HomeMy WebLinkAboutzTIR-3923
FINAL TECHNICAL INFORMATION REPORT
Allura at Tiffany Park
S.E. 18th Street and 124th Place S.E.
Renton, Washington
Prepared for:
Mainvue WA, LLC
1110 - 112th Ave NE, Suite 202
Bellevue, WA 98004
February 23, 2017
Revised March 9, 2017
Revised May 1, 2017
Our Job No. 16055
CIVIL ENGINEERING, LAND PLANNING, SURVEYING
18215 72ND AVENUE SOUTH KENT, WA 98032 (425) 251-6222 (425) 251-8782 FAX
BRANCH OFFICES ¤ TUMWATER, WA ¤ LONG BEACH, CA ¤ WALNUT CREEK, CA ¤ SAN DIEGO, CA
www.barghausen.com
08/23/17
LUA-13001572
U-16006368
PR-13007339 R-3923
FINAL
IN COMPIANCE WITH CITY OF RENTON STANDARDS
DEVELOPMENT ENGINEERING
Ann Fowler 08/24/2017
SURFACE WATER UTILITY
rstraka 08/28/2017
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16055.016.doc
TABLE OF CONTENTS
1.0 PROJECT OVERVIEW
Figure 1 – TIR Worksheet
Figure 2 – Site Location
Figure 3 – Drainage Basins, Subbasins, and Site Characteristics
Figure 4 – Soils
Figure 5 - FEMA Map
2.0 CONDITIONS AND REQUIREMENTS SUMMARY
2.1 Analysis of the Core Requirements
2.2 Analysis of the Special Requirements
2.3 SEPA and Hearing Examiner Conditions
3.0 OFF-SITE ANALYSIS
4.0 FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
A. Existing Site Hydrology
B. Developed Site Hydrology
C. Performance Standards
D. Flow Control System
E. Water Quality System
5.0 CONVEYANCE SYSTEM ANALYSIS AND DESIGN
6.0 SPECIAL REPORTS AND STUDIES
6.1 Reserve at Tiffany Park - Hydraulic Assessment for Offsite Storm System prepared by Ed
McCarthy, PE, PS dated February 24, 2017
6.2 Allura at Tiffany Park - Wetland Hydrology Analysis prepared by Ed McCarthy, PE, PS
dated October 27, 2016
6.3 Revised Tree Protection Plan - Reserve at Tiffany Park prepared by Washington Forestry
Consultants dated October 4, 2016
6.4 Geotechnical Engineering Study Allura at Tiffany Park prepared by Earth Solutions NW,
LLC dated November 11, 2016
7.0 OTHER PERMITS
7.1 Postmaster / Mailbox Locations Approval
7.2 Roadway Easement and Agreement for 124th
7.3 NPDES Permit dated March 22, 2017
8.0 CONSTRUCTION STORMWATER POLLUTION PREVENTION PLAN (CSWPPP) ANALYSIS
AND DESIGN
16055.016.doc
9.0 BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
9.1 Bond Quantities
9.2 Facility Summary Form
10.0 OPERATIONS AND MAINTENANCE MANUAL
APPENDIX
APPENDIX A - Lower Cedar River Basin and Nonpoint Pollution Action Plan
Tab 1.0
16055.016.doc
1.0 PROJECT OVERVIEW
The proposed Plat of Reserve at Tiffany Park is a single-family residential project consisting of
94 lots zoned R8. The project is 21.66 acres in size containing four tax parcels (212305-9044,
212305-9051, 212305-9054, and 212305-9061). The site is located at the dead end of S.E. 18th
Street near the intersection of Monroe Avenue S.E. in a portion of Section 21, Township 23 North,
Range 5 East, W.M., in the City of Renton.
The site is polygonal in shape and ties into two existing road stubs. The first is located in the
northwest corner of the site at the dead-end of S.E. 18th Street. The second road stub is located
to the southwest of the site on the southern side of the Cedar River Pipeline at the dead-end of
124th Place S.E. These road stubs are to be tied into and will be extended into the site to provide
public access and circulation. This site is undeveloped and is currently zoned R8; with a majority
of the site being composed of second-growth forest. The elevations of the site range from 456 to
398. There are four wetlands located on site; three of them are Category 2, with one Category 3.
The site is entirely surrounded by existing single family residences. Along the east property line
is the Mercer Island Pipe Line R/W. Along the south boundary is the Cedar River Pipeline R/W.
Access to the site from 124th Place S.E required the developer to an access easement through
the Cedar River Pipeline R/W this easement is provided in section 7.1 of this report.
On-site soils are mapped as mostly Alderwood, with a small portion along the southern boundary
mapped as Arents. Please refer to the Soils Map in this section. All drainage calculations were
modeled as till soils.
The project will be constructing roadways consisting of curb and gutter, sidewalk, and street
trees. The site will tie into the existing roads at the dead-ends of S.E. 18th Street and 124th
Place S.E. All roads for this project have been designed to be 26 feet wide, with an 8-foot
planter strip at the back of curb and a 5-foot sidewalk (both sides). Overall the proposed public
right-of-way is to be 53 feet in width.
The topography on site is gentle and rolling. The site generally slopes from east to west from
elevation 456 to 398. The project will be mass graded with cuts and fills balanced on-site. The
wetland areas will remain undisturbed along with portions of their buffers. Buffer averaging is
proposed. Other portions of the site will remain undisturbed in an effort to preserve as many
existing trees as possible.
The drainage facilities are required to meet the requirements of the 2009 King County Surface
Water Design Manual (KCSWDM) and the 2010 City of Renton Amendments to the KCSWDM.
The drainage design shall meet at a minimum the Flow Control Duration Standard - Matching
Forested and Basic Water Quality Treatment. The drainage facility located in Tract A is a
detention pond sized for Level 2 Flow Control. Water quality will be met by the use of a
StormFilter for this project. The project will be discharging the drainage from the pond to the
existing drainage system within S.E. 18th Street near the intersection of Lake Youngs Way SE.
Please refer to Section 4.0 for detailed drainage calculations.
Figure 1
TIR Worksheet
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 3/09/17
1 16055.018.doc
Part 1 PROJECT OWNER AND
PROJECT ENGINEER
Part 2 PROJECT LOCATION AND
DESCRIPTION
Project Owner MainVue WA, LLC
Phone (425) 646-4022
Address 1110 112th AVE NE, Suite 202
Bellevue, WA 98004
Project Engineer Barry Talkington
Company Barghausen Consulting Engineers , Inc.
Phone (425) 251-6222
Project Name Allura at Tiffany Park
DDES Permit #
Location Township 23N
Range 05E
Section 21
Site Address East of Intersection of S.E. 18th
ST & Monroe AVE S.E., Renton, WA
Part 3 TYPE OF PERMIT APPLICATION Part 4 OTHER REVIEWS AND PERMITS
Landuse Services
Subdivision / Short Subd. / UPD
Building Services
M/F / Commercial / SFR
Clearing and Grading
Right-of-Way Use
Other
DFW HPA
COE 404
DOE Dam Safety
FEMA Floodplain
COE Wetlands
Other
Shoreline
Management
Structural
Rockery/Vault/
ESA Section 7
Part 5 PLAN AND REPORT INFORMATION
Technical Information Report
Type of Drainage Review Full / Targeted /
(circle): Large Site
Date (include revision November 11, 2016
dates): March 9, 2017
Date of Final:
Site Improvement Plan (Engr. Plans)
Type (circle one): Full / Modified /
Small Site
Date (include revision November 11, 2016
dates): February 27, 2017
Date of Final:
Part 6 ADJUSTMENT APPROVALS
Type (circle one): Standard / Complex / Preapplication / Experimental / Blanket
Description: (include conditions in TIR Section 2)
Date of Approval:
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 3/09/17
2 16055.018.doc
Part 7 MONITORING REQUIREMENTS
Monitoring Required: Yes / No
Start Date:
Completion Date:
Describe:
Part 8 SITE COMMUNITY AND DRAINAGE BASIN
Community Plan :
Special District Overlays:
Drainage Basin: Lower Cedar River Basin
Stormwater Requirements:
Part 9 ONSITE AND ADJACENT SENSITIVE AREAS
River/Stream
Lake
Wetlands
Closed Depression
Floodplain
Other
Steep Slope
Erosion Hazard
Landslide Hazard
Coal Mine Hazard
Seismic Hazard
Habitat Protection
Part 10 SOILS
Soil Type Slopes Erosion Potential
AgC 6-15 percent High
AmC 6-15 percent High
High Groundwater Table (within 5 feet) Sole Source Aquifer
Other Seeps/Springs
Additional Sheets Attached
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 3/09/17
3 16055.018.doc
Part 11 DRAINAGE DESIGN LIMITATIONS
REFERENCE LIMITATION / SITE CONSTRAINT
Core 2 – Offsite Analysis
Sensitive/Critical Areas
SEPA
Other
Additional Sheets Attached
Part 12 TIR SUMMARY SHEET (provide one TIR Summary Sheet per Threshold Discharge Area)
Threshold Discharge Area:
(name or description) Discharge to existing conveyance system at SE 18th ST & Lake Youngs Way SE
Core Requirements (all 8 apply)
Discharge at Natural Location Number of Natural Discharge Locations: 1
Offsite Analysis Level: 1 / 2 / 3 dated:
Flow Control Level: 1 / 2 / 3 or Exemption Number
(incl. facility summary sheet) Small Site BMPs
Conveyance System Spill containment located at: N/A
Erosion and Sediment Control ESC Site Supervisor:
Contact Phone:
After Hours Phone:
Maintenance and Operation Responsibility: Private / Public
If Private, Maintenance Log Required: Yes / No
Financial Guarantees and Provided: Yes / No
Liability
Water Quality Type: Basic / Sens. Lake / Enhanced Basicm / Bog
(include facility summary sheet) or Exemption No.
Landscape Management Plan: Yes / No
Special Requirements (as applicable)
Area Specific Drainage Type: CDA / SDO / MDP / BP / LMP / Shared Fac. / None
Requirements Name:
Floodplain/Floodway Delineation Type: Major / Minor / Exemption / None
100-year Base Blood Elevation (or range):
Datum:
Flood Protection Facilities Describe:
Source Control Describe landuse:
(comm./industrial landuse) Describe any structural controls:
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 3/09/17
4 16055.018.doc
Oil Control High-use Site: Yes / No Treatment BMP:
Maintenance Agreement: Yes / No
with whom?
Other Drainage Structures
Describe:
Part 13 EROSION AND SEDIMENT CONTROL REQUIREMENTS
MINIMUM ESC REQUIREMENTS
DURING CONSTRUCTION
Clearing Limits
Cover Measures
Perimeter Protection
Traffic Area Stabilization
Sediment Retention
Surface Water Control
Dewatering Control
Dust Control
Flow Control
MINIMUM ESC REQUIREMENTS
AFTER CONSTRUCTION
Stabilize Exposed Surfaces
Remove and Restore Temporary ESC Facilities
Clean and Remove All Silt and Debris Ensure
Operation of Permanent Facilities
Flag Limits of SAO and open space
preservation areas
Other
Part 14 STORMWATER FACILITY DESCRIPTIONS (Note: Include Facility Summary and Sketch)
Flow Control Type/Description Water Quality Type/Description
Detention
Infiltration
Regional Facility
Shared Facility
Flow Control
BMPs
Other
Vault
Biofiltration
Wetpool
Media Filtration
Oil Control
Spill Control
Flow Control BMPs
Other
StormFilter
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 3/09/17
5 16055.018.doc
Part 15 EASEMENTS/TRACTS Part 16 STRUCTURAL ANALYSIS
Drainage Easement
Covenant
Native Growth Protection Covenant
Tract
Other
Cast in Place Vault
Retaining Wall
Rockery > 4' High
Structural on Steep Slope
Other
Part 17 SIGNATURE OF PROFESSIONAL ENGINEER
I, or a civil engineer under my supervision, have visited the site. Actual site conditions as observed were
incorporated into this worksheet and the attached Technical Information Report. To the best of my
knowledge the information provided here is accurate.
March 9, 2017
Signed/Date
Figure 2
Site Location
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VICINITY MAP
Job Number
18215 72ND AVENUE SOUTH
KENT, WA 98032
(425) 251-6222
(425) 251-8782
CIVIL ENGINEERING, LAND PLANNING,
SURVEYING, ENVIRONMENTAL SERVICES
N.T.S.N/A 16055
DATE: 11/04/13
Reserve at Tiffany Park
Renton, Washington
P:\16000s\16055\exhibit\graphics\16055 vmap.cdr
REFERENCE: Thomas Guide (2006)
SITE
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ASSESSOR MAP
Job Number
18215 72ND AVENUE SOUTH
KENT, WA 98032
(425) 251-6222
(425) 251-8782
CIVIL ENGINEERING, LAND PLANNING,
SURVEYING, ENVIRONMENTAL SERVICES
N.T.S.N/A 16055
DATE: 11/04/13
Reserve at Tiffany Park
Renton, Washington
P:\16000s\16055\exhibit\graphics\16055 amap.cdr
SITE
REFERENCE: King County Department of Assessments (Dec. 2011)
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ALLURA AT TIFFANY PARK
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Figure 3
Drainage Basins,
Subbasins, and Site
Characteristics
Figure 4
Soils Map
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SOIL SURVEY MAP
Job Number
18215 72ND AVENUE SOUTH
KENT, WA 98032
(425) 251-6222
(425) 251-8782
CIVIL ENGINEERING, LAND PLANNING,
SURVEYING, ENVIRONMENTAL SERVICES
N.T.S.N/A 16055
DATE: 11/04/13
Reserve at Tiffany Park
Renton, Washington
P:\16000s\16055\exhibit\graphics\16055 soil.cdr
REFERENCE: USDA, Natural Resources Conservation Service
LEGEND:
AgC = Alderwood gravelly sandy loam, 6-15% slopes
SITE
AmC = Arents, Alderwood material, 6-15% slopes
Figure 5
FEMA Map
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Title:
FEMA MAP
Job Number
18215 72ND AVENUE SOUTH
KENT, WA 98032
(425) 251-6222
(425) 251-8782
CIVIL ENGINEERING, LAND PLANNING,
SURVEYING, ENVIRONMENTAL SERVICES
N.T.S.N/A 16055
DATE: 11/04/13
Reserve at Tiffany Park
Renton, Washington
P:\16000s\16055\exhibit\graphics\16055 fema.cdr
REFERENCE: Federal Emergency Management Agency (Portion of Map 53033C0983 F, May 1995)
SITE
Tab 2.0
16055.016.doc
2.0 CONDITIONS AND REQUIREMENTS SUMMARY
2.1 Analysis of the Core Requirements
Core Requirement No. 1: Discharge at the Natural Location.
Response: The storm drainage from the project will be conveyed to a detention vault
that will outlet to the existing downstream drainage system in S.E. 18th Street per the
City of Renton’s request. This will serve as our project discharge location. A portion of
the lots along the existing wetlands (Wetland A, Wetland B and Wetland C) will discharge
their roof drains into the wetland areas to maintain wetland hydrology. Please reference
the Wetland Hydrology Analysis prepared by Ed McCarthy, PE, PS dated October 27,
2016 located in section 6.2 of this report. Runoff from these wetlands will be collected
and routed to the on-site drainage facility.
Core Requirement No. 2: Off-Site Analysis.
Response: A Level 1 Downstream Drainage Analysis is provided in Section 3.0 of this
Technical Information Report. A more detailed Level 2 Downstream Drainage Analysis is
provided in section 6.1 of this report as requested by SEPA condition 2.
Core Requirement No. 3: Flow Control.
Response: The project is providing a detention facility which is designed for Flow
Control Duration Standard Matching Forested Site Conditions. At a minimum the sites
developed discharge release will match the predeveloped durations for the range of
predeveloped discharge rates from 50-percent of the 2-year peak flow up to the 50-year
peak flow as well as peak discharge rates for the 2-year and 10-year return periods
Core Requirement No. 4: Conveyance System.
Response: The conveyance and backwater analysis has been provided in Section 5.0 of
this report.
Core Requirement No. 5: Erosion and Sediment Control.
Response: Temporary erosion control measures have been provided in Section 8.0 of
this report.
Core Requirement No. 6: Maintenance and Operations.
Response: A Maintenance and Operations Manual has been provided in Section 10.0 of
this report.
Core Requirement No. 7: Financial Guarantees and Liability.
Response: The project will provide a Bond Quantity Worksheet to establish a bond
amount for installation of public infrastructure, including water, sewer, storm, installation
of the detention facility and water quality filters, and drainage facility restoration and site
stabilization financial guarantee prior to construction.
Core Requirement No. 8: Water Quality.
16055.016.doc
Response: This project utilizes a StormFilter sized for Basic Water Quality Treatment.
Sizing calculations have been provided and prepared by Contech and are located within
section 4.0 of this report.
2.2 Analysis of the Special Requirements
Special Requirement No. 1: Other Adopted Area-Specific Requirements.
Response: The proposed project is not located in a designated Critical Drainage Area.
Special Requirement No. 2: Flood Hazard Area Delineation.
Response: As indicated by the FEMA Map included in this report (portion of Map
53033C0983 F, May 1995), the proposed site does not lie within a floodplain or floodway
or a stream, so this special requirement does not apply.
Special Requirement No. 3: Flood Protection Facilities.
Response: This project does not rely on an existing flood protection facility or propose to
modify or construct a new flood protection facility, so this special requirement does not
apply.
Special Requirement No. 4: Source Control.
Response: The project does not require a commercial building or commercial site
development permit, so this special requirement does not apply.
Special Requirement No. 5: Oil Control.
Response: This site is not classified as a High Use Site given the criteria in the 2009
KCSWDM, so this special requirement does not apply and no special control treatment is
necessary.
Special Requirement No. 6: Aquifer Protection Area
Response: The project site is located within a Zone 2 Aquifer Protection Area. Per the
City of Renton Amendments to the King County Surface Water Design Manual, the only
requirements are to provide liners to open water drainage facilities and conveyance
systems. This project proposes to provide a closed detention facility (underground vault)
and closed conveyance system; therefore, this Special Requirement is not applicable.
- 1 - 16055.017.docx
DETERMINATION OF NON-SIGNIFICANCE-MITIGATED (DNSM]
MITIGATION MEASURES AND ADVISORY NOTES
Project Nos. LUA13-001572, ECF, PP, CAR
Henley USA LLC
The Reserve at Tiffany Park
MITIGATION MEASURES:
CONDITION RESPONSE
1. All earthwork performed, implemented by the applicant, shall be
consistent with the recommendations of the geotechnical report,
prepared by Associated Earth Sciences, Inc., dated September 28,
2012.
This condition has revised per the Hearing Examiners Conditions
dated January 26th, 2015. Per hearing examiner condition #1 it
now reads as follows.
