of 1 gpm/ft2 of media surface area in accordance with Ecology's 2011
Technical Guidance Manual for Evaluating Emerging Stormwater Treatment
Technologies Technology Assessment Protocol – Ecology (TAPE).
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Applicant's Performance Claim:
The combined data from the two field sites reported in the TER (Heritage Marketplace
and Lake Stevens) indicate that the performance of a StormFilter system configured for
inline bypass with ZPG™ media and a hydraulic loading rate of 1 gpm/ft2 of media
surface area meets Ecology performance goals for Basic Treatment.
Ecology’s Recommendations:
Based on the weight of the evidence and using its best professional judgment, Ecology
finds that:
StormFilter, using ZPG™ media and operating at a hydraulic loading rate of no more
than 1 gpm/ft2 of media surface area, is expected to provide effective stormwater
treatment achieving Ecology’s Basic Treatment (TSS removal) performance goals.
Contech demonstrated this is through field and laboratory testing performed in
accordance with the approved protocol. StormFilter is deemed satisfactory with
respect to factors other than treatment performance (e.g., maintenance; see the
protocol’s Appendix B for complete list).
Findings of Fact:
Influent TSS concentrations and particle size distributions were generally within the
range of what Ecology considers “typical” for western Washington (silt-to-silt loam).
Contech sampled thirty-two (32) storm events at two sites for storms from April 2003
to March 2004, of which Contech deemed twenty-two (22) as “qualified” and were
therefore included in the data analysis set.
Statistical analysis of these 22 storm events verifies the data set’s adequacy.
Analyzing all 22 qualifying events, the average influent and effluent concentrations
and aggregate pollutant load reduction are 114 mg/L, 25 mg/L, and 82%,
respectively.
Analyzing all 22 qualifying events based on the estimated average flow rate during
the event (versus the measured peak flow rate), and more heavily weighting those
events near the design rate (versus events either far above or well below the design
rate) does not significantly affect the reported results.
For the 7 qualifying events with influent TSS concentrations greater than 100 mg/L,
the average influent and effluent concentrations and aggregate pollutant load
reduction are 241 mg/L, 34 mg/L, and 89%, respectively. If we exclude the 2 of 7
events that exceed the maximum 300 mg/L specified in Ecology’s guidelines, the
average influent and effluent concentrations and aggregate pollutant load reduction
are 158 mg/L, 35 mg/L, and 78%, respectively.
For the 15 qualifying events with influent TSS concentrations less than 100 mg/L, the
average influent and effluent concentrations and aggregate pollutant load reduction
are 55 mg/L, 20 mg/L, and 61%, respectively. If the 6 of 15 events that fall below the
minimum 33 mg/L TSS specified in Ecology’s guidelines are excluded, the average
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 7
influent and effluent concentrations and aggregate pollutant load reduction are 78
mg/L, 26 mg/L, and 67%, respectively.
For the 8 qualifying events with peak discharge exceeding design flow (ranging from
120 to 257% of the design rate), results ranged from 52% to 96% TSS removal, with
an average of 72%.
Due to the characteristics of the hydrographs, the field results generally reflect flows
below (ranging between 20 and 60 percent of) the tested facilities’ design rate.
During these sub-design flow rate periods, some of the cartridges operate at or near
their individual full design flow rate (generally between 4 and 7.5 GPM for an 18”
cartridge effective height) because their float valves have opened. Float valves
remain closed on the remaining cartridges, which operate at their base “trickle” rate
of 1 to 1.5 GPM.
Laboratory testing using U.S. Silica’s Sil-Co-Sil 106 fine silica product showed an
average 87% TSS removal for testing at 7.5 GPM per cartridge (100% design flow
rate).
Other relevant testing at I-5 Lake Union, Greenville Yards (New Jersey), and Ski Run
Marina (Lake Tahoe) facilities shows consistent TSS removals in the 75 to 85%
range. Note that the evaluators operated the I-5 Lake Union at 50%, 100%, and
125% of design flow.
SMI’s application included a satisfactory “Factors other than treatment performance”
discussion.
Note: Ecology’s 80% TSS removal goal applies to 100 mg/l and greater influent TSS.
Below 100 mg/L influent TSS, the goal is 20 mg/L effluent TSS.
Technology Description:
The Stormwater Management StormFilter® (StormFilter), a flow-through stormwater
filtration system, improves the quality of stormwater runoff from the urban environment
by removing pollutants. The StormFilter can treat runoff from a wide variety of sites
including, but not limited to: retail and commercial development, residential streets,
urban roadways, freeways, and industrial sites such as shipyards, foundries, etc.
Operation:
The StormFilter is typically comprised of a vault that houses rechargeable, media-filled,
filter cartridges. Various media may be used, but this designation covers only the zeolite-
perlite-granulated activated carbon (ZPG™) medium. Stormwater from storm drains
percolates through these media-filled cartridges, which trap particulates and may remove
pollutants such as dissolved metals, nutrients, and hydrocarbons. During the filtering
process, the StormFilter system also removes surface scum and floating oil and grease.