"All earthwork performed, implemented by the applicant, shall be
consistent with the recommendations of the geotechnical report,
prepared by Associated Earth Sciences, Inc., dated September 28,
2012 or consistent with the recommendations of the final City-
approved geotechnical remit."
2. The final drainage report shall include a more detailed downstream
analysis. Pursuant to KCSWDM 1.2.2.1, a Level 2 downstream
analysis for 1/4 mile from the project site is required. The applicant
should note that Level 3 flow control could be required as part of
the Level 2 downstream analysis. A revised final drainage report
and associated plans, based on the 2009 King County Surface
Water Design Manual as amended by the City of Renton, is
required to be submitted to the satisfaction of the Plan Reviewer
prior to construction permit approval. The applicant shall also be
required to comply with, and implement, any recommended
mitigation measures included in the revised Drainage Report.
Condition acknowledged a level 2 downstream analysis has been
included within the revised drainage report.
3. The applicant shall be required to retain 30% of the significant trees
on site with exclusions for those trees that are considered dead,
diseased, or dangerous, trees located within proposed rights-of-
way, and trees located within the critical areas and their associated
buffers.
The proposed site preserves more than 30% of the existing
significant trees within designated open space tracts.
4. The applicant shall be required to provide, to the Current Planning
Project Manager, tree retention inspection/monitoring reports after
initial clearing, final grading, and annually for two years by a
Condition acknowledged.
- 2 - 16055.017.docx
CONDITION RESPONSE
qualified professional forester. The inspection/monitoring reports
shall identify any retained trees that develop problems due to
changing site conditions and prescribe mitigation. The applicant
shall also be required to comply with, and implement, any
recommended mitigation measures included in the inspection
reports.
5. The applicant shall be required to submit a mitigation plan,
prepared by a qualified professional, which will address vermin
abatement during project grading and site improvements. The
vermin abatement mitigation plan shall be submitted to, and
approved by, the Current Planning Project Manager prior to
construction permit approval. The applicant shall also be required
to comply and implement any recommended mitigation according
to an approved plan.
A vermin abatement plan will be provided to the Current Planning
Project Manager prior to construction permit approval.
6. A minimum 15-foot wide partially sight obscuring landscape buffer
along the perimeter of the site shall be provided. The 15-feet
would allow for the offset of tree planting, as opposed to a linear
tree line, which would create a more natural buffer in keeping with
the existing character of the site. Such landscaping or landscape
plus fencing shall be, at minimum, 6-feet high at maturity and at
least 50% sight-obscuring. Existing mature trees are located within
this 15 foot buffer should be maintain and protected during
construction unless determined by an Arborist that such tree is
dead, diseased, or dangerous.
This condition has revised per the Hearing Examiners Conditions
dated January 26th, 2015. Per hearing examiner condition #1 it
now reads as follows.
"The applicant shall revise its landscaping plan to provide for a 10
foot wide on-site street frontage landscape strip as required by
RMC 4-4-070(F)(1) for all lots and a 10 foot wide, site obscuring
perimeter landscaping adjacent to areas where the retaining walls
are four or more feet in height. Landscaping at maturity must
exceed the height of the adjacent retaining wall. The final detailed
landscape plan shall be submitted to and approved by the Current
Planning Project Manager prior to construction permit approval.
Such landscaping shall include a mixture of trees, shrubs, and
groundcover as approved by the Department of Community and
Economic Development."
7. The applicant shall install a STOP sign with a stopline in
thermoplastic on the southbound approach of Monroe Ave SE to
SE 18th St in order to address the sight distance concerns at this
intersection prior to Final Plat approval. The final design is subject
to final construction permit review prior to construction permit
issuance.
Condition acknowledged. The installation of a stop sign and
stopline are shown on the engineering plans and will be installed
prior to final plat approval.
8. The applicant shall submit a revised TIA including an analysis of
the 124th Place SE and SE 158th St intersection sight distance and
Condition acknowledged.
- 3 - 16055.017.docx
CONDITION RESPONSE
recommend appropriate mitigation. The revised TIA shall be
submitted to, and approved by, the Plan Reviewer prior to utility
construction permits. The applicant shall also be required to
comply with, and implement, any recommended mitigation
measures included in the revised TIA.
9. The applicant shall install directional information signage (white
letters on green background) at S Puget Drive and 116th Ave SE
facing west prior to Final Plat approval. The signs shall read
"TIFFANY PARK" with a left arrow and "CASCADE" with a right
arrow. The final design is subject to final construction permit
review prior to construction permit issuance.
This sign appears to have been installed at some point in 2015.
This condition is therefore satisfied.
10. An additional CROSSROAD (W2-1 symbol) warning sign with a
15MPH advisory speed shall be installed by the applicant on the
southwest directional approach to Beacon Way SE, along the north
side of SE 16th St (east of Beacon Way SE). The final design is
subject to final construction permit review prior to construction
permit issuance.
Condition acknowledged. The installation of a crossroad warning
sign and a 15mph advisory speed sign are shown on the
engineering plans and will be installed prior to final plat
approval.
11. The applicant shall provide a marked crosswalk at the intersection
of SE 18th St and Lake Youngs Way SE prior to Final Plat
approval. The final design is subject to final construction permit
review prior to construction permit issuance.
Condition acknowledged. A marked crosswalk at the intersection of
SE 18th St and Lake Yours Way SE is shown on the engineering
plans and will be installed prior to final plat approval.
HEARING EXAMINER'S DECISION
Henley USA LLC
The Reserve at Tiffany Park
Dated January 26, 2015
CONDITION RESPONSE
1. The applicant shall comply with the mitigation measures issued as
part of the Determination of Non-Significance Mitigated, dated
September 22, 2014 except as modified below:
a. MDNS Condition 1 shall be revised as follows:
- 4 - 16055.017.docx
CONDITION RESPONSE
All earthwork performed, implemented by the applicant, shall
be consistent with the recommendations of the geotechnical
report, prepared by Associated Earth Sciences, Inc., dated
September 28, 2012 or consistent with the recommendations of
the final City-approved geotechnical remit
Condition acknowledged.
b. MDNS Condition 6 shall be stricken and replaced with the
following [as modified by the Ruling on Reconsideration]:
The applicant shall revise its landscaping plan to provide for a
10 foot wide on-site street frontage landscape strip as required
by RMC 4-4-070(F)(1) for all lots and a 10 foot wide, site
obscuring perimeter landscaping adjacent to areas where the
retaining walls are four or more feet in height. Landscaping at
maturity must exceed the height of the adjacent retaining wall.
The final detailed landscape plan shall be submitted to and
approved by the Current Planning Project Manager prior to
construction permit approval. Such landscaping shall include a
mixture of trees, shrubs, and groundcover as approved by the
Department of Community and Economic Development.
All walls bordering the perimeter of the site are less than 4 feet in
height when not provided a 10 foot wide landscaping buffer.
Please reference the associated Landscape plans for further
information regarding proposed plantings.
2. The applicant shall be required to demonstrate compliance with the
minimum 50-foot lot width requirement for all lots with less than 50
feet in width at the foremost points (where the side lot lines
intersect with the street right-of-way line) pursuant to RMC 4-11-
120. The average distance between the side lines connecting front
and rear lot lines shall be submitted to the Current Planning Project
Manager prior to construction permit approval.
A revised Preliminary Plat Plan has been included within the
Construction Permit Plan Set. All lots comply with RMC 4-11-
120.
3. Condition No. 3 has been deleted as directed in the Ruling on
Reconsideration.
N/A
4. The applicant shall be required to submit a revised plat and
landscaping plan, which are elements of the City's required
construction plan set, depicting curb bulbouts at street intersections
where on-street parking is located or calling for no curb bulbouts
and installation of "no parking" designations where street parking is
prohibited at street intersections. The revised plat and landscaping
plan shall be submitted to and approved by the Current Planning
Project Manager prior to construction permit approval.
The developer has elected to not provide bulbouts at street
intersections within the development. "No Parking" signs are called
out on the appropriate plan sheets within the Construction Permit
Plan Set.
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CONDITION RESPONSE
5. The applicant shall eliminate individual access directly from internal
public streets for those lots abutting private streets and/or shared
driveway access easements, specifically Lots 12-14, Lots 15-17,
Lots 38-40 and Lots 78-81 in shared driveways. Said lots shall be
required to take access from the abutting private street and/or
access easement and shall not exceed access thresholds pursuant
to RMC 4-6-060.J and K. Lot 11 may access the public street
directly. The revised plat plan shall be submitted to, and approved
by, the Current Planning Project Manager prior to construction
permit approval. Furthermore, the access restriction for such lots is
required to be noted on the face of the Final Plat prior to recording.
The lot numbering referenced in the above condition reflects the
original 97-lot version submitted as Exhibit 2 to the Hearing
Examiner. As part of the approval process, the plat was approved
for 96 lots. Due to this revision as well as the proposed revisions
listed above, the lot numbering has changed. Lots 12 to 14 have
been renumbered to Lots 11 to 13 and will take shared access from
Tract N. Lots 15 to 17 have been renumbered to Lots 14 to 16 and
will take shared access from Tract O. Lots 38 to 40 have been
renumbered to Lots 37 to 39 and will take shared access from Tract
P. Lots 78 to 81 have been renumbered to Lots 75 to 78 and will
take shared access from Tract Q.
6. The applicant shall revise the proposed mitigation plan to depict all
retaining walls on site, including lock & load walls on the north and
east sides of Wetlands B and C. The applicant shall also identify if
proposed walls are anticipated to impact critical area buffers and
provide appropriate mitigation for such impacts. A Final Mitigation
Plan, pursuant to RMC 4-8-120.W, shall be submitted to, and
approved by the Current Planning Project Manager prior to
construction permit approval.
Condition acknowledged. The Mitigation Plans have been revised
to address this requirement.
7. The temporary buffer impacts consisting of minor intrusions or
disturbance from construction activities shall be restored with
appropriate grading, soil amendments, and the planting of native
species to the satisfaction of the Current Planning Project Manager.
The revised mitigation plan shall be submitted to and approved by,
the Current Planning Project Manager prior to construction permit
approval.
Condition acknowledged. The Mitigation Plans have been revised
to address this requirement.
8. The existing wetland mitigation plan already assures that 1,331
square feet of additional wetland buffer area is being provided to
mitigate for both existing buffer impacts to Wetland E that are not
associated with the Plat, as well as the loss of 14 square feet of the
Wetland E buffer which loss is associated with the extension of SE
18th Street. To provide an additional offset for the impacts
resulting from the requested exemption associated with the fill of 14
square feet of buffer to extend SE 18th Street. The applicant has
agreed to provide and shall provide enhancement to the Wetland E
buffer immediately abutting SE 18th Street, as well as enhanced
plantings adjoining that buffer area within Tract M. A revised
Condition acknowledged. The Mitigation Plans have been revised
to address this requirement.
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CONDITION RESPONSE
mitigation plan shall be submitted to, and approved by, the Current
Planning Project Manager prior to construction permit approval.
9. The applicant shall be required to establish a Native Growth
Protection Easement over those parts of the site encompassing
wetlands and their associated buffers and place fencing and
signage along the outer buffer edge prior to Final Plat approval.
The Native Growth Protection Easement and the associated
fencing shall be designated on the Landscaping Plans.
10. The applicant shall be required to submit a fill source statement if
fill materials are brought to the site in order to the City to ensure
only clean fill is imported prior to construction.
Condition acknowledged.
11. The applicant shall provide a final Tree Retention Plan, complying
with the 30% tree retention SEPA mitigation measure while
demonstrating proposed retaining walls would not impact trees
proposed for retention. The Final Tree Retention Plan shall be
submitted to, and approved by, the Current Planning Project
Manager prior to construction permit approval.
Condition acknowledged. The proposed site preserves more than
30% of the existing significant trees within designated open space
tracts.
12. The applicant shall submit a revised plat plan, which is an element
of the City's required construction plan set, depicting a safe
pedestrian crossing, across the 124th Place SE extension, for the
Seattle Waterline Pedestrian Trail. The revised plat plan, as part of
the construction plan set, shall be submitted to, and approved by
the Current Planning Project Manager, Community Services
Department, and the Transportation Department prior to
construction permit approval.
The following note has been added to the Preliminary Plat -
Horizontal Control Plan: "Safe pedestrian crossing for the Seattle
Waterline Pedestrian Trail across 124th PL SE shall be provided.
Refer to Sheet 26 for specific details."
13. The applicant shall be required to obtain right-of-way or a public
access easement through the Cedar River Pipeline, for the
extension of 124th Place SE, to the satisfaction of the Plan
Reviewer prior to construction permit approval.
Condition acknowledged. And ingress egress easement had been
acquired through the Cedar River Pipeline. Please see applicable
easement documents provided in Section 7.2 of this report.
14. Pedestrian lighting shall be depicted on the lighting plan at the
entrances of Tracts C and E (from the proposed right-of-way). The
lighting plan shall be submitted to, and approved by, the Current
Planning Project Manager and the Plan Reviewer prior to
construction permit approval.
Pedestrian lighting has been provided near the entrances of both
tracts and can be found on both the construction and lighting
plans.
15. The Preliminary Plat plan shall be revised so that no more than 4
lots may gain access via a shared driveway and that at least one
such lot shall meet minimum lot width requirements along a street
As noted above, lot numbering has changed. As such, Lots 14, 17,
and 38 have all been renumbered to Lots 13, 16, and 27. These
lots have all been widened to 35 feet at the right of way line, as
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CONDITION RESPONSE
frontage pursuant to RMC 4-7-170.D (a minimum of 80% or the
required lot width/40 feet or 35 feet along a street curve). The lot(s)
which provides physical frontage along the street shall only be
allowed vehicular access from the shared private driveway. In
order to provide shared access, Lots 14, 17 and 3 shall be widened
to 35 feet and take primary access from the shared driveway. The
revised plat plan shall be submitted to and approved by the Current
Planning Project Manager prior to construction permit approval.
they intersect a curve, and will take access from Tracts N, O, and P
respectively.
16. The plat plan shall be revised so that all lots have no less than a
40-foot lot width where side lot lines intersect with the street right of
way or for radial lots be a minimum of 35 feet in width. Specifically,
proposed Lots 14, 17, and 38 would be required to be widened to
35 feet in order to comply with the condition. The revised plat plan
shall be submitted to and approved by the Current Planning Project
Manager prior to construction permit approval.
As noted above, lot numbering has changed. As such, Lots 14, 17,
and 38 have all been renumbered to Lots 13, 16, and 27. These
lots have all been widened to 35 feet at the right of way line.
17. The applicant shall submit a revised plat plan depicting the
elimination of all pipestem lots (lots which are less than 40 feet in
width where the side lot lines intersect with the street right-of-way
or for radial lots are less than 35 feet) within the subdivision.
Specifically, proposed Lots 12, 14, 15, 17, 38, 40, and 79 would be
required to be eliminated or revised to meet minimum frontage
width requirements. The applicant may also submit an alternative
plat plan which includes a combination of all lots fronting onto a
public street meeting minimum lot widths and those portions of the
lots now proposed for shared driveway/access easements could be
placed in Shared Driveway Tracts with easements placed over
them pursuant to RMC 4-6-060, Street Standards. The revised plat
plan shall be submitted to and approved by the Current Planning
Project Manager prior to construction permit approval.
As noted above, lot numbering has changed. Lots 12 to 14 have
been renumbered to Lots 11 to 13 and will take shared access from
Tract N. Lots 15 to 17 have been renumbered to Lots 14 to 16 and
will take shared access from Tract O. Lots 38 to 40 have been
renumbered to Lots 37 to 39 and will take shared access from Tract
P. Lots 78 to 81 have been renumbered to Lots 75 to 78 and will
take shared access from Tract Q. Shared access easements will
be provided over these tracts.
18. Any proposal to convert the Stormwater vault within Tract A to a
Stormwater detention pond be considered a Major Plat Amendment
subject to the requirements outlined under RMC 4-7-080M.2.
Condition acknowledged.
19. The applicant shall be required to create a homeowners'
association and maintenance agreement(s) for the shared utilities,
landscape areas and maintenance and responsibilities for all
shared improvements of this development. A draft of the
A homeowner's association and maintenance agreement for all
shared utilities, landscape areas and maintenance and
responsibilities for all shared improvements of this development
shall be provided prior to the recording of the final plat.
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CONDITION RESPONSE
document(s) shall be submitted to Current Planning Project
Manager for review and approval by the City Attorney and Property
Services section prior to the recording of the final plat.
20. The applicant shall submit the results of the Phase I Environmental
Site Assessment to the City for review. Appropriate mitigation, if
any, shall be completed prior to issuance of building permits.
Condition acknowledged.
21. All road names shall be approved by the City. Condition acknowledged.
22. Easements may be required for the maintenance and operation of
utilities as specified by the Department.
Easements will be provided for their subject utilities upon their
request.
23. Sanitary sewers shall be provided by the developer at no cost to
the City and designed in accordance with City standards. Side
sewer lines shall be installed eight feet (8') into each lot if sanitary
sewer mains are available, or provided with the subdivision
development.
Condition acknowledged sewer stubs will extend at a minimum of 8
feet into the lots.
24. Any cable TV conduits shall be undergrounded at the same time as
other basic utilities are installed to serve each lot. Conduit for
service connections shall be laid to each lot line.
Condition acknowledged.
25. Concrete permanent control monuments shall be established at
each and every controlling corner of the subdivision. Interior
monuments shall be located as determined by the Department. All
surveys shall be per the City of Renton surveying standards. All
other lot corners shall be marked per the City surveying standards.
The subdivider shall install all street name signs necessary in the
subdivision.
Condition acknowledged.
26. [This condition added as directed by the Ruling on Reconsideration
to address Roof run-off]. Roof run-off that impacts wetlands shall
not be allowed mix with polluting surfaces. Category 2 wetlands
may not be structurally or hydrologically engineered for runoff
quantity or quality control as required by KCSWDM Reference 5.
City staff shall require design adjustments as authorized by
KCSWDM 1.2 to the extent necessary to prevent adverse impacts
to wetland hydrology caused by roof runoff.
Roof run-off being directed to the wetlands onsite in order to
maintain their hydrology will not be mixed with run-off from pollution
generating surfaces.
SEPA and Hearing
Examiners Conditions
2.3
Tab 3.0
16055.016.doc
3.0 OFF-SITE ANALYSIS
Task 1 STUDY AREA DEFINITION AND MAPS
The proposed Plat of Reserve at Tiffany Park is a single-family residential project consisting of 94 lots
zoned R8. The project is 21.66 acres in size containing four tax parcels (212305-9044, 212305-9051,
212305-9054, and 212305-9061). The site is located at the dead end of S.E. 18th Street near the
intersection of Monroe Avenue S.E. in a portion of Section 21, Township 23 North, Range 5 East, W.M.,
in the City of Renton.
The site is polygonal in shape and ties into two existing road stubs. The first is located in the northwest
corner of the site at the dead-end of S.E. 18th Street. The second road stub is located to the southwest
of the site on the southern side of the Cedar River Pipeline at the dead-end of 124th Place S.E. These
road stubs are to be tied into and will be extended into the site to provide public access and circulation.
This site is undeveloped and is currently zoned R8; with a majority of the site being composed of second-
growth forest. The elevations of the site range from 456 to 398. There are five wetlands located on site;
three of them are Category 2 and two are Category 3.
The site is entirely surrounded by existing single family residences. Along the east property line is the
Mercer Island Pipe Line R/W. Along the south boundary is the Cedar River Pipeline R/W. Access to the
site from 124th Place S.E required the developer to an access easement through the Cedar River
Pipeline R/W this easement is provided in section 7.1 of this report.
On-site soils are mapped as mostly Alderwood, with a small portion along the southern boundary mapped
as Arents. Please refer to the Soils Map in this section. All drainage calculations were modeled as till
soils.
The project will be constructing roadways consisting of curb and gutter, sidewalk, and street trees. The
site will tie into the existing roads at the dead-ends of S.E. 18th Street and 124th Place S.E. All roads for
this project have been designed to be 26 feet wide, with an 8-foot planter strip at the back of curb and a
5-foot sidewalk (both sides). Overall the proposed public right-of-way is to be 53 feet in width.
The topography on site is gentle and rolling. The site generally slopes from east to west from elevation
456 to 398. The project will be mass graded with cuts and fills balanced on-site. The wetland areas will
remain undisturbed along with portions of their buffers. Buffer averaging is proposed. Other portions of
the site will remain undisturbed in an effort to preserve as many existing trees as possible.
The drainage facilities are required to meet the requirements of the 2009 King County Surface Water
Design Manual (KCSWDM) and the 2010 City of Renton Amendments to the KCSWDM. The drainage
design shall meet at a minimum the Flow Control Duration Standard Matching Forested Site Conditions
and Basic Water Quality Treatment. The drainage facility located in Tract A is a detention vault sized for
Flow Control Duration Standard Matching Forested Site Conditions. Water quality will be met by the use
of a StormFilter for this project. In order to provide the necessary depth within the detention facility a new
conveyance system will be constructed within S.E. 18th Street and connect to the existing storm line at
the intersection of S.E. Lake Youngs Way. Please refer to Section 4.0 for detailed drainage calculations.
UPSTREAM DRAINAGE ANALYSIS:
Upstream of the site to the northeast is the existing Mercer Island Pipeline. This pipeline is approximately
60 feet wide. The pipeline is fully cleared with grass overgrowth and is slightly crowned along the center
of the right-of-way for its full length adjacent to the project site. Due to the inability to efficiently bypass
the 30-foot-wide portion that flows onto the project site, it is proposed that this region of runoff be
collected and routed to the on-site drainage facility. As such, this area is being considered as part of the
pre-developed site and is not part of the upstream basin.
16055.016.doc
There is also an upstream basin to the east of the Mercer Island Pipe Line R/W that is tributary to the on-
site Wetland "D". This basin consists of runoff from a portion of 129th Place S.E. and the 19th Court S.E.
culdesac along with the surrounding homes. Runoff from this basin is collected and routed by a series of
catch basins and storm pipes to an existing ditch along the east side of the pipeline R/W. A twelve-inch
culvert crosses the pipeline and discharges runoff into the on-site Wetland "D". Runoff from this upstream
basin and from Wetland "D" will be collected in a separate conveyance system and routed through the
site to Wetlands "B/C" which they are tributary to in the existing condition. Any potential runoff from
Wetlands "B/C" will be collected and routed through the on-site drainage facility. As such, this area is
being considered as part of the pre-developed site and is not part of the upstream basin. For further detail
please refer to the Upstream Basin Map in Section 1.0.
16055.016.doc
TASK 2 RESOURCE REVIEW
• Adopted Basin Plans: The site is located within the Mainstem subarea of the Cedar River
Basin. The Mainstem subarea is included in the Lower Cedar River Basin and Nonpoint Pollution
Action Plan. Refer to Appendix A for the portions of the basin that applies to this project.
• Finalized Drainage Studies: This is not applicable.
• Basin Reconnaissance Summary Report: This site is located in the Mainstem subarea of the
Lower Cedar River Basin, which is covered by the Lower Cedar River Basin and Nonpoint
Pollution Action Plan dated July 1997 (included in Appendix A).
• Critical Drainage Area Maps: This project will not discharge to any critical areas or wetlands as
it is to tie into an existing storm drain conveyance system downstream of the detention and water
quality system. As a result no critical areas are to be affected.
• Floodplain and Floodway FEMA Maps: Please see the attached FEMA Map (Section 1.0)
utilized for this analysis. As indicated on the map the site is located in Zone X and is outside of
the 500-year flood plain.
• Other Off-Site Analysis Reports: A site investigation was conducted in preparation of this
Level 1 Off-Site Drainage Analysis. A Level 2 Off-Site Drainage Analysis as request by SEPA
Condition 2 has been provided in Section 6.1 of this report. The United States Department of
Agriculture Soils Conservation Service Map is also provided. See Figure 4 – Soils Map in Section
1.0.
• Sensitive Areas Folios: Based on a review of the King County Sensitive Areas Map Folios, the
site does not contain any On-Site Wetlands, Erosion Sensitive Areas, Land Slide Areas, or any
Known Drainage Complaints. However, through field survey and analysis it has been determined
that there are five wetlands on site. As a result a formal wetland study is included in Section 6.0.
• Road Drainage Problems: This is not applicable.
• United States Department of Agriculture King County Soils Survey: Based on the Soils Map
(see Figure 4 – Soils Map Section 1.0) for this area, the majority of the site is located in the soils
configuration known as Alderwood gravelly sandy loam, and there is a small portion along the
south end of the project that is classified as Arents, Alderwood material.
• Wetland Inventory Map: Using the COR Maps and NWMaps applications on the City of Renton
website there is no known documentation or inventory of wetlands for the project site. However,
through field survey and analysis it has been determined that there are five wetlands on site. As
a result a formal wetland study is included in Section 6.0.
• Migrating River Studies: This is not applicable.
• City of Renton Aquifer Protection Zones: Per the City of Renton's GIS Map the project site is
located within a Zone 2 Aquifer Protection Area.
16055.016.doc
TASK 3 FIELD INSPECTION
The field reconnaissance for this Level 1 Off-Site Drainage Analysis was conducted on August 16, 2013
and November 5, 2013 for the purpose of analyzing the proposed project site and its upstream and
downstream corridors. The site visit on August 16, 2013 was sunny and dry with no evidence of standing
water or ponding along the ditch line north of the Mercer Island Pipeline. The visit on November 5, 2013
was cloudy with rain, with evidence of mild runoff from the cul-de-sac of S.E. 19th Court to its designated
collection system. It should be noted that there was some evidence of flowing or standing runoff along
the ditch line north of the Mercer Island Pipeline, but at the locations inspected depths did not exceed
more than 1 inch. The off-site drainage system was inspected one-quarter mile downstream following the
existing closed conveyance system to Tiffany Park Elementary School where the runoff is collected by a
60-inch trunk line and ultimately conveyed northwest to Ginger Creek.
3.1 Conveyance System Nuisance Problems (Type 1)
Conveyance system nuisance problems are minor but not chronic flooding or erosion problems
that result from the overflow of a constructed conveyance system that is substandard or has
become too small as a result of upstream development. Such problems warrant additional
attention because of their chronic nature and because they result from the failure of a
conveyance system to provide a minimum acceptable level of protection.
There were no conveyance system nuisance problems observed during the August 16, 2013 site
visit. Furthermore, based on a review of the drainage complaints received from the City of
Renton, there is no evidence of past conveyance system nuisance problems occurring in the
direct downstream drainage course, as there is a record of none having been submitted.
This site will have a Flow Control Duration Standard Matching Forested Site Conditions, which
will restrict the flow of the 2-year release rate to 50 percent of the pre-developed site and will
provide adequate mitigation to prevent any future drainage complaints as a result of this
proposed site development.
3.2 Severe Erosion Problems (Type 2)
Severe erosion problems can be caused by conveyance system overflows or the concentration of
runoff into erosion-sensitive open drainage features. Severe erosion problems warrant additional
attention because they pose a significant threat either to health and safety or to public or private
property.
Based on our site visit there and the lack of drainage complaints, there was no evidence of or
potential for erosion/incision sufficient to pose a sedimentation hazard downstream within the
limits of the study. There are no defined drainage channels or ditches leaving the site. All runoff
is either infiltrated on site or sheet flows off site where it is collected by the storm drain
conveyance systems of the downstream suburban area. Stormwater runoff from the proposed
roads will be collected and conveyed to a detention and water quality facility where it will then be
discharged by tying into the existing stormwater conveyance system within S.E. 18th Street. As a
result no future erosion problems should occur because of this development downstream.
3.3 Severe Flooding Problems (Type 3)
Severe flooding problems can be caused by conveyance system overflows or the elevated water
surfaces of ponds, lakes, wetlands, or closed depressions. Severe flooding problems are defined
as follows:
• Flooding of the finished area of a habitable building for runoff events less than or equal to
the 100-year event. Examples include flooding of finished floors of homes and
16055.016.doc
commercial or industrial buildings. Flooding in electrical/heating systems and
components in the crawlspace or garage of a home. Such problems are referred to as
"severe building flooding problems."
• Flooding over all lanes of a roadway or severely impacting a sole access driveway for
runoff events less than or equal to the 100-year event. Such problems are referred to as
"severe roadway flooding problems."
Based on a review of the FEMA Map (Section 1.0) the proposed site is outside of the 500-
year floodplain, and there is no evidence of severe flooding problems encountered during our
visit.
16055.016.doc
TASK 4 DRAINAGE SYSTEM DESCRIPTION AND PROBLEM DESCRIPTIONS
DOWNSTREAM DRAINAGE ANALYSIS:
The contents provided within this section of the report are consistent with that which is required for a
Level 1 Downstream Drainage Analysis. In the pre-developed condition all downstream drainage currently
flows off site onto the properties immediately adjacent to the west or onto S.E. 18th Street where it is
collected by the existing stormwater conveyance system.
In the developed condition stormwater being discharged from the site will be conveyed to a new catch
basin being installed along an existing 18-inch diameter storm drain pipe at the intersection of Lake
Youngs Way S.E. and S.E. 18th Street, approximately 600 feet northwest of the site. A new conveyance
system will be constructed within S.E.18th Street in order to provide adequate depth within the on-site
detention facility. Upon discharging to the existing storm system at Lake Youngs Way S.E. the existing
18-inch concrete pipe turns south and conveys stormwater to the entrance of Tiffany Park. Our field
investigation found that the existing storm pipe turns north and enters the parking lot. At this point we
were unable to follow the exact route of the existing storm as the remodel of Tiffany Park Elementary
added additional storm utilities within the parking lot.
We requested as-builts of the storm within Tiffany Park from the City of Renton but were unable to obtain
the information. We were able to obtain as-built information that shows a 60-inch CMP storm pipe runs
along the west property line of the school. This 60-inch storm pipe continues along the rear yards of the
properties on the west side of Index Court S.E. A review of the City's GIS map shows that the storm
system within Lake Youngs Way S.E. ties into the 60-inch trunk line at the southwest corner of the school
property. The trunk line runs northerly for approximately 1,100 feet before turning east to Lake Youngs
Way S.E., approximately 150 feet west of the intersection with Index Court S.E. The 60-inch trunk line
continues to flow in a northerly direction within Lake Youngs Way S.E. for approximately 1,000 feet to the
intersection of Royal Hills Drive. The trunk line discharges to the headwaters of Ginger Creek at the
southeast corner of this intersection. At this point we are well beyond the quarter mile downstream point
from the project. Because the project will be providing Flow Control Duration Standard Matching
Forested and there is no evidence of flooding or erosion within the downstream system we do not
anticipate any significant impacts due to the project.
Please note that SEPA Condition 2 requested that an additional Level 2 Downstream Drainage Analysis
was performed, the document can be found in Section 6.1 of this report.
TASK 5 MITIGATION OF EXISTING OR POTENTIAL PROBLEMS
During the analysis of the downstream system there were no existing problems detected or in need of
mitigation. The project will be providing Flow Control Duration Standard Matching Forested Site
Conditions and therefore no further mitigation of potential problems will be needed.
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Tab 4.0
16055.016.doc
4.0 FLOW CONTROL AND WATER QUALITY FACILITY ANALYSIS AND DESIGN
A. Existing Site Hydrology
The site is polygonal in shape and ties into two existing road stubs. The first is located in
the northwest corner of the site at the dead-end of S.E. 18th Street. The second road
stub is located to the southwest of the site on the southern side of the Cedar River
Pipeline at the dead end of 124th Place S.E. This site is undeveloped and is currently
zoned R8; with a majority of the site being composed of second-growth forest. The site is
comprised four tax parcels (212305-9044, 212305-9051, 212305-9054, and 212305-
9061). The elevations of the site range from 456 to 398. There are five wetlands located
on site; three of them are Category 2, with two Category 3.
The site is bordered by two pipelines. Along the entire length of the site to the south is
the Cedar River Pipeline. Similarly the northeastern boundary of the site is bordered by
the Mercer Island Pipeline along its entirety. The western and northern edges of the site
are surrounded by single-family homes on medium-sized lots. On-site soils are mapped
as mostly Alderwood, and a small portion of Arents. In the undeveloped condition runoff
flows off site onto the properties immediately adjacent to the west or onto S.E. 18th
Street where it is collected by the existing stormwater conveyance system. Please refer
to the pre-developed drainage area map within Section 1.0 for basin area breakdown for
land cover areas.
Pre-Developed Basin:
The Pre-Developed Basin can be broken down as follows:
Notes:
1. Ex. R/W upstream = 0.65 Ac
Clean rooftops upstream = 0.40 Ac
Roof area measured conservatively from aerial photographs
2. Ex Pasture upstream = 1.51 Ac
Ex Till Grass upstream = 1.37 Ac
Ex Till Forest = 20.79 Ac
The Pre-Developed Peak Rates are as follows:
2-year = 0.86 cfs
10-year = 1.47 cfs
100-year =2.47 cfs
B. Developed Site Hydrology
The completed project will create 94 lots, the total developed area will be 21.66 acres in
size. New impervious surfaces will include roadways, driveways, and roof areas. The
project will be providing landscaped pervious areas, open space/park areas, and a
drainage facility.
Impervious Pervious Total Area
1.05 Ac(1) 23.67 Ac(2) 24.72 Ac
16055.016.doc
A conveyance system consisting of catch basins and storm pipe will be constructed in the
roadways to collect drainage from impervious surfaces and lots and conveyed to the new
drainage facility.
A detention vault and StormFilter vault will be constructed in Tract A to provide water
quality and flow control for the project. The vault will contain a control structure fitted with
a riser overflow. Runoff will be conveyed to a proposed 18-inch pipe which will discharge
runoff into the existing storm drain conveyance system at the intersection of Lake Youngs
Way S.E. and S.E. 18th Street. For further detail please reference the Developed Basin
Map in Section 1.0.
Please note that in the developed condition that the tributary areas to the on-site
wetlands will be altered during construction. In order to maintain their existing
hydrological function a portion of the lots along the existing wetlands (Wetland A,
Wetland B and Wetland C) will discharge their roof drains into the wetland areas to
maintain wetland hydrology. Please reference the Wetland Hydrology Analysis prepared
by Ed McCarthy, PE, PS dated October 27, 2016 located in section 6.2 of this report.
Runoff from these wetlands will be collected and routed to the on-site drainage facility.
Additionally you may reference the Wetland Tributary Area Map and the Developed
Wetland Tributary Area Map located within this section of the report.
Post Developed Basin:
The Post Developed Basin includes the developed basin area tributary to the new
drainage facility. Individual Lot BMPs are required per the 2009 KCSWDM and 2010 City
of Renton Amendments. Full Infiltration and Full Dispersion are not feasible due to the
soil types and limited flow paths available. For purposes of sizing the onsite drainage
facility we utilized the Reduced Impervious Surface Credit Individual Lot BMP. The R-8
zone allows for 75 percent max impervious surface per lot. For purposes of sizing the
drainage facilities we reduced the allowable impervious coverage to 65 percent. The
following list provides a basin area breakdown:
Notes:
1. Roads and Sidewalks = 4.29 Ac
Lot Area @ 65% impervious = 7.62 Ac
Ex. R/W and roof tops upstream = 1.05 Ac
2. Ex Pasture upstream = 1.51 Ac
Till Grass = 6.68 Ac
Ex Till Forest = 3.33 Ac
The Post Developed Peak Release Rates are as follows:
2-year = 0.47 cfs
10-year = 1.23 cfs
100-year = 5.53 cfs
Impervious Pervious Total Area
12.96 Ac(1) 11.52 Ac(2) 24.48 Ac
16055.016.doc
Bypass Basins:
The two bypass basins include small areas along the western portion of S.E. 18th Street
and the southern portion of 124th Place S.E. near the boundaries of the site. Due to the
existing roadway stubs in relation to the maximum water surface elevation in the vault we
are unable to route the runoff to the on-site detention vault. These two areas meet at the
same point of convergence located one-quarter mile downstream. In the existing
condition the 100-year peak flow rate is less than 0.4 cfs at 0.09cfs. Both bypass basins
are 0.12 in size for a total of 0.24 acres of bypass area. Bypass Basin #1 creates 0.09
acres of new impervious surface and Bypass Basin #2 creates 0.10 acres of new
impervious surface area. Water quality requirements are not applicable because both
areas create less than 5,000 square feet of new impervious surface within each bypass
area. In order to meet the compensatory mitigation by a flow control facility the detention
facility has been sized to accommodate this bypass area.
Both bypass basins are collected by the downstream conveyance systems adjacent to
the developed plat. These systems eventually converge at the intersection of S.E. 18th
Street and Lake Youngs Way S.E. where they combine with runoff from the developed
site and are ultimately conveyed and discharged into Ginger Creek.
Combined Bypass peak rates are as follows:
Pre-Developed
2-year = 0.05 cfs
10-year = 0.06 cfs
100-year = 0.09 cfs
Developed
2-year = 0.05 cfs
10-year = 0.06 cfs
100-year = 0.10 cfs
C. Performance Standards
The KCRTS Runoff Time Series Program was used to size the detention facility. The
detention pond was sized for the Flow Control Duration Standard Matching Forested Site
Conditions based on the requirements of the 2009 KCSWDM and the 2010 City of
Renton Amendments to the KCSWDM. Individual Lot BMPs are required as well. Full
infiltration and Full Dispersion are not feasible due to the soil types and limited flow paths
available.