Once filtered through the media, the treated stormwater is directed to a collection pipe or
discharged to an open channel drainage way.
This document includes a bypass schematic for flow rates exceeding the water quality
design flow rate on page 8.
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StormFilter Configurations:
Contech offers the StormFilter in multiple configurations: precast, high flow, catch basin,
curb inlet, linear, volume, corrugated metal pipe, drywell, and CON/Span form. Most
configurations use pre-manufactured units to ease the design and installation process.
Systems may be either uncovered or covered underground units.
The typical precast StormFilter unit is composed of three sections: the energy dissipater,
the filtration bay, and the outlet sump. As Stormwater enters the inlet of the StormFilter
vault through the inlet pipe, piping directs stormwater through the energy dissipater into
the filtration bay where treatment will take place. Once in the filtration bay, the
stormwater ponds and percolates horizontally through the media contained in the
StormFilter cartridges. After passing through the media, the treated water in each
cartridge collects in the cartridge’s center tube from where piping directs it into the outlet
sump by a High Flow Conduit under-drain manifold. The treated water in the outlet
sump discharges through the single outlet pipe to a collection pipe or to an open channel
drainage way. In some applications where you anticipate heavy grit loads, pretreatment
by settling may be necessary.
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 9
Figure 1. Stormwater Management StormFilter Configuration with Bypass
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 10
Figure 2. The StormFilter Cartridge
Cartridge Operation:
As the water level in the filtration bay begins to rise, stormwater enters the StormFilter
cartridge. Stormwater in the cartridge percolates horizontally through the filter media
and passes into the cartridge’s center tube, where the float in the cartridge is in a closed
(downward) position. As the water level in the filtration bay continues to rise, more
water passes through the filter media and into the cartridge’s center tube. Water
displaces the air in the cartridge and it purges from beneath the filter hood through the
one-way check valve located in the cap. Once water fills the center tube there is enough
buoyant force on the float to open the float valve and allow the treated water to flow into
the under-drain manifold. As the treated water drains, it tries to pull in air behind it. This
causes the check valve to close, initiating a siphon that draws polluted water throughout
the full surface area and volume of the filter. Thus, water filters through the entire filter
cartridge throughout the duration of the storm, regardless of the water surface elevation in
the filtration bay. This continues until the water surface elevation drops to the elevation
of the scrubbing regulators. At this point, the siphon begins to break and air quickly
flows beneath the hood through the scrubbing regulators, causing energetic bubbling
between the inner surface of the hood and the outer surface of the filter. This bubbling
agitates and cleans the surface of the filter, releasing accumulated sediments on the
surface, flushing them from beneath the hood, and allowing them to settle to the vault
floor.
Adjustable cartridge flow rate:
Inherent to the design of the StormFilter is the ability to control the individual cartridge
flow rate with an orifice-control disc placed at the base of the cartridge. Depending on
the treatment requirements and on the pollutant characteristics of the influent stream as
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 11
specified in the CONTECH Product Design Manual, operators may adjust the flow rate
through the filter cartridges. By decreasing the flow rate through the filter cartridges, the
influent contact time with the media is increased and the water velocity through the
system is decreased, thus increasing both the level of treatment and the solids removal
efficiencies of the filters, respectively (de Ridder, 2002).
Recommended research and development:
Ecology encourages CONTECH to pursue continuous improvements to the StormFilter.
To that end, CONTECH recommends the following actions:
Determine, through laboratory testing, the relationship between accumulated solids
and flow rate through the cartridge containing the ZPG™ media. Completed 11/05.
Determine the system’s capabilities to meet Ecology’s enhanced, phosphorus, and oil
treatment goals.
Develop easy-to-implement methods of determining that a StormFilter facility
requires maintenance (cleaning and filter replacement).
Contact Information:
Applicant Contact: Jeremiah Lehman
Contech Engineered Solutions
11835 NE Glenn Widing Drive
Portland, OR, 97220
503-258-3136
jlehman@conteches.com
Applicant Web link http://www.conteches.com/
CONTECH - StormFilter® GULD Maintenance Update (November 2012) P a g e | 12
Ecology web link: http://www.ecy.wa.gov/programs/wq/stormwater/newtech/index.html
Ecology Contact: Douglas C. Howie, P.E.
Department of Ecology
Water Quality Program
(360) 407-6444
douglas.howie@ecy.wa.gov
Revision History
Date Revision
Jan 2005 Original Use Level Designation
Dec 2007 Revision
May 2012 Maintenance requirements updated
November 2012 Design Storm and Maintenance requirements updated
January 2013 Updated format to match Ecology standard format
September 2014 Added Peak Diversion StormFilter Alternate Configuration
November 2016 Revised Contech contact information
April 2017 Revised sizing language to note sizing based on Off-line
calculations