For purposes of sizing the onsite drainage facility we utilized the Reduced Impervious
Surface Credit Individual Lot BMP. The R-8 zone allows for 75 percent max impervious
surface per lot. For purposes of sizing the drainage facilities the allowable impervious
coverage was reduced to 65 percent.
The detention vault has been designed to provide flow duration control. Please see the
attached duration analysis curve chart to see that flow control performance has been
met.
D. Flow Control System
The King County Runoff Time Series (KCRTS) Program was used to size the detention
facility. Please refer to the KCRTS computations attached in this section. Based on the
detention pond sizing calculations, the pond volume required is 213,296 cubic feet. The
pond volume provided is 229,130 cubic feet. Overflow sizing calculations are also
provided in this section. The Vault will contain a control structure fitted with a riser
overflow.
16055.016.doc
Please refer to the drainage facility plan sheets in this section for details
E. Water Quality System
Basic Water Quality Treatment based on the requirements of the 2009 KCSWDM and
2010 City of Renton Amendments will be fulfilled by a StormFilter located immediately
downstream of the control structure using ZPG cartridges. For further detail on the sizing
of the StormFilter please refer to the sizing calculations provided by Contech within this
section.
Please refer to the drainage facility plan sheets in this section for details
TRACT A DETENTION VAULT
TIME SERIES AND PEAK FLOW RATES
LA
3.33 0.00 0.00000 Till Forest
1.51 0.00 0.00000 Till Pasture
6.68 0.00 0.00000 Till Grass
0.00 0.00 0.00000 Outwash Forest
0.00 0.00 0.00000 Outwash Pasture
0.00 0.00 0.00000 Outwash Grass
0.00 0.00 0.00000 Wetland
12.96 0.00 0.00000 Impervious
16055dev.tsf
T
1.000000
Flow Frequency Analysis
Time Series File:16055dev.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
3.96 6 2/09/01 2:00 7.98 1 100.00 0.990
3.18 8 1/05/02 16:00 4.90 2 25.00 0.960
4.73 3 2/27/03 7:00 4.73 3 10.00 0.900
3.37 7 8/26/04 2:00 4.22 4 5.00 0.800
4.06 5 10/28/04 16:00 4.06 5 3.00 0.667
4.22 4 1/18/06 16:00 3.96 6 2.00 0.500
4.90 2 10/26/06 0:00 3.37 7 1.30 0.231
7.98 1 1/09/08 6:00 3.18 8 1.10 0.091
Computed Peaks 6.95 50.00 0.980
Flow Frequency Analysis
Time Series File:16055-dev.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
3.96 6 2/09/01 2:00 7.96 1 100.00 0.990
3.17 8 1/05/02 16:00 4.88 2 25.00 0.960
4.72 3 2/27/03 7:00 4.72 3 10.00 0.900
3.36 7 8/26/04 2:00 4.21 4 5.00 0.800
4.04 5 10/28/04 16:00 4.04 5 3.00 0.667
4.21 4 1/18/06 16:00 3.96 6 2.00 0.500
4.88 2 10/26/06 0:00 3.36 7 1.30 0.231
7.96 1 1/09/08 6:00 3.17 8 1.10 0.091
Computed Peaks 6.93 50.00 0.980
Developed Peak Flows
100yr Peak
10yr Peak
2yr peak
Flow Frequency Analysis
Time Series File:rdout.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) (ft) Period
1.64 2 2/09/01 20:00 5.43 11.40 1 100.00 0.990
0.386 7 12/28/01 18:00 1.64 10.61 2 25.00 0.960
1.21 4 3/06/03 22:00 1.40 9.25 3 10.00 0.900
0.333 8 8/26/04 6:00 1.21 8.34 4 5.00 0.800
0.466 6 1/05/05 17:00 1.18 8.21 5 3.00 0.667
1.18 5 1/18/06 23:00 0.466 6.60 6 2.00 0.500
1.40 3 11/24/06 8:00 0.386 5.19 7 1.30 0.231
5.43 1 1/09/08 10:00 0.333 3.87 8 1.10 0.091
Computed Peaks 4.17 11.30 50.00 0.980
Vault Peak Flow Release Rates
100yr Peak
10yr Peak
2yr peak
ALLURA AT TIFFANY PARK
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800-338-1122 513-645-7000 513-645-7993 FAX
9025 Centre Pointe Dr., Suite 400, West Chester, OH 45069
SF0822
STORMFILTER
STANDARD DETAILTHIS PRODUCT MAY BE PROTECTED BY ONE OR MORE OF THE FOLLOWINGU.S. PATENTS: 5,322,629; 5,524,576; 5,707,527; 5,985,157; 6,027,639; 6,649,048;RELATED FOREIGN PATENTS, OR OTHER PATENTS PENDING.
STORMFILTER TREATMENT CAPACITY IS A FUNCTION OF THE CARTRIDGE SELECTION AND THE NUMBER OF CARTRIDGES. THE STANDARD VAULTSTYLE IS SHOWN WITH THE MAXIMUM NUMBER OF CARTRIDGES (56). VAULT STYLE OPTIONS INCLUDE INLET BAY (49), INLET BAY/OUTLET BAY (46),
OUTLET BAY (51), NLET BAY/FULL HEIGHT BAFFLE WALL (41), FULL HEIGHT BAFFLE WALL (46). STORMFILTER 8X22 PEAK HYDRAULIC CAPACITY IS 1.8
CFS. IF THE SITE CONDITIONS EXCEED 1.8 CFS AN UPSTREAM BYPASS STRUCTURE IS REQUIRED.
F
OR
MAINTENANCE CALL 1.800.338.1 122
C l ean water starts here
GENERAL NOTES
1.CONTECH TO PROVIDE ALL MATERIALS UNLESS NOTED OTHERWISE.
2.DIMENSIONS MARKED WITH ( ) ARE REFERENCE DIMENSIONS. ACTUAL DIMENSIONS MAY VARY.3.FOR SITE SPECIFIC DRAWINGS WITH DETAILED VAULT DIMENSIONS AND WEIGHTS, PLEASE CONTACT YOUR CONTECH ENGINEERED SOLUTIONSLLC REPRESENTATIVE. www.ContechES.com
4.STORMFILTER WATER QUALITY STRUCTURE SHALL BE IN ACCORDANCE WITH ALL DESIGN DATA AND INFORMATION CONTAINED IN THIS
DRAWING.5.STRUCTURE SHALL MEET AASHTO HS20 LOAD RATING, ASSUMING EARTH COVER OF 0' - 5' AND GROUNDWATER ELEVATION AT, OR BELOW, THEOUTLET PIPE INVERT ELEVATION. ENGINEER OF RECORD TO CONFIRM ACTUAL GROUNDWATER ELEVATION. CASTINGS SHALL MEET AASHTO
M306 AND BE CAST WITH THE CONTECH LOGO.
6.FILTER CARTRIDGES SHALL BE MEDIA-FILLED, PASSIVE, SIPHON ACTUATED, RADIAL FLOW, AND SELF CLEANING. RADIAL MEDIA DEPTH SHALLBE 7-INCHES. FILTER MEDIA CONTACT TIME SHALL BE AT LEAST 38 SECONDS.
7.SPECIFIC FLOW RATE IS EQUAL TO THE FILTER TREATMENT CAPACITY (gpm) DIVIDED BY THE FILTER CONTACT SURFACE AREA (sq ft).
8.STORMFILTER STRUCTURE SHALL BE PRECAST CONFORMING TO ASTM C-857 AND AASHTO LOAD FACTOR DESIGN METHOD.
INSTALLATION NOTES
A.ANY SUB-BASE, BACKFILL DEPTH, AND/OR ANTI-FLOTATION PROVISIONS ARE SITE-SPECIFIC DESIGN CONSIDERATIONS AND SHALL BE
SPECIFIED BY ENGINEER OF RECORD.
B.CONTRACTOR TO PROVIDE EQUIPMENT WITH SUFFICIENT LIFTING AND REACH CAPACITY TO LIFT AND SET THE STORMFILTER VAULT (LIFTINGCLUTCHES PROVIDED).
C.CONTRACTOR TO INSTALL JOINT SEALANT BETWEEN ALL VAULT SECTIONS AND ASSEMBLE VAULT.
D.CONTRACTOR TO PROVIDE, INSTALL, AND GROUT PIPES. MATCH OUTLET PIPE INVERT WITH OUTLET BAY FLOOR.
E.CONTRACTOR TO TAKE APPROPRIATE MEASURES TO PROTECT CARTRIDGES FROM CONSTRUCTION-RELATED EROSION RUNOFF.
STORMFILTER DESIGN NOTES
CARTRIDGE HEIGHT
SPECIFIC FLOW RATE (gpm/sf)
CARTRIDGE FLOW RATE (gpm)
RECOMMENDED HYDRAULIC DROP (H)
27"18"LOW DROP
3.05'2.3'1.8'
CARTRIDGE SELECTION
18.79 12.53 8.35
2 gpm/sf
22.5 11.25 15 10 57.5
1.67* gpm/sf 1 gpm/sf 2 gpm/sf 1.67* gpm/sf 1 gpm/sf 2 gpm/sf 1.67* gpm/sf 1 gpm/sf
* 1.67 gpm/sf SPECIFIC FLOW RATE IS APPROVED WITH PHOSPHOSORB® (PSORB) MEDIA ONLY
HY
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SECTION A-A
OUTLET PIPE
OVERFLOW
ASSEMBLY
GRADERING/RISERS
INLET
DISSIPATOR
INLET PIPE
CONTRACTOR TO
GROUT TO FINISHED
GRADE
STORMFILTERCARTRIDGE
FLOW KIT
STEP
OUTLETINLET
PLAN VIEW
VAULT STYLE: OUTLET SUMP (NIB)
INLETDISSIPATOR
(9'-3")
OUTLET SUMP
2'-
0
"
A A
(2'-0")
STORMFILTER CARTRIDGE
22'-0"
8'-
0
"
ALTERNATE PIPELOCATION (TYP)
6" CONCRETE
WALL WIDTH
MAY VARYREGIONALLY
**
STRUCTURE ID
WATER QUALITY FLOW RATE (cfs)
PEAK FLOW RATE (cfs)
RETURN PERIOD OF PEAK FLOW (yrs)
NUMBER OF CARTRIDGES REQUIRED
MEDIA TYPE (PERLITE, ZPG, PSORB)
PIPE DATA:I.E.MATERIAL DIAMETER
INLET PIPE #1
INLET PIPE #2
OUTLET PIPE
SITE SPECIFIC
DATA REQUIREMENTS
WIDTH HEIGHTANTI-FLOTATION BALLAST
NOTES/SPECIAL REQUIREMENTS:
DOWNSTREAM RIM ELEVATION
CARTRIDGE FLOW RATE (gpm/f)
* PER ENGINEER OF RECORD
CARTRIDGE HEIGHT (27", 18", LOW DROP(LD))
UPSTREAM RIM ELEVATION
**
402.5
18"CPEP384.60
18"CPEP386.90
ZPG
1.00
53
100
5.53
0.47
SF#1
18"
402.5
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Tab 5.0
16055.016.doc
5.0 CONVEYANCE SYSTEM ANALYSIS AND DESIGN
The on-site conveyance system was designed in accordance with the 2009 KCSWDM and the
2010 City of Renton Amendments to the KCSWDM. The proposed conveyance system for this
project is curb, gutter, catch basins, and storm drainage pipe. The majority of the storm drainage
pipe used will consist of smooth-walled line corrugated polyethylene pipe with a Manning's
roughness coefficient design value of 0.014.
100-year conveyance calculations for the pipes have been completed using the Rational Method
as shown on the enclosed Excel spreadsheet. The following are the parameters used in design
of the pipes:
1. A Runoff Coefficient – 'C' value was calculated from the 2009 KCSWDM for each tributary
area pursuant to table 3.2.1.A.
2. A 100-year/24-hour precipitation of 3.9 inches in accordance with Figure 3.2.1D.
3. A starting time of concentration of 6.3.
4. An "n" factor of 0.014 (0.012 for Backwater Analysis)
The tributary areas have been calculated to each of the catch basins connecting to the proposed
piping system, as shown on the enclosed map.
A 100-year backwater analysis to determine the hydraulic grade line and to see if any catch basin
rims overtop has also been performed using KCBW in accordance with the 2009 KCSWDM and
the 2010 City of Renton Amendments to the KCSWDM. Please see the attached calculations in
this section.
Tab 6.0
16055.016.doc
6.0 SPECIAL REPORTS AND STUDIES
The following special reports have been prepared and have been submitted under separate
cover.
6.1 Reserve at Tiffany Park - Hydraulic Assessment for Offsite Storm System prepared by Ed
McCarthy, PE, PS dated February 24, 2017
6.2 Allura at Tiffany Park - Wetland Hydrology Analysis prepared by Ed McCarthy, PE, PS
dated October 27, 2016
6.3 Revised Tree Protection Plan - Reserve at Tiffany Park prepared by Washington Forestry
Consultants dated October 4, 2016
6.4 Geotechnical Engineering Study Allura at Tiffany Park prepared by Earth Solutions NW,
LLC dated November 11, 2016
Reserve at Tiffany Park -
Hydraulic Assessment for
Offsite Storm System,
prepared by Ed McCarthy,
PE, PS dated February
24, 2017
6.1
Technical Memorandum
Re: The Reserve at Tiffany Park – Hydraulic Assessment for Offsite Storm System
Project: LUA13-001572 Project Location: Renton, WA
Prepared by: Ed McCarthy, PE, PS
9957 171st Ave SE
Renton, WA 98059
Prepared for: Barghausen Consulting Engineers
18215 72nd Avenue South
Kent, WA 98032
Date: Revised 2-24-17
1
Background Information
This report documents the results of a Level 2 (King County Department of Natural Resources,
2009) hydraulic assessment that I conducted for the existing storm system within the Tiffany
Park area of Renton, Washington (Figure 1). The storm system evaluated extends from the
discharge connection location for the proposed Reserve at Tiffany Park plat to the pipe
network’s outfall at the headwater of Ginger Creek.
The Reserve at Tiffany Park plat is a proposed residential project with 98 lots on 20.79 acres.
Stormwater from the developed site will be collected onsite and detained in a stormwater vault
designed to Level 2 Flow Control standards. Stormwater from the vault will be discharged to a
new 18-inch diameter conveyance pipe that will convey flows from the west side of the
development, down SE 18th Street, to the intersection of Lake Young Way SE. The new pipe
system will connect to an existing storm pipe that flows in a southwest direction along Lake
Young Way SE. The existing pipe system is also 18-inch diameter until it merges with a 60-
inch diameter trunkline about 600 feet downstream from the connection point. The trunkline
collects runoff from contributing tributary pipe systems and ultimately discharges to Ginger
Creek. Stormwater from the Reserve at Tiffany Park currently discharges to the Ginger Creek
conveyance system but flows to the network in a dispersed manner.
Method of Analysis
A backwater analysis was conducted to evaluate the hydraulic grade line in the downstream
pipe system for the predicted 25-year storm. The reach of storm pipe extending from Ginger
Creek to the intersection of Lake Young Way SE and SE 18th Street was evaluated.
Catchment areas that drain to the pipe network were delineated based on the following
resources:
City of Renton storm system map
Aerial topography with 2-foot contour intervals
Cedar River Basin Plan catchment boundaries
2
Each of the catchments represents a tributary pipe network that collects runoff from surrounding
development. The pipe network was modeled with the Reserve at Tiffany Park in its proposed
developed condition.
Pipe materials, pipe lengths, pipe invert elevations, and catch basin rim elevations for the pipe
system, were based on the as-built engineering plans for Tiffany Park No. 2 (Group Four, Inc.
March 16, 1979), storm inventory data from the City’s GIS database, and field measurements.
Flow inputs to the pipe network were predicted using KCRTS with a 15-minute time step.
Residential development is the primary land use in the basin. A total of 52 percent effective
impervious area was assumed in calculating cover types for this land use. The flow contribution
to the pipe network from the Reserve at Tiffany Park was based on the predicted 25-year
outflow rate from the proposed stormwater vault for developed conditions (Barghausen
Consulting Engineers, February 20, 2017). A small amount of bypass from the proposed
development also discharges to the downstream pipe network, which was also included in the
analysis.
A custom spreadsheet based on formulas presented in King County’s Surface Water Design
Manual was used to perform the hydraulic backwater calculations. The downstream boundary
condition assumed normal flow conditions at the pipe outfall in Ginger Creek. The 60-inch
diameter pipe reach is CMP and was modeled with a roughness coefficient of 0.024. The
existing 18-inch diameter pipe reach is concrete pipe and was modeled with a roughness
coefficient of 0.012.
Modeling Results
Soils in the basin are predominately of the Alderwood and Arents series, both of which are
considered till soils (Figure 2). A total area of 220.52 acres contributes to the pipe network
(Table A.1, Figure 3). The pipe network basin was broken down into eight catchments, each
representing a tributary input to the downstream pipe trunkline (Figure 3).
A flow network diagram for the conveyance system, showing inflow locations of each
catchment, is provided in Figure A.1. A summary of the contributing areas and their associated
cover types is provided in Table A.1. The 25-year peak flow rates for each of the catchments are
also shown in Table A.1. KCRTS documentation used in calculating the flow rates for each of
the contributing catchments is provided in Appendix B, as are the predicted outflow rates from
the stormwater vault for the Reserve at Tiffany Park. The KCRTS design for the proposed
stormwater vault is also provided in Appendix B.
The King County Surface Water Design Manual (KCSWDM) (King County Department of
Natural Resources, 2009) requires that existing downstream conveyance systems have sufficient
capacity to convey and contain at least the predicted 25-year peak flow rate assuming developed
3
conditions for tributary areas. The KCSWDM also requires that the 100-year peak rate to the
pipe system does not aggravate a severe flooding1 or severe erosion problem.
Backwater calculations demonstrate that basin flows, including the discharge from the Reserve
at Tiffany Park, are conveyed in the pipe network with no overflow predicted for up to the 25-
year storm. Backwater results are provided in Table A.2 for the pipe network with discharge
from the Reserve at Tiffany Park under proposed developed conditions. The contributing 25-
year peak flow rate from the Reserve at Tiffany Park site to the storm system was predicted to
only slightly increase under proposed developed conditions. Under proposed developed
conditions the 25-year peak rate from the stormwater vault and bypass area was predicted to be
1.71 cubic feet per second versus 1.35 cubic feet per second under forested conditions (Table
A.1 and Appendix B).
Stormwater is predicted to surge from the trunkline at various catch basin locations for the 100-
year peak rate for both existing and proposed developed conditions. The upper reach of the
trunkline is located between Tiffany Park Elementary school and adjacent residential lots. The
lower reach of the trunkline is along roadway. While city staff cites instances of past nuisance
flooding along the trunkline, no documentation of severe flooding is on the record. Presumably,
if severe flooding is a potential outcome of large storms, it likely would have occurred over the
past 36 years since the system was installed.
The existing 100-year predicted flow to the system is 165 cubic feet per second. Contributions
from the proposed Reserve at Tiffany Park would increase the 100-year rate by less than 1
percent, to 166 cubic feet per second. This relatively small increase in flow would not
noticeably aggravate the extent of flooding that has the potential to occur.
If you have questions regarding my assessment or conclusions, or need additional information,
please contact me.
1 Severe flooding is when there is flooding across all lanes of a roadway or a sole access driveway or there is
flooding of the finished floor area of a habitable building (King County Department of Natural Resources, 2009).
4
Sincerely,
Edward J. McCarthy, Ph.D., P.E.
5
References
Barghausen Consulting Engineers, February 20, 2017. Tiffany Park Stormwater Vault
Calculations. Kent, Wash.
Barghausen Consulting Engineers, February 24, 2014. Preliminary Technical
Information Report. Reserve at Tiffany Park, SE 18th Street and 124th Place SE,
Renton, Washington. Kent, Wash.
Group Four, Inc. March 16, 1979. As-Built Plans – Tiffany Park No. 2 – Sheets 6, 8,
and 11 of 13. Lynnwood, Wash.
King County Department of Natural Resources, 2009. King County Surface Water
Design Manual. Seattle.
King County Department of Public Works, Surface Water Management Division,
November 1993. Cedar River Current and Future Conditions Report. Seattle.
U.S. Department of Agriculture, Soil Conservation Service, 1973. Soil Survey of King County Area,
Washington. Seattle.
9
Appendix A. Catchment Areas and Backwater Analysis
Table A.1. Catchment Cover Types and Flow Rates – Proposed Conditions
Catchment Land Use Forest Landscape Impervious Total
25-year Flow
Rate
(AC) (AC) (AC) (AC) (CFS)
C10 Residential 5.23 5.67 10.90 6.25
C20 Residential 7.04 7.62 14.66 10.10
Park/Utility 5.26 0.58 5.84
C20 Subtotal 12.29 8.21 20.50
C30 Residential 7.97 8.63 16.60 13.91
School 5.34 3.56 8.90
C30 Subtotal 13.31 12.19 25.50
C40 Residential 13.68 14.82 28.50 16.36
C50 Residential 43.71 47.35 91.06 53.70
Park 4.05 0.45 4.50
Open Space 4.34 4.34
C50 Subtotal 4.34 47.76 47.80 99.90
C60 Residential 5.04 5.46 10.50 6.02
C70 Residential 3.33 5.36 12.10 20.79 1.71
C80 Residential 2.88 1.05 3.93
Total 7.67 105.55 107.30 220.52 108.05
Notes:
1. Residential Land Use: 52% impervious area assumed.
2. Cover types for Catchment C70 are based on proposed site plan.
3. Catchment C80 flows to the proposed stormwater vault.
4. Predicted outflow rates from Catchments C70 and C80 used in hydraulic assessment are
those predicted to discharge from the proposed Tiffany Park stormwater vault plus bypass
areas.
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12
Appendix B. KCRTS Inputs
Proposed Vault Design
KCRTS Basins
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : c10.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG15R.rnf :
Till Grass 5.23 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI15R.rnf :
Impervious 5.67 acres
--------------
Total Area : 10.90 acres
Peak Discharge: 9.33 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:c10.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:c10.tsf :
13
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:c10.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:c10.pks :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : c20.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG15R.rnf :
Till Grass 12.29 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI15R.rnf :
Impervious 8.21 acres
--------------
Total Area : 20.50 acres
Peak Discharge: 15.89 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:c20.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:c20.tsf :
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:c20.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:c20.pks :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
14
Project Location : Sea-Tac
Computing Series : c30.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG15R.rnf :
Till Grass 13.31 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI15R.rnf :
Impervious 12.19 acres
--------------
Total Area : 25.50 acres
Peak Discharge: 21.10 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:c30.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:c30.tsf :
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:c30.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:c30.pks :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : c40.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG15R.rnf :
Till Grass 13.68 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI15R.rnf :
Impervious 14.82 acres
--------------
Total Area : 28.50 acres
Peak Discharge: 24.39 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:c40.tsf :
Time Series Computed
KCRTS Command
15
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:c40.tsf :
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:c40.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:c40.pks :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : c50.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTF15R.rnf :
Till Forest 4.34 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG15R.rnf :
Till Grass 47.76 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI15R.rnf :
Impervious 47.80 acres
--------------
Total Area : 99.90 acres
Peak Discharge: 80.84 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:c50.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:c50.tsf :
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:c50.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:c50.pks :
16
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : c60.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG15R.rnf :
Till Grass 5.04 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI15R.rnf :
Impervious 5.46 acres
--------------
Total Area : 10.50 acres
Peak Discharge: 8.99 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:c60.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:c60.tsf :
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:c60.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:c60.pks :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : c70.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating 15-minute Time Series File
17
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTF15R.rnf :
Till Forest 20.79 acres
--------------
Total Area : 20.79 acres
Peak Discharge: 2.28 CFS at 9:30 on Jan 9 in Year 8
Storing Time Series File:c70.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:c70.tsf :
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:c70.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:c70.pks :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : c80.tsf
Regional Scale Factor : 1.00
Data Type : Reduced
Creating 15-minute Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTP15R.rnf :
Till Pasture 1.51 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG15R.rnf :
Till Grass 1.37 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI15R.rnf :
Impervious 1.05 acres
--------------
Total Area : 3.93 acres
Peak Discharge: 2.24 CFS at 6:30 on Jan 9 in Year 8
Storing Time Series File:c80.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
18
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:c80.tsf :
Flow Frequency Analysis
--------------------------------------------------------
Time Series File:c80.tsf
Project Location:Sea-Tac
Frequencies & Peaks saved to File:c80.pks :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
eXit KCRTS Program
------------------
19
KCRTS 15-Minute Peak Flow Rates
Flow Frequency Analysis
Time Series File:c10.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
2.70 6 8/27/01 18:00 9.33 1 100.00 0.990
2.02 8 1/05/02 15:00 6.25 2 25.00 0.960
6.25 2 12/08/02 17:15 3.95 3 10.00 0.900
2.17 7 8/23/04 14:30 3.83 4 5.00 0.800
3.95 3 11/17/04 5:00 3.36 5 3.00 0.667
3.36 5 10/27/05 10:45 2.70 6 2.00 0.500
3.83 4 10/25/06 22:45 2.17 7 1.30 0.231
9.33 1 1/09/08 6:30 2.02 8 1.10 0.091
Computed Peaks 8.30 50.00 0.980
Flow Frequency Analysis
Time Series File:c20.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
3.94 6 10/08/00 4:15 15.89 1 100.00 0.990
3.15 8 1/05/02 15:00 10.10 2 25.00 0.960
10.10 2 12/08/02 17:15 7.20 3 10.00 0.900
3.18 7 8/26/04 0:45 5.71 4 5.00 0.800
7.20 3 11/17/04 5:00 5.18 5 3.00 0.667
5.18 5 10/27/05 10:45 3.94 6 2.00 0.500
5.71 4 10/25/06 22:45 3.18 7 1.30 0.231
15.89 1 1/09/08 6:30 3.15 8 1.10 0.091
Computed Peaks 13.96 50.00 0.980
Flow Frequency Analysis
Time Series File:c30.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
5.81 6 8/27/01 18:00 21.11 1 100.00 0.990
4.44 8 1/05/02 15:00 13.91 2 25.00 0.960
13.91 2 12/08/02 17:15 9.14 3 10.00 0.900
4.68 7 8/23/04 14:30 8.31 4 5.00 0.800
9.14 3 11/17/04 5:00 7.37 5 3.00 0.667
7.37 5 10/27/05 10:45 5.81 6 2.00 0.500
8.31 4 10/25/06 22:45 4.68 7 1.30 0.231
21.11 1 1/09/08 6:30 4.44 8 1.10 0.091
Computed Peaks 18.71 50.00 0.980
20
Flow Frequency Analysis
Time Series File:c40.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
7.06 6 8/27/01 18:00 24.39 1 100.00 0.990
5.27 8 1/05/02 15:00 16.36 2 25.00 0.960
16.36 2 12/08/02 17:15 10.34 3 10.00 0.900
5.68 7 8/23/04 14:30 10.01 4 5.00 0.800
10.34 3 11/17/04 5:00 8.79 5 3.00 0.667
8.79 5 10/27/05 10:45 7.06 6 2.00 0.500
10.01 4 10/25/06 22:45 5.68 7 1.30 0.231
24.39 1 1/09/08 6:30 5.27 8 1.10 0.091
Computed Peaks 21.72 50.00 0.980
Flow Frequency Analysis
Time Series File:c50.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
22.77 6 8/27/01 18:00 80.86 1 100.00 0.990
17.26 8 1/05/02 15:00 53.70 2 25.00 0.960
53.70 2 12/08/02 17:15 34.47 3 10.00 0.900
18.35 7 8/23/04 14:30 32.46 4 5.00 0.800
34.47 3 11/17/04 5:00 28.59 5 3.00 0.667
28.59 5 10/27/05 10:45 22.77 6 2.00 0.500
32.46 4 10/25/06 22:45 18.35 7 1.30 0.231
80.86 1 1/09/08 6:30 17.26 8 1.10 0.091
Computed Peaks 71.80 50.00 0.980
Flow Frequency Analysis
Time Series File:c60.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
2.60 6 8/27/01 18:00 8.99 1 100.00 0.990
1.94 8 1/05/02 15:00 6.02 2 25.00 0.960
6.02 2 12/08/02 17:15 3.80 3 10.00 0.900
2.10 7 8/23/04 14:30 3.69 4 5.00 0.800
3.80 3 11/17/04 5:00 3.24 5 3.00 0.667
3.24 5 10/27/05 10:45 2.60 6 2.00 0.500
3.69 4 10/25/06 22:45 2.10 7 1.30 0.231
8.99 1 1/09/08 6:30 1.94 8 1.10 0.091
Computed Peaks 8.00 50.00 0.980
21
Flow Frequency Analysis
Time Series File: c70.tsf – subject site – forested conditions
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
1.35 2 2/09/01 17:15 2.28 1 100.00 0.990
0.404 7 1/06/02 2:30 1.35 2 25.00 0.960
0.963 4 3/06/03 18:45 1.04 3 10.00 0.900
0.049 8 3/08/04 18:45 0.963 4 5.00 0.800
0.644 6 1/05/05 7:30 0.887 5 3.00 0.667
1.04 3 1/18/06 20:00 0.644 6 2.00 0.500
0.887 5 11/24/06 5:15 0.404 7 1.30 0.231
2.28 1 1/09/08 9:30 0.049 8 1.10 0.091
Computed Peaks 1.97 50.00 0.980
Flow Frequency Analysis
Time Series File:c80.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.581 6 2/09/01 12:30 2.24 1 100.00 0.990
0.429 7 1/05/02 15:00 1.43 2 25.00 0.960
1.43 2 12/08/02 17:15 0.889 3 10.00 0.900
0.411 8 8/26/04 0:45 0.728 4 5.00 0.800
0.889 3 11/17/04 5:00 0.681 5 3.00 0.667
0.681 5 10/27/05 10:45 0.581 6 2.00 0.500
0.728 4 10/25/06 22:45 0.429 7 1.30 0.231
2.24 1 1/09/08 6:30 0.411 8 1.10 0.091
Computed Peaks 1.97 50.00 0.980
KCRTS Stormwater Design and Outflow Rates for the Reserve at Tiffany Park Vault
22
Allura at Tiffany Park -
Wetland Hydrology
Analysis prepared by
Ed McCarthy, PE, PS
dated October 27, 2016
6.2
ED MCCARTHY, P.E., PS
Hydrology ▪ Hydraulics ▪ Engineering
9957 171 AVENUE SE
RENTON, WA 98059
(425) 271-5734
October 27, 2016
Mr. Barry Talkington
Barghausen Consulting Engineers, Inc.
18215 72nd Ave South
Kent, WA 98032
Re: Allura at Tiffany Park– Wetland Hydrology Analysis
Renton, Washington
Dear Mr. Talkington:
At your request I’ve conducted a hydrologic analysis of wetlands that are located at the
Allura at Tiffany Park site (Figure 1). The wetlands that I evaluated are identified as
Wetland A and Wetlands B/C within the proposed plat. I used the hydrologic model
KCRTS to compare predevelopment hydrology in the wetlands to that predicted to occur
after the proposed Allura at Tiffany Park project has been completed. Other wetlands on
the site include Wetlands D and E, which are not affected by the proposed project, and
therefore were not evaluated.
Allura at Tiffany Park
The Allura at Tiffany Park site is located at the end of SE 18th Street in the Tiffany Park
area of Renton, Washington. Wetland A is located in the northwest portion of the site.
Wetlands B/C are located in the southeast portion of the site. None of the wetlands have a
well-defined outlet, but each is within the basin that drains to Ginger Creek (Barghausen
Consulting Engineers, February 24, 2014).
The proposal for development includes constructing a single-family residential plat with
road, utility and drainage improvements. Runoff collected from the developed area will
be conveyed to a stormwater vault located in the west portion of the site (Barghausen
Consulting Engineers, November 15, 2016) and subsequently discharged to a pipe system
that discharges to Ginger Creek. Each of the wetlands evaluated is a forested depression
type wetland. Wetlands A and C have a Category 2 rating. Wetland B has a Category 3
rating (Schulz, June 3, 2014). Photos of the wetlands are provided in Attachment C.
Method of Analysis
A hydrologic assessment of contributing basins was conducted to characterize flow
regimes to the wetlands. The basin areas draining to the wetlands under existing
conditions were delineated using the project’s topographic map having 2-foot contour
intervals (Figure 2). The basin for Wetland A is mostly onsite with a portion of the basin
extending into the right-of-way along the north property line.
Mr. Barry Talkington
Page 2
October 27, 2016
Wetlands B and C are adjacent to each other and their hydrology can be assessed by
evaluating a single basin. The basin for Wetlands B/C is also mostly onsite, but a
significant portion of the basin extends offsite, to the north. The basin areas draining to
the wetlands under proposed developed conditions were calculated based on the drainage
plan for the project (Figure 3).
The areas of the basins were broken down into categories of land cover type and
hydrologic soil group. Categories of land cover types included forest, pasture, landscape
and impervious. These areas were delineated using a color aerial photograph from King
County Water and Land Resource Department (KCWLRD, 2005). Hydrologic soil
groups included Group C/D, being poorly drained soil with a relatively high amount of
surface runoff. The hydrologic soil groups were based on those pre-designated to mapped
soils series (SCS, 1973).
The hydrology of the wetlands was evaluated for two scenarios including i) existing basin
conditions and ii) proposed developed basin conditions. Hydrology data for the wetlands’
basins were input to the King County Runoff Time Series v6.00 (KCRTS) hydrologic
model. KCRTS is a continuous hydrologic model that develops runoff time series for a
50-year period of rainfall record (October 1948 through September 1998). A rainfall
correction factor of 1.00 was applied to calibrate the rainfall data for the Seatac area rain
gage to the site. The KCRTS program generates statistical reports for several hydrologic
parameters including peak flow rates for estimated return periods, flow durations and
flow volume. These data are useful in evaluating wetland hydrology.
Wetland Hydrology Management Guidelines (King County DDES, January 1, 2012) were
used in assessing effects of the proposed Allura at Tiffany Park development on the
wetlands’ hydrology. The basic analysis procedure outlined in Appendix A of the
Wetland Hydrology Management Guidelines was used in assessing the wetlands’
hydrology.
In particular, wetland inflow durations were assessed for both existing and proposed
developed conditions for both Wetland A and Wetlands B/C. Flow durations were
calculated and compared for the four seasons of the year including spring, summer, fall
and winter. For purposes of this study, spring is defined as extending from February 1
through May 31, summer extends from June 1 through August 31, fall extends from
September 1 through November 30, and winter extends from December 1 through
January 31. A 25 percent flow duration margin, bracketing the predicted predeveloped
durations, was plotted on each of the flow duration charts to help assess the relative
magnitude of duration comparisons.
The following hydrologic parameters were also calculated and compared for existing and
proposed developed basin conditions:
Peak wetland inflow rates for selected return periods.
Mr. Barry Talkington
Page 3
October 27, 2016
Runoff flow volumes to the wetlands. Runoff volumes calculated by KCRTS
include both surface runoff and interflow (shallow groundwater). Under forested
conditions, interflow is typically the dominant component.
Simulation Results
Under existing basin conditions, a total area of 1.99 acres was measured to drain to
Wetland A and 10.35acres to Wetlands B/C (Figure 2, Table A.1). Under proposed
developed conditions, 0.74 acre was measured to drain to Wetland A and 5.40 acres to
Wetlands B/C (Figure 3, Table A.2). The average annual rainfall for the 50-year period of
simulation record was 37.6 inches with a minimum amount of 23.8 inches in 1952 and a
maximum amount of 54.6 inches in 1950 (Figure 4).
A listing for the KCRTS time series generation of contributing areas is provided in
Attachment B.1. Hydrologic effects of the proposed development on wetland hydrology,
in terms of peak wetland inflow rates, average annual inflow volumes and wetland flow
durations are described below.
Measures to Supplement Wetland Hydrology
The hydrology of the wetlands will be sustained by direct rainfall, runoff from the
wetland buffers and discharge from selected roofs that would be collected and dispersed
in the forested buffer of the wetlands. The roof area that would be directed to each
wetland was determined using the hydrology model for each wetland complex, and by
trial and error, attempting to maintain a reasonable balance among seasonal flow
durations, peak inflow rates and annual inflow volumes.
For Wetland A, a total roof area of 0.28 acre was found to be an appropriate area and
would be dispersed to the wetland buffer. For Wetlands B/C, a total roof area of 0.52 acre
would be dispersed to the wetland buffer. Potential overflow from Wetlands B/C would
be collected at the downstream edge of the wetland complex and conveyed to the
proposed stormwater vault.
The upstream tributary area to Wetlands B/C includes runoff from 3.64 acres of offsite
area and also runoff from onsite Wetland D. The flow contributions from these upstream
tributary areas will be maintained under developed conditions. Runoff from Wetland D
would be collected in a pipe and conveyed to the south and dispersed at the edge of
Wetland C’s buffer.
Wetland Inflow Rates
Predicted peak inflow rates to the wetlands under proposed developed conditions
reasonably match those for existing basin conditions (Figures 5 and 6). For Wetlands
B/C, predicted developed inflow rates to the wetlands for storms larger than a 2-year
event are less than those for existing conditions. For both Wetland A and Wetlands B/C,
dispersion of flows to the buffer would further attenuate the rates.
Mr. Barry Talkington
Page 4
October 27, 2016
Wetland Inflow Volumes
The average annual runoff volume to Wetland A was predicted to be 1.21 acre-feet under
existing basin conditions versus 1.00 acre-feet under proposed basin conditions
(Attachment B.3). The average annual runoff to Wetlands B/C was predicted to be 9.69
acre-feet under existing basin conditions versus 7.98 acre-feet under proposed basin
conditions. In each case, a 17 percent decrease in runoff to the wetlands was predicted.
While adding more roof drainage to the wetlands would increase the runoff volume, this
additional flow would cause other hydrology inputs such as flow durations and peak
inflow rates to further deviate from existing conditions.
Wetland Flow Durations
Due to its small basin area, the flow durations for Wetland A were more difficult to
match to existing conditions than they were for Wetlands B/C. Flow durations for the
wetter fall and winter months for proposed developed conditions were generally within a
25 percent margin of durations for existing conditions for Wetland A (Figures 9 and 10).
The flow durations for the spring months for Wetland A were close to the lower 25
percent margin for existing conditions for Wetland A (Figure 7). Summer flow durations
for Wetland A were predicted to be notably higher than those for existing basin
conditions (Figure 8). The low volume of runoff that would occur over this typically dry
period, however, would not result in adverse impacts to the wetland complex. In my
opinion, providing an excess of runoff to the wetland during the dry summer months is
preferred compared to reducing the wetland’s hydrology during these months.
For Wetlands B/C, flow durations for the proposed developed conditions are close to
those for existing basin conditions for spring, fall and winter months (Figures 11, 13 and
14). Summer flow durations for Wetlands B/C were predicted to be slightly higher than
those for existing basin conditions (Figure 12).
Key Results
Based on the foregoing analysis, I believe that the proposed drainage plan will reasonably
maintain the hydrology of Wetland A and Wetlands B/C. Under the proposed
development, a net average decrease in runoff to both wetland complexes is predicted to
occur. In general, hydrologic analyses estimated that flow durations would be within 25
percent of the existing flow durations for the spring, fall and winter months.
Supplementing the wetlands’ hydrology with roof drainage, dispersed to the wetland
buffers, will be an important component of the drainage plan for Wetland A and
Wetlands B/C. In addition, maintaining flow contributions from offsite tributary areas for
Wetlands B/C, will be important in maintaining the hydrology of these wetlands.
Mr. Barry Talkington
Page 5
October 27, 2016
Sincerely,
Edward J. McCarthy, Ph.D., P.E.
AL
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ALLURA AT TIFFANY PARK
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Figure 3. Developed Basins.
Mr. Barry Talkington
Page 9
October 27, 2016
Figure 4. Annual rainfall amounts used in hydrologic model for wetland basin.
Based on Seatac precipitation gage with 1-hour time increments.
14
.
4
32
.
4
54
.
6
40
.
3
23
.
8
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4
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8
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7
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1
33
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7
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4
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2
48
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4
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9
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5
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7
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Calendar Year
Mr. Barry Talkington
Page 10
October 27, 2016
Figure 5. Wetland A peak inflow rates.
0.05
0.10
0.15
0.20
0.25
1 10 100
Pe
a
k
I
n
f
l
o
w
R
a
t
e
(
C
F
S
)
Return Period (Years)
Predeveloped
Developed
Mr. Barry Talkington
Page 11
October 27, 2016
Figure 6. Wetlands B/C peak inflow rates.
0.10
0.30
0.50
0.70
0.90
1.10
1.30
1.50
1 10 100
Pe
a
k
I
n
f
l
o
w
R
a
t
e
(
C
F
S
)
Return Period (Years)
Predeveloped
Developed
Mr. Barry Talkington
Page 12
October 27, 2016
Figure 7. Wetland A flow durations for spring months – February 1 through May
31.
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
0.18
0.2
1.00E-05 1.00E-04 1.00E-03 1.00E-02 1.00E-01 1.00E+00
Fl
o
w
R
a
t
e
(
C
F
S
)
Probability of Exceedence
Predeveloped
Developed
25% Margin Low
25% Margin High
Mr. Barry Talkington
Page 13
October 27, 2016
Figure 8. Wetland A flow durations for summer months – June 1 through August
31.
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
0.18
0.2
1.00E-05 1.00E-04 1.00E-03 1.00E-02 1.00E-01 1.00E+00
Fl
o
w
R
a
t
e
(
C
F
S
)
Probability of Exceedence
Predeveloped
Developed
25% Margin Low
25% Margin High
Mr. Barry Talkington
Page 14
October 27, 2016
Figure 9. Wetland A flow durations for fall months – September 1 through
November 30.
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
0.18
0.2
1.00E-05 1.00E-04 1.00E-03 1.00E-02 1.00E-01 1.00E+00
Fl
o
w
R
a
t
e
(
C
F
S
)
Probability of Exceedence
Forested
Developed
25% Margin Low
25% Margin High
Mr. Barry Talkington
Page 15
October 27, 2016
Figure 10. Wetland A flow durations for winter months – December 1 through
January 31.
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
0.18
0.2
1.00E-05 1.00E-04 1.00E-03 1.00E-02 1.00E-01 1.00E+00
Fl
o
w
R
a
t
e
(
C
F
S
)
Probability of Exceedence
Predeveloped
Developed
25% Margin Low
25% Margin High
Mr. Barry Talkington
Page 16
October 27, 2016
Figure 11. Wetlands B/C flow durations for spring months – February 1 through
May 31.
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
1.00E-05 1.00E-04 1.00E-03 1.00E-02 1.00E-01 1.00E+00
Fl
o
w
R
a
t
e
(
C
F
S
)
Probability of Exceedence
Predeveloped
Developed
25% Margin Low
25% Margin High
Mr. Barry Talkington
Page 17
October 27, 2016
Figure 12. Wetlands B/C flow durations for summer months – June 1 through
August 31.
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
1.00E-05 1.00E-04 1.00E-03 1.00E-02 1.00E-01 1.00E+00
Fl
o
w
R
a
t
e
(
C
F
S
)
Probability of Exceedence
Predeveloped
Developed
25% Margin Low
25% Margin High
Mr. Barry Talkington
Page 18
October 27, 2016
Figure 13. Wetlands B/C flow durations for fall months – September 1 through
November 30.
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
1.00E-05 1.00E-04 1.00E-03 1.00E-02 1.00E-01 1.00E+00
Fl
o
w
R
a
t
e
(
C
F
S
)
Probability of Exceedence
Predeveloped
Developed
25% Margin Low
25% Margin High
Mr. Barry Talkington
Page 19
October 27, 2016
Figure 14. Wetlands B/C flow durations for winter months – December 1 through
January 31.
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
1.00E-05 1.00E-04 1.00E-03 1.00E-02 1.00E-01 1.00E+00
Fl
o
w
R
a
t
e
(
C
F
S
)
Probability of Exceedence
Predeveloped
Developed
25% Margin Low
25% Margin High
References
Barghausen Consulting Engineers, November 15, 2016. Allura at Tiffany Park –
Proposed Drainage and Site Plan. Kent, Wash.
Barghausen Consulting Engineers, February 24, 2014. Preliminary Technical
Information Report - Reserve at Tiffany Park. Kent, Wash.
King County DDES, January 1, 2012. Critical Areas Mitigation Guidelines. Appendix A
– Wetland Hydrology Management Guidelines. Renton, Wash.
King County Department of Natural Resources, 2009. King County Surface Water
Design Manual. Seattle.
King County Department of Natural Resources, January 1999. King County Runoff Time
Series (KCRTS) – Hydrologic Simulation Model for Implementing the Runoff-
Files Methodology – Computer Software Reference Manual. Seattle.
Schulz, Gary, June 3, 2014. Wetland Determination- Reserve at Tiffany Park –
Preliminary Plat – City of Renton, Washington. Seattle.
U.S. Department of Agriculture, Soil Conservation Service, 1973. Soil Survey of King County
Area, Washington. Seattle.
Attachment A. Wetland Basin Areas
Table A.1. Wetland A Basin Areas under Existing and Developed Conditions
Existing Conditions
Basin Forest Pasture Landscape Impervious Total
(AC) (AC) (AC) (AC) (AC)
Onsite 1.89 0.10 - - 1.99
Total 1.89 0.10 - - 1.99
Developed Conditions
Basin Forest Pasture Landscape Impervious Total
(AC) (AC) (AC) (AC) (AC)
Onsite 0.46 - - 0.28 0.74
Total 0.46 - - 0.28 0.74
Table A.2. Wetlands B/C Basin Areas under Existing and Developed Conditions
Existing Conditions
Basin Forest Pasture Landscape Impervious Total
(AC) (AC) (AC) (AC) (AC)
Onsite 6.42 - - - 6.42
Offsite - 1.51 1.37 1.05 3.93
Total 6.42 1.51 1.37 1.05 10.35
Developed Conditions
Basin Forest Pasture Landscape Impervious Total
(AC) (AC) (AC) (AC) (AC)
Onsite 1.24 - - 0.52 1.76
Offsite - 1.22 1.37 1.05 3.64
Total 1.24 1.51 1.37 1.57 5.40
Attachment B.1. KCRTS Time Series
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : wetapre.tsf
Regional Scale Factor : 1.00
Data Type : Historic
Creating Hourly Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTF60H.rnf :
Till Forest 1.89 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTP60H.rnf :
Till Pasture 0.10 acres
--------------
Total Area : 1.99 acres
Peak Discharge: 0.136 CFS at 9:00 on Jan 9 in 1990
Storing Time Series File:wetapre.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:wetapre.tsf :
Flow Frequency Analysis LogPearson III Coefficients
--------------------------------------------------------
Time Series File:wetapre.tsf Mean= -1.310 StdDev= 0.232
Project Location:Sea-Tac Skew= -0.142
Frequencies & Peaks saved to File:wetapre.pks :
Analysis Tools Command
----------------------
Compute Flow DURATION and Exceedence
------------------------------------
Loading Time Series File:wetapre.tsf :
Computing Interval Locations
Computing Flow Durations
Durations & Exceedence Probabilities to File:wetapre.dur :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : wetadev.tsf
Regional Scale Factor : 1.00
Data Type : Historic
Creating Hourly Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTF60H.rnf :
Till Forest 0.46 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI60H.rnf :
Impervious 0.28 acres
--------------
Total Area : 0.74 acres
Peak Discharge: 0.142 CFS at 6:00 on Jan 9 in 1990
Storing Time Series File:wetadev.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:wetadev.tsf :
Flow Frequency Analysis LogPearson III Coefficients
--------------------------------------------------------
Time Series File:wetadev.tsf Mean= -1.105 StdDev= 0.105
Project Location:Sea-Tac Skew= 0.451
Frequencies & Peaks saved to File:wetadev.pks :
Analysis Tools Command
----------------------
Compute Flow DURATION and Exceedence
------------------------------------
Loading Time Series File:wetadev.tsf :
Computing Interval Locations
Computing Flow Durations
Durations & Exceedence Probabilities to File:wetadev.dur :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : wetbcpre.tsf
Regional Scale Factor : 1.00
Data Type : Historic
Creating Hourly Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTF60H.rnf :
Till Forest 6.42 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTP60H.rnf :
Till Pasture 1.51 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG60H.rnf :
Till Grass 1.37 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI60H.rnf :
Impervious 1.05 acres
--------------
Total Area : 10.35 acres
Peak Discharge: 1.23 CFS at 6:00 on Jan 9 in 1990
Storing Time Series File:wetbcpre.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:wetbcpre.tsf :
Flow Frequency Analysis LogPearson III Coefficients
--------------------------------------------------------
Time Series File:wetbcpre.tsf Mean= -0.290 StdDev= 0.165
Project Location:Sea-Tac Skew= 0.344
Frequencies & Peaks saved to File:wetbcpre.pks :
Analysis Tools Command
----------------------
Compute Flow DURATION and Exceedence
------------------------------------
Loading Time Series File:wetbcpre.tsf :
Computing Interval Locations
Computing Flow Durations
Durations & Exceedence Probabilities to File:wetbcpre.dur :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
CREATE a new Time Series
------------------------
Production of Runoff Time Series
Project Location : Sea-Tac
Computing Series : wetbcdev.tsf
Regional Scale Factor : 1.00
Data Type : Historic
Creating Hourly Time Series File
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTF60H.rnf :
Till Forest 1.24 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTP60H.rnf :
Till Pasture 1.51 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STTG60H.rnf :
Till Grass 1.37 acres
Loading Time Series File:C:\KC_SWDM\KC_DATA\STEI60H.rnf :
Impervious 1.57 acres
--------------
Total Area : 5.69 acres
Peak Discharge: 1.13 CFS at 6:00 on Jan 9 in 1990
Storing Time Series File:wetbcdev.tsf :
Time Series Computed
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute PEAKS and Flow Frequencies
----------------------------------
Loading Stage/Discharge curve:wetbcdev.tsf :
Flow Frequency Analysis LogPearson III Coefficients
--------------------------------------------------------
Time Series File:wetbcdev.tsf Mean= -0.259 StdDev= 0.128
Project Location:Sea-Tac Skew= 0.458
Frequencies & Peaks saved to File:wetbcdev.pks :
Analysis Tools Command
----------------------
Compute Flow DURATION and Exceedence
------------------------------------
Loading Time Series File:wetbcdev.tsf :
Computing Interval Locations
Computing Flow Durations
Durations & Exceedence Probabilities to File:wetbcdev.dur :
Analysis Tools Command
----------------------
RETURN to Previous Menu
-----------------------
KCRTS Command
-------------
eXit KCRTS Program
------------------
Attachment B.2. KCRTS Peak Flow Rates
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:wetapre.tsf Mean= -1.310 StdDev= 0.232
Project Location:Sea-Tac Skew= -0.142
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.060 17 2/16/49 22:00 0.136 1 89.50 0.989
0.119 4 3/03/50 16:00 0.127 2 32.13 0.969
0.127 2 2/09/51 18:00 0.121 3 19.58 0.949
0.040 32 1/30/52 9:00 0.119 4 14.08 0.929
0.031 42 1/18/53 19:00 0.118 5 10.99 0.909
0.045 28 1/06/54 5:00 0.098 6 9.01 0.889
0.079 10 2/07/55 21:00 0.096 7 7.64 0.869
0.068 13 12/20/55 17:00 0.086 8 6.63 0.849
0.053 21 12/09/56 15:00 0.080 9 5.86 0.829
0.056 20 1/16/58 20:00 0.079 10 5.24 0.809
0.046 24 1/24/59 2:00 0.079 11 4.75 0.789
0.086 8 11/20/59 21:00 0.070 12 4.34 0.769
0.046 22 2/24/61 15:00 0.068 13 3.99 0.749
0.028 44 1/03/62 2:00 0.066 14 3.70 0.729
0.037 36 11/25/62 14:00 0.064 15 3.44 0.709
0.046 25 1/01/64 18:00 0.061 16 3.22 0.690
0.033 39 11/30/64 12:00 0.060 17 3.03 0.670
0.035 38 1/06/66 3:00 0.059 18 2.85 0.650
0.079 11 1/19/67 14:00 0.057 19 2.70 0.630
0.046 23 2/03/68 23:00 0.056 20 2.56 0.610
0.046 26 12/03/68 17:00 0.053 21 2.44 0.590
0.039 34 1/13/70 23:00 0.046 22 2.32 0.570
0.033 40 12/06/70 8:00 0.046 23 2.22 0.550
0.096 7 2/28/72 3:00 0.046 24 2.13 0.530
0.042 30 1/13/73 5:00 0.046 25 2.04 0.510
0.045 27 1/15/74 2:00 0.046 26 1.96 0.490
0.070 12 12/26/74 23:00 0.045 27 1.89 0.470
0.043 29 12/02/75 20:00 0.045 28 1.82 0.450
0.005 50 3/24/77 19:00 0.043 29 1.75 0.430
0.037 37 12/10/77 17:00 0.042 30 1.70 0.410
0.022 46 2/12/79 8:00 0.041 31 1.64 0.390
0.059 18 12/15/79 8:00 0.040 32 1.59 0.370
0.033 41 12/26/80 4:00 0.040 33 1.54 0.350
0.064 15 10/06/81 15:00 0.039 34 1.49 0.330
0.057 19 1/05/83 8:00 0.038 35 1.45 0.310
0.038 35 1/24/84 11:00 0.037 36 1.41 0.291
0.019 48 2/11/85 6:00 0.037 37 1.37 0.271
0.098 6 1/18/86 21:00 0.035 38 1.33 0.251
0.080 9 11/24/86 4:00 0.033 39 1.30 0.231
0.031 43 1/14/88 12:00 0.033 40 1.27 0.211
0.019 47 4/05/89 16:00 0.033 41 1.24 0.191
0.136 1 1/09/90 9:00 0.031 42 1.21 0.171
0.118 5 4/05/91 2:00 0.031 43 1.18 0.151
0.040 33 1/27/92 17:00 0.028 44 1.15 0.131
0.041 31 3/22/93 23:00 0.023 45 1.12 0.111
0.012 49 3/03/94 3:00 0.022 46 1.10 0.091
0.061 16 2/19/95 20:00 0.019 47 1.08 0.071
0.121 3 2/09/96 1:00 0.019 48 1.05 0.051
0.066 14 1/02/97 9:00 0.012 49 1.03 0.031
0.023 45 1/07/98 11:00 0.005 50 1.01 0.011
Computed Peaks 0.161 100.00 0.990
Computed Peaks 0.141 50.00 0.980
Computed Peaks 0.122 25.00 0.960
Computed Peaks 0.096 10.00 0.900
Computed Peaks 0.091 8.00 0.875
Computed Peaks 0.077 5.00 0.800
Computed Peaks 0.050 2.00 0.500
Computed Peaks 0.033 1.30 0.231
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:wetadev.tsf Mean= -1.105 StdDev= 0.105
Project Location:Sea-Tac Skew= 0.451
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.084 20 2/16/49 21:00 0.142 1 89.50 0.989
0.131 3 3/03/50 16:00 0.132 2 32.13 0.969
0.088 14 2/09/51 2:00 0.131 3 19.58 0.949
0.063 43 10/15/51 13:00 0.119 4 14.08 0.929
0.061 45 3/24/53 15:00 0.108 5 10.99 0.909
0.075 27 12/19/53 19:00 0.105 6 9.01 0.889
0.079 22 2/07/55 17:00 0.103 7 7.64 0.869
0.078 23 12/20/55 17:00 0.101 8 6.63 0.849
0.090 13 12/09/56 14:00 0.098 9 5.86 0.829
0.077 26 12/25/57 16:00 0.097 10 5.24 0.809
0.060 47 11/18/58 13:00 0.094 11 4.75 0.789
0.078 24 11/20/59 5:00 0.094 12 4.34 0.769
0.068 34 2/14/61 21:00 0.090 13 3.99 0.749
0.062 44 11/22/61 2:00 0.088 14 3.70 0.729
0.067 38 12/15/62 2:00 0.088 15 3.44 0.709
0.077 25 12/31/63 23:00 0.088 16 3.22 0.690
0.067 36 12/21/64 4:00 0.087 17 3.03 0.670
0.069 31 1/05/66 16:00 0.085 18 2.85 0.650
0.094 12 11/13/66 19:00 0.085 19 2.70 0.630
0.105 6 8/24/68 16:00 0.084 20 2.56 0.610
0.065 39 12/03/68 16:00 0.083 21 2.44 0.590
0.069 32 1/13/70 22:00 0.079 22 2.32 0.570
0.065 40 12/06/70 8:00 0.078 23 2.22 0.550
0.103 7 2/27/72 7:00 0.078 24 2.13 0.530
0.064 42 1/13/73 2:00 0.077 25 2.04 0.510
0.068 33 11/28/73 9:00 0.077 26 1.96 0.490
0.097 10 12/26/74 23:00 0.075 27 1.89 0.470
0.065 41 12/02/75 20:00 0.072 28 1.82 0.450
0.071 29 8/26/77 2:00 0.071 29 1.75 0.430
0.098 9 9/17/78 2:00 0.070 30 1.70 0.410
0.088 15 9/08/79 15:00 0.069 31 1.64 0.390
0.085 19 12/14/79 21:00 0.069 32 1.59 0.370
0.085 18 11/21/80 11:00 0.068 33 1.54 0.350
0.119 4 10/06/81 15:00 0.068 34 1.49 0.330
0.087 17 10/28/82 16:00 0.068 35 1.45 0.310
0.072 28 1/03/84 1:00 0.067 36 1.41 0.291
0.060 46 6/06/85 22:00 0.067 37 1.37 0.271
0.094 11 1/18/86 16:00 0.067 38 1.33 0.251
0.108 5 10/26/86 0:00 0.065 39 1.30 0.231
0.052 49 11/11/87 0:00 0.065 40 1.27 0.211
0.067 37 8/21/89 17:00 0.065 41 1.24 0.191
0.142 1 1/09/90 6:00 0.064 42 1.21 0.171
0.132 2 11/24/90 8:00 0.063 43 1.18 0.151
0.070 30 1/27/92 15:00 0.062 44 1.15 0.131
0.047 50 11/01/92 16:00 0.061 45 1.12 0.111
0.053 48 11/30/93 22:00 0.060 46 1.10 0.091
0.068 35 11/30/94 4:00 0.060 47 1.08 0.071
0.101 8 2/08/96 10:00 0.053 48 1.05 0.051
0.088 16 1/02/97 6:00 0.052 49 1.03 0.031
0.083 21 10/04/97 15:00 0.047 50 1.01 0.011
Computed Peaks 0.149 100.00 0.990
Computed Peaks 0.136 50.00 0.980
Computed Peaks 0.124 25.00 0.960
Computed Peaks 0.108 10.00 0.900
Computed Peaks 0.105 8.00 0.875
Computed Peaks 0.095 5.00 0.800
Computed Peaks 0.077 2.00 0.500
Computed Peaks 0.065 1.30 0.231
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:wetbcpre.tsf Mean= -0.290 StdDev= 0.165
Project Location:Sea-Tac Skew= 0.344
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.600 17 2/16/49 21:00 1.23 1 89.50 0.989
1.20 2 3/03/50 16:00 1.20 2 32.13 0.969
0.808 7 2/09/51 15:00 1.08 3 19.58 0.949
0.426 38 1/30/52 8:00 0.920 4 14.08 0.929
0.354 43 3/24/53 15:00 0.896 5 10.99 0.909
0.488 21 12/19/53 19:00 0.849 6 9.01 0.889
0.619 16 2/07/55 17:00 0.808 7 7.64 0.869
0.628 15 12/20/55 17:00 0.796 8 6.63 0.849
0.641 14 12/09/56 14:00 0.757 9 5.86 0.829
0.466 27 1/16/58 16:00 0.706 10 5.24 0.809
0.379 41 1/23/59 23:00 0.703 11 4.75 0.789
0.678 12 11/20/59 21:00 0.678 12 4.34 0.769
0.449 35 2/14/61 21:00 0.666 13 3.99 0.749
0.314 46 11/22/61 2:00 0.641 14 3.70 0.729
0.455 31 12/15/62 2:00 0.628 15 3.44 0.709
0.495 20 12/31/63 23:00 0.619 16 3.22 0.690
0.395 40 12/21/64 4:00 0.600 17 3.03 0.670
0.453 32 1/05/66 16:00 0.575 18 2.85 0.650
0.703 11 1/19/67 14:00 0.524 19 2.70 0.630
0.524 19 8/24/68 16:00 0.495 20 2.56 0.610
0.453 33 12/03/68 16:00 0.488 21 2.44 0.590
0.460 29 1/13/70 23:00 0.482 22 2.32 0.570
0.449 36 12/06/70 8:00 0.475 23 2.22 0.550
0.849 6 2/27/72 7:00 0.474 24 2.13 0.530
0.411 39 1/13/73 2:00 0.471 25 2.04 0.510
0.442 37 11/28/73 9:00 0.471 26 1.96 0.490
0.757 9 12/26/74 23:00 0.466 27 1.89 0.470
0.462 28 12/02/75 20:00 0.462 28 1.82 0.450
0.312 47 8/26/77 2:00 0.460 29 1.75 0.430
0.475 23 9/22/78 19:00 0.458 30 1.70 0.410
0.356 42 9/08/79 15:00 0.455 31 1.64 0.390
0.575 18 12/14/79 21:00 0.453 32 1.59 0.370
0.474 24 11/21/80 11:00 0.453 33 1.54 0.350
0.896 5 10/06/81 15:00 0.453 34 1.49 0.330
0.482 22 1/05/83 8:00 0.449 35 1.45 0.310
0.471 25 1/03/84 1:00 0.449 36 1.41 0.291
0.279 48 6/06/85 22:00 0.442 37 1.37 0.271
0.796 8 1/18/86 16:00 0.426 38 1.33 0.251
0.706 10 11/24/86 3:00 0.411 39 1.30 0.231
0.324 45 1/14/88 12:00 0.395 40 1.27 0.211
0.259 49 11/05/88 14:00 0.379 41 1.24 0.191
1.23 1 1/09/90 6:00 0.356 42 1.21 0.171
1.08 3 11/24/90 8:00 0.354 43 1.18 0.151
0.453 34 1/27/92 17:00 0.342 44 1.15 0.131
0.342 44 3/22/93 22:00 0.324 45 1.12 0.111
0.227 50 11/30/93 22:00 0.314 46 1.10 0.091
0.458 30 2/19/95 17:00 0.312 47 1.08 0.071
0.920 4 2/08/96 10:00 0.279 48 1.05 0.051
0.666 13 1/02/97 6:00 0.259 49 1.03 0.031
0.471 26 10/04/97 15:00 0.227 50 1.01 0.011
Computed Peaks 1.37 100.00 0.990
Computed Peaks 1.20 50.00 0.980
Computed Peaks 1.04 25.00 0.960
Computed Peaks 0.845 10.00 0.900
Computed Peaks 0.806 8.00 0.875
Computed Peaks 0.701 5.00 0.800
Computed Peaks 0.502 2.00 0.500
Computed Peaks 0.382 1.30 0.231
Flow Frequency Analysis LogPearson III Coefficients
Time Series File:wetbcdev.tsf Mean= -0.259 StdDev= 0.128
Project Location:Sea-Tac Skew= 0.458
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.591 19 2/16/49 21:00 1.13 1 89.50 0.989
1.09 2 3/03/50 16:00 1.09 2 32.13 0.969
0.656 13 2/09/51 2:00 1.02 3 19.58 0.949
0.427 43 1/30/52 8:00 0.940 4 14.08 0.929
0.413 44 3/24/53 15:00 0.793 5 10.99 0.909
0.529 26 12/19/53 19:00 0.770 6 9.01 0.889
0.566 22 2/07/55 17:00 0.732 7 7.64 0.869
0.571 21 12/20/55 17:00 0.718 8 6.63 0.849
0.659 12 12/09/56 14:00 0.701 9 5.86 0.829
0.539 24 12/25/57 16:00 0.695 10 5.24 0.809
0.406 45 11/18/58 13:00 0.688 11 4.75 0.789
0.560 23 11/20/59 5:00 0.659 12 4.34 0.769
0.476 34 2/14/61 21:00 0.656 13 3.99 0.749
0.429 41 11/22/61 2:00 0.644 14 3.70 0.729
0.483 32 12/15/62 2:00 0.640 15 3.44 0.709
0.529 25 12/31/63 23:00 0.630 16 3.22 0.690
0.457 37 12/21/64 4:00 0.623 17 3.03 0.670
0.482 33 1/05/66 16:00 0.621 18 2.85 0.650
0.695 10 11/13/66 19:00 0.591 19 2.70 0.630
0.718 8 8/24/68 16:00 0.580 20 2.56 0.610
0.453 39 12/03/68 16:00 0.571 21 2.44 0.590
0.485 31 1/13/70 22:00 0.566 22 2.32 0.570
0.476 35 12/06/70 8:00 0.560 23 2.22 0.550
0.793 5 2/27/72 7:00 0.539 24 2.13 0.530
0.428 42 1/13/73 2:00 0.529 25 2.04 0.510
0.507 29 11/28/73 9:00 0.529 26 1.96 0.490
0.732 7 12/26/74 23:00 0.518 27 1.89 0.470
0.457 38 12/02/75 20:00 0.512 28 1.82 0.450
0.443 40 8/26/77 2:00 0.507 29 1.75 0.430
0.640 15 9/22/78 19:00 0.492 30 1.70 0.410
0.518 27 9/08/79 15:00 0.485 31 1.64 0.390
0.630 16 12/14/79 21:00 0.483 32 1.59 0.370
0.621 18 11/21/80 11:00 0.482 33 1.54 0.350
0.940 4 10/06/81 15:00 0.476 34 1.49 0.330
0.580 20 10/28/82 16:00 0.476 35 1.45 0.310
0.512 28 1/03/84 1:00 0.463 36 1.41 0.291
0.388 46 6/06/85 22:00 0.457 37 1.37 0.271
0.701 9 1/18/86 16:00 0.457 38 1.33 0.251
0.688 11 10/26/86 0:00 0.453 39 1.30 0.231
0.321 49 1/14/88 12:00 0.443 40 1.27 0.211
0.376 47 8/21/89 17:00 0.429 41 1.24 0.191
1.13 1 1/09/90 6:00 0.428 42 1.21 0.171
1.02 3 11/24/90 8:00 0.427 43 1.18 0.151
0.492 30 1/27/92 15:00 0.413 44 1.15 0.131
0.310 50 3/22/93 22:00 0.406 45 1.12 0.111
0.325 48 11/30/93 22:00 0.388 46 1.10 0.091
0.463 36 11/30/94 4:00 0.376 47 1.08 0.071
0.770 6 2/08/96 10:00 0.325 48 1.05 0.051
0.644 14 1/02/97 6:00 0.321 49 1.03 0.031
0.623 17 10/04/97 15:00 0.310 50 1.01 0.011
Computed Peaks 1.20 100.00 0.990
Computed Peaks 1.08 50.00 0.980
Computed Peaks 0.960 25.00 0.960
Computed Peaks 0.811 10.00 0.900
Computed Peaks 0.781 8.00 0.875
Computed Peaks 0.698 5.00 0.800
Computed Peaks 0.538 2.00 0.500
Computed Peaks 0.438 1.30 0.231
Attachment B.3. KCRTS Runoff Volumes
KCRTS Command
-------------
Enter the Analysis TOOLS Module
-------------------------------
Analysis Tools Command
----------------------
Compute VOLUME Discharge
------------------------
Loading Time Series File:wetapre.tsf :
Discharge Volume
----------------
Discharge Volume from Time Series
wetapre.tsf
between 10/01/48 00:00 and 09/30/98 23:59
2643779. Cu-Ft or 60.693 Ac-Ft in 18250.0 days
Discharge Volume File:volwetafpre.prn :
Volume Computed
Analysis Tools Command
----------------------
Compute VOLUME Discharge
------------------------
Loading Time Series File:wetadev.tsf :
Discharge Volume
----------------
Discharge Volume from Time Series
wetadev.tsf
between 10/01/48 00:00 and 09/30/98 23:59
2185299. Cu-Ft or 50.168 Ac-Ft in 18250.0 days
Discharge Volume File:volwetadev.prn :
Volume Computed
Analysis Tools Command
----------------------
Compute VOLUME Discharge
------------------------
Loading Time Series File:wetbcpre.tsf :
Discharge Volume
----------------
Discharge Volume from Time Series
wetbcpre.tsf
between 10/01/48 00:00 and 09/30/98 23:59
21104772. Cu-Ft or 484.499 Ac-Ft in 18250.0 days
Discharge Volume File:volwetspre.prn :
Volume Computed
Analysis Tools Command
----------------------
Compute VOLUME Discharge
------------------------
Loading Time Series File:wetbcdev.tsf :
Discharge Volume
----------------
Discharge Volume from Time Series
wetbcdev.tsf
between 10/01/48 00:00 and 09/30/98 23:59
17380086. Cu-Ft or 398.992 Ac-Ft in 18250.0 days
Discharge Volume File:volwetbcdev.prn :
Volume Computed
Analysis Tools Command
----------------------
eXit KCRTS Program
------------------
End of EXEC file..Begin Interactive Mode
KCRTS Command
-------------
eXit KCRTS Program
------------------
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Revised Tree Protection
Plan - Reserve at
Tiffany Park prepared
by Washington Forestry
Consultants dated
October 4, 2016
6.3
FORESTRY AND VEGETATION MANAGEMENT SPECIALISTS
WFCI
3601943-1 723
FAX 3601943-4 1 28
1919 Yelm Hwy SE, Suite C
Olympia, WA 98501
URBANIRURAL FORESTRY TREE APPRAISAL HAZARD TREE ANALYSIS
RIGHT-OF-WAYS VEGETATION MANAGEMENT ENVIRONMENTAL STUDIES CONTRACT FORESTERS
Member of International Society of Arboriculture and Society of American Foresters
- Revised Tree Protection Plan-
RESERVE AT TIFFANY PARK
SE 18th Street and 124th Pl. SE Renton, WA
Prepared for: Barbara Yarington, Henley USA
Prepared by: Washington Forestry Consultants, Inc. Original Report Date: October 23, 2014
Revised Report Date: October 4, 2016
Introduction The project proponent is planning to construct a new 96 lot subdivision on 21.66 acres at SE 18th Street in Renton, WA. The proponent has retained WFCI to:
• Evaluate and inventory all trees on the site pursuant to the requirements of the City of Renton Tree Protection Ordinance.
• Make recommendations for retention of significant trees, along with required protection
and cultural measures. Observations Methodology
WFCI has evaluated trees 6 inches diameter at breast height (DBH) and larger in the proposed
project area, and assessed their potential to be incorporated into the new project. The tree evaluation phase used methodology developed by Nelda Matheny and Dr. James Clark in their 1998 publication Trees and Development: A Technical Guide to Preservation of Trees
During Land Development.
Site Description The site was previously logged many years ago and was not replanted. The trees on the site are
all naturally regenerated. Five small wetlands are located on the site. There are no structures
located on the site. There are many trails throughout the site.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 2
Forest Inventory by Forest Cover Type There are two forest cover types for the purpose of description. Both types are natural stands. These stands were inventoried using variable area plots installed on a systematic grid across the site. This sample of the tree population will predict the total population of trees with a 95% level
of confidence. The trees within the proposed tree tracts were 100% inventoried and evaluated.
The location of the types is illustrated on the aerial photo in Attachment #1. Type I. -- Type I is the largest type of the site. The trees in this type are native species. The species found in this type include bigleaf maple (Acer macrophyllum), western hemlock (Tsuga
heterophylla), western red cedar (Thuja plicata) and Douglas-fir (Pseudotsuga menziesii). There
are a small number of other species intermixed. A total of 847 trees are projected to exist in the type, ranging in diameter from 6 to 36 inches DBH. Six hundred and thirty-two (632) of the trees were classified as sound, healthy, long-term trees in the dominant and co-dominant crown class. The other 215 trees are not long-term trees
due to structural defects or poor health (dead, diseased, or hazardous). Table 1. Summary of Trees in Type I.
Species
DBH Range (in.) Trees/acre Total # of Trees
# of Trees in Poor Health*
# of Healthy Trees
Species Composition of Stand
Bigleaf Maple 6-36 48.7 715 174 541 84% Douglas-fir 17 1.6 21 0 21 3%
Western Red
Cedar
14 2.3 34 0 34 4%
Western
Hemlock
14-15 5.2 77 41 36 9%
Sum 6-36 57.8 847 215 632 100%
*Dead, diseased, or hazardous.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 3
Type II. -- This is a conifer dominated type on the site. A total of 458 trees ranging in diameter
from 6 to 26 inches at DBH are projected to be in the type. The tree species found in this type include bigleaf maple, Douglas-fir, western hemlock and western red cedar. There are a small number of other species intermixed. Three hundred and thirteen (313) trees were classified as sound, healthy, long-term trees in the dominant and co-
dominant crown class. The other 145 trees are not long-term trees due to poor health (dead, diseased, or hazardous). Table 2. Summary of Trees in Type II.
Species DBH Range (in.) Trees/acre Total # of Trees
# of Trees in Poor Health*
# of Healthy Trees
Species Composition of Stand
Bigleaf Maple 6-24 29.4 229 124 105 50%
Douglas-fir 14-26 13.5 105 21 84 23%
Western Red Cedar 18-24 2.9 23 0 23 5%
Western Hemlock 10-22 12.9 101 0 101 22%
Sum 6-26 58.7 458 145 313 100% *Dead, diseased, or hazardous. Summary of All Trees on the Site There are a total of 1,305 trees on the site that range from 6 to 36 inches DBH. Of these 1,305
trees, there are 360 trees that are dead, dying, or diseased, leaving 945 that are considered to be
healthy trees. Bigleaf maple is the predominant tree species making up 72% of the significant trees in the forest. Table 3. Summary of all Trees on the Site.
Species DBH Range (in.) Total # of Trees
# of Trees in Poor Health*
# of Healthy Trees
Species Composition of Stand
Bigleaf Maple 6-36 944 298 646 72% Douglas-fir 14-26 126 21 105 10%
Western Red
Cedar 18-24 57 0 57 4%
Western
Hemlock 10-22 178 41 137 14%
Sum 6-36 1,305 360 945 100%
Off-Site Impacts Tree removal on this parcel will not impact trees on any surrounding parcels.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 4
Discussion
Potential for Tree Retention
The following table provides a summary of all potential tree tract areas on the site and whether the trees could be saved or removed in the project. There are 12 tracts (Tracts A, B, D, E, F, G, H, I, J, K, L, and M) that have the potential to have trees retained on them. These are
illustrated on the proposed site plan in Attachment #2. A detailed summary of trees by tract,
species, condition, and DBH class is provided in Table 4 below. A list of the individual trees is provided in Attachment #4. Table 4. Summary of tree inventory by Tract (see map in Attachment #2 for tract locations).
Tract
Description of Area
# Trees- Existing*
DBH
Range (in)
# Trees to be Removed for
Health Issues*
# Trees to be Removed for
Grading Issues
# Trees Proposed
to Be Saved*
A South end of Tract A 19 6-24 2 1 16
B Area surrounding
Wetland A
77 6-50 2 6 69
D Area east of lots 14-32 71 6-28 10 7 54
E Between lots 32 and 33 4 6-24 1 3 0
F East of Lots 33-34 1 24 0 1 0
G Area surrounding
Wetland D
4 12-28 1 0 3
H Area south of lot 39 46 6-36 1 0 45
I Area south of lots 37-38 2 15-26 0 0 2
J Area south of lot 44-45 10 7-30 0 1 9
K Area surrounding Wetlands B and C 11 8-29 0 0 11
L Area south of lot 82 17 6-36 0 1 16
M Area surrounding
Wetland E
17 6-22 0 1 16
Summary 279 6-50 17 21 241
*Based on 100% field inventory in tracts on October 17 & 20, 2014 and September 28, 2016 with staked boundary
lines. The inventory was done in the field and not from the surveyed map. A total of 17 trees were found in the tracts should be removed because of poor health and/or
structural defects. Twenty-one trees will need to be removed because of grading (cuts or fills)
for wall or street construction. The remaining 241 trees could be retained in the 12 tracts. This tree inventory was done after staking of the tree tracts.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 5
Tree Density Calculations Title 4-4-130 of the Renton Municipal Code calls for 30% of all healthy significant trees in buildable areas to be retained on the project, or where the required number cannot be retained, replacement trees are to be planted. The following is a summary of the required and planned tree
retention as based on the currently proposed plan:
Total Project Area 21.66 acres Critical Areas and Buffers <1.70 acres> Rights-of-ways <4.15 acres>
Buildable Area 15.81 acres
Total Number of Significant Trees on Site 1,305 trees Trees Excluded from Retention Calculation: Trees that are Dead Diseased or Dangerous <360 trees>
Trees in Proposed Public Streets <238 trees>
Trees in Critical Areas and Buffers <72 trees> Trees on Private Easements <15 trees> Number of Healthy, Significant Trees in Buildable Area: 620 trees Required Tree Retention:
30% of healthy significant trees in buildable area: 186 trees Planned Tree Retention <241 trees> Excess of Retention over the Minimum Requirement 55 trees
Required number of replacement trees: 0 trees There are 620 healthy significant trees in the buildable area of the site. At least 186 of these trees need to be retained to meet the City of Renton Code. The proposed plan retains 241 trees
outside of the critical areas and buffers, an excess of 55 trees.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 6
Recommendations
Tree Protection Measures Trees to be saved must be protected during construction by a six foot high chain link fence
(Attachment #8), located at the edge of the root protection zone (RPZ). The RPZ shall be the
dripline of the stand of trees, or the limits of construction of the tree tract. Placards shall be placed on the fencing every 50 feet indicating the words, "NO TRESPASSING - Protected Trees". The individual tree RPZ is the dripline (6 feet minimum), unless otherwise delineated by WFCI in the field and described in the attached tree list (Attachment #4).
Tree protection fences should be placed around the edge of the root protection zone (RPZ). The fence should be erected after logging but prior to the start of clearing. The fences should be maintained until the start of the landscape installation.
There should be no equipment activity (including rototilling) within the root protection zone. No irrigation lines, trenches, or other utilities should be installed within the RPZ. Cuts or fills should impact no more than 20% of a tree’s root system. If topsoil is added to the root zone of a protected tree, the depth should not exceed 2 inches of a sandy loam or loamy fine sand topsoil and should not cover more than 20% of the root system.
If roots are encountered outside the RPZ during construction, they should be cut cleanly with a saw and covered immediately with moist soil. Noxious vegetation within the root protection zone should be removed by hand. If a proposed save tree must be impacted by grading or fills more than allowed for by WFCI in the tree list, then the tree should be re-evaluated by WFCI to
determine if the tree can be saved with mitigating measures, or if the tree should be removed.
Pruning and Thinning All individual trees to be saved near or within developed areas should have their crowns raised to
provide a minimum of 8 feet of ground clearance over sidewalks and landscape areas, 15 feet over parking lots or streets, and at least 10 feet of building clearance. All pruning should be done according to the ANSI A300 standards for proper pruning, and be completed by an International Society of Arboriculture Certified Arborist®, or be supervised by a
Certified Arborist®. Hazard Tree Inspection WFCI should be contacted to inspect all save trees and tree tracts after initial logging to mark
any additional trees for removal that are deemed to be high risk trees to targets within and outside of the save tree areas. A second inspection of the save trees should occur after the completion of grading to determine if any trees were damaged during grading activity.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 7
Conclusions and Timeline for Activity
1. 241 trees are proposed to be retained in tree tracts within the site (outside of critical areas and
their buffers). This exceeds the 186 tree minimum retention (30%) requirement by 55 trees. 2. The final, approved tree protection plan map should be included in the construction drawings for bid and construction of the project and should be labeled as such. 3. Stake and heavily flag the clearing limits.
4. Contact WFCI to attend pre-job conference and discuss tree protection issues with
contractors. WFCI can verify all trees to be saved and/or removed are adequately marked for retention. 5. Complete logging. Complete necessary hazard tree removals and invasive plant removals from the tree protection areas. No equipment should enter the tree protection areas during
logging.
6. Contact WFCI to inspect the tree tracts after logging, but prior to land clearing to identify any additional hazard trees that should be removed. 7. Install tree protection fences along the 'limits of construction'. The fences should be located at the limits of construction or at the dripline of the save tree or as otherwise specified by
WFCI. Maintain fences throughout construction.
8. Complete clearing of the project. 9. Do not excavate stumps within 10’ of trees to be saved. These should be individually evaluated by WFCI to determine the method of removal. 10. Complete all necessary pruning on save trees or stand edges to provide at least 8’ of ground
clearance near sidewalks and trails, and 15’ above all driveways or access roads. 11. Complete grading and construction of the project. 12. Contact WFCI to final inspect the tree protection areas after grading. 13. All save trees within reach of targets should be inspected annually for 2 years by a qualified professional forester retained by the homeowners association, and bi-annually thereafter.
The purpose of these inspections is to identify trees that develop problems due to changing micro-site conditions and to prescribe cultural care or removal.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 8
Summary
The City of Renton Municipal Code calls for 30% of the significant trees be retained on the buildable area of the site or mitigated for. Based on the current site plan, 246 existing trees in 12
tracts will be retained. This exceeds the minimum 186 tree (30%) requirement by 55 trees.
Therefore, no additional replacement trees are required. This tree protection plan coupled with 72 additional trees in the wetlands and buffers, and the healthy red alders and black cottonwoods that exist but were not counted, will help to preserve
the forested character of the area. As the street trees and landscape trees fill in the buildable area
over time, Tiffany Park will be a very well-treed residential community. Please give me a call if you have further questions.
Respectfully submitted, Washington Forestry Consultants, Inc.
Galen M. Wright, ASCA, ACF ISA Board Certified Master Arborist PN-0129 BU Certified Forester No. 44 ISA Tree Risk Assessor Qualified
attachments: #1: aerial photo with forest cover types #2: site plan with tree tracts #3: private access roads on site plan #4: tree list of tree tract trees #5: individual tree rating key
#6: description of tree evaluation methodology #7: glossary of terms #8: tree protection fence detail #9: assumptions and limiting conditions
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 9
Attachment #1: Aerial Photo of Reserve at Tiffany Park
with Forest Cover Types (King County iMAP)
Site Boundary Forest Cover Type Boundary
Type I
Type II
NORTH
No Scale
Type I
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 10
Tract M Tract B
Tract D
Tract F
Tract G
Tract H
Tract I
Tract J
Tract K
Tract L
Attachment #2: Reserve at Tiffany Park Proposed
Tree Retention Areas and Tree Protection Fence Locations
Tree Protection Fence (Typ)
Tract A
Tract E
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 11
Attachment #3: Reserve at Tiffany Park Private Easement Areas
Private Access Easements (Typ)
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 12
Attachment #4. List of Trees in Tree Tracts.
(attached)
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11
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 13
Attachment #5: Individual Tree Rating Key for Tree Condition
RATING SYMBOL DEFINITION
Very Good VG • Balanced crown that is characteristic of the species
• Normal lateral and terminal branch growth rates for the species and soil type
• Stem sound, normal bark vigor
• No root problems
• No insect or disease problems
• Long-term, attractive tree
Good G • Crown lacking symmetry but nearly balanced
• Normal lateral and terminal branch growth rates for the species and soil type
• Minor twig dieback O.K.
• Stem sound, normal bark vigor
• No root problems
• No or minor insect or disease problems – insignificant
• Long-term tree Fair F • Crown lacking symmetry due to branch loss
• Slow lateral and terminal branch growth rates for the species and soil type
• Minor and major twig dieback – starting to decline
• Stem partly unsound, slow diameter growth and low bark vigor
• Minor root problems
• Minor insect or disease problems
• Short-term tree 10-30 years
RATING SYMBOL DEFINITION
Poor P • Major branch loss – unsymmetrical crown
• Greatly reduced growth
• Several structurally import dead or branch scaffold branches
• Stem has bark loss and significant decay with poor bark vigor
• Root damage
• Insect or disease problems – remedy required
• Short-term tree 1-10 years
Very Poor VP • Lacking adequate live crown for survival and growth
• Severe decline
• Minor and major twig dieback
• Stem unsound, bark sloughing, previous stem or large branch
failures, very poor bark vigor
• Severe root problems or disease
• No or minor insect or disease problems
• Mortality expected within the next few years Dead DEAD • Dead
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 14
Cultural Care Needs:
ABBRV. ACTIVITY DESCRIPTION
CC Crown Cleaning
Pruning of dead, dying, diseased, damaged, or defective branches over 1/2 inch in diameter –includes removal of dead tops
CT Crown Thinning
Pruning of branches described in crown cleaning, plus thinning of up to 20% of the live branches over ½ inch diameter. Branch should be 1/3 to ½ the diameter of the lateral branch. Thinning should be well distributed throughout crown of tree, and should release healthy, long-term branches.
RC Crown
Reduction
Reduction of the crown of a tree by pruning to lateral branches. Generally used to
remove declining branches or to lighten end weight on long branches.
CR Crown
Raising
Pruning of lower branches to remove deadwood or to provide ground or building
clearances.
RMV Remove Remove tree due to decline or hazardous conditions that cannot be mitigated by
pruning. RS Remove Sprouts
Remove basal sprouts from stem of tree.
Rep Replace Tree is small – is in decline or dead. Replace with suitable tree species.
HT Hazard Tree Tree is hazardous and cannot be mitigated by pruning. Recommendation is to
remove tree. None No Work No work necessary at this time.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 15
Attachment #6: Description of Tree Evaluation Methodology
The evaluation of the tree condition on this site included the visual assessment of:
1. Live-crown ratio, 2. Lateral and terminal branch growth rates, 3. Presence of dieback in minor and major scaffold branches and twigs,
4. Foliage color,
5. Stem soundness and other structural defects, 6. Visual root collar examination, 7. Presence of insect or disease problems. 8. Windfirmness if tree removal will expose this tree to failure.
In cases where signs of internal defect or disease were suspected, a core sample was taken to look for stain, decay, and diameter growth rates. Also, root collars were exposed to look for the presence of root disease.
In all cases, the overall appearance of the tree was considered relative to its ability to add value
to either an individual lot or the entire subdivision. Also, the scale of the tree and its proximity to both proposed and existing houses was considered.
Lastly, the potential for incorporation into the project design is evaluated, as well as potential site
plan modifications that may allow otherwise removed tree(s) to be both saved and protected in the development. Trees that are preserved in a development must be carefully selected to make sure that they can survive construction impacts, adapt to a new environment, and perform well in the landscape.
Healthy, vigorous trees are better able to tolerate impacts such as root injury, changes in soils moisture regimes, and soil compaction than are low vigor trees. Structural characteristics are also important in assessing suitability. Trees with significant decay and other structural defects that cannot be treated are likely to fail. Such trees should not be
preserved in areas where damage to people or property could occur. Trees that have developed in a forest stand are adapted to the close, dense conditions found in such stands. When surrounding trees are removed during clearing and grading, the remaining trees are exposed to extremes in wind, temperature, solar radiation, which causes sunscald, and
other influences. Young, vigorous trees with well-developed crowns are best able to adapt to these changing site conditions.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 16
Attachment #7: Glossary of Forestry and Arboricultural Terminology
DBH: Diameter at Breast Height (measured 4.5 ft. above the ground line on the high side of the
tree).
Caliper: In Issaquah - Caliper is referring to diameter measurement at DBH. Live Crown Ratio: Ratio of live foliage on the stem of the tree. Example: A 100’ tall tree with
40 feet of live crown would have a 40% live crown ratio. Conifers with less than 30%
live crown ratio are generally not considered to be long-term trees in forestry. Crown: Portion of a trees stem covered by live foliage.
Crown Position: Position of the crown with respect to other trees in the stand.
Dominant Crown Position: Receives light from above and from the sides. Codominant Crown Position: Receives light from above and some from the sides.
Intermediate Crown Position: Receives little light from above and none from the sides. Trees tend to be slender with poor live crown ratios. Suppressed Crown Position: Receives no light from above and none from the sides. Trees
tend to be slender with poor live crown ratios.
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 17
Attachment #8: Tree Protection Fence Detail
6 ft. Temporary Chain Link Fence
NO TRESPASSING - Protected Trees
The Reserve at Tiffany Park – Revised Tree Protection Plan 10/04/16
Washington Forestry Consultants, Inc Page 18
Attachment #9: Assumptions and Limiting Conditions
1) Any legal description provided to the Washington Forestry Consultants, Inc. is assumed to be correct. Any titles and ownership's to any property are assumed to be good and marketable. No responsibility is assumed for matters legal in character. Any and all property is appraised or evaluated as though free and clear, under responsible ownership and competent management. 2) It is assumed that any property is not in violation of any applicable codes, ordinances, statutes, or other governmental regulations, unless otherwise stated. 3) Care has been taken to obtain all information from reliable sources. All data has been verified insofar as possible; however, Washington Forestry Consultants, Inc. can neither guarantee nor be responsible for the accuracy of information. 4) Washington Forestry Consultants, Inc. shall not be required to give testimony or to attend court by reason of this report unless subsequent contractual arrangements are made, including payment of an additional fee for such services as described in the fee schedule and contract of engagement. 5) Loss or alteration of any part of this report invalidated the entire report. 6) Possession of this report or a copy thereof does not imply right of publication or use for any purpose by any other than the person to whom it is addressed, without the prior expressed written or verbal consent of Washington Forestry Consultants, Inc. 7) Neither all or any part of the contents of this report, nor copy thereof, shall be conveyed by anyone, including the client, to the public through advertising, public relations, news, sales or other media, without the prior expressed written or verbal consent of Washington Forestry Consultants, Inc. -- particularly as to value conclusions, identity of Washington Forestry Consultants, Inc., or any reference to any professional society or to any initialed designation conferred upon Washington Forestry Consultants, Inc. as stated in its qualifications. 8) This report and any values expressed herein represent the opinion of Washington Forestry Consultants, Inc., and the fee is in no way contingent upon the reporting of a specified value, a stipulated result, the occurrence neither of a subsequent event, nor upon any finding in to reported. 9) Sketches, diagrams, graphs, and photographs in this report, being intended as visual aids, are not necessarily to scale and should not be construed as engineering or architectural reports or surveys. 10) Unless expressed otherwise: 1) information contained in this report covers only those items that were examined and reflects the condition of those items at the time of inspection; and 2) the inspection is limited to visual examination of accessible items without dissection, excavation, probing, or coring. There is no warranty or guarantee, expressed or implied, that problems or deficiencies of the tree or other plant or property in question may not arise in the future.
Note: Even healthy trees can fail under normal or storm conditions. The only way to eliminate all risk is to remove all trees within reach of all targets. Annual inspections by an ISA Certified Arborist or Certified Forester will
reduce the potential of tree failures. It is impossible to predict with certainty that a tree will stand or fail, or the timing of the failure. It is considered an ‘Act of God’ when a tree fails, unless it is directly felled or pushed over by man’s actions.
Geotechnical Engineering
Study Allura at Tiffany
Park prepared by Earth
Solutions NW, LLC dated
November 11, 2016
6.4
EarthSolutionsNWLLC
EarthSolutionsNWLLC
Geotechnical Engineering
Geology
Environmental Scientists
Construction Monitoring
1805 -136th Place N.E.,Suite 201 Bellevue,WA 98005
(425)449-4704 Fax (425)449-4711
www.earthsolutionsnw.com
GEOTECHNICAL ENGINEERING STUDY
ALLURAAT TIFFANY PARK
SOUTHEAST 18th STREET &
MONROE AVENUE SOUTHEAST
RENTON,WASHINGTON
ES-3633.03
Drwn.
Checked Date
Date Proj.No.
Plate
Earth Solutions NWLLC
Geotechnical Engineering,Construction Monitoring
EarthSolutionsNWLLC
EarthSolutionsNWLLC and Environmental Sciences
Vicinity Map
Allura at Tiffany Park
Renton,Washington
MRS
KDH
11/11/2016
Nov.2016
3633.03
1
NORTH
NOTE:This plate may contain areas of color.ESNW cannot be
responsible for any subsequent misinterpretation of the information
resulting from black &white reproductions of this plate.
Reference:
King County,Washington
Map 656
By The Thomas Guide
Rand McNally
32nd Edition
SITE
Plate
Proj.No.
Date
Checked By
Drwn.By
E a r t h
S o l u t i o n s
N W L L C
G e o t e c h n i c a l
E n g i n e e r i n g ,C o n s t r u c t i o n
M o n i t o r i n g
a n d
E n v i r o n m e n t a l
S c i e n c e s
E a r t h
S o l u t i o n s
N W L L C
E a r t h
S o l u t i o n s
N W L L C
T e s t
P i t
L o c a t i o n
P l a n
A l l u r a
a t
T i f f a n y
P a r k
R e n t o n ,
W a s h i n g t o n
MRS
KDH
11/11/2016
3633.03
2
N O R T H
0 80 160 320
Scale in Feet1"=160'
NOTE:This plate may contain areas of color.ESNW cannot be
responsible for any subsequent misinterpretation of the information
resulting from black &white reproductions of this plate.
NOTE:The graphics shown on this plate are not intended for design
purposes or precise scale measurements,but only to illustrate the
approximate test locations relative to the approximate locations of
existing and /or proposed site features.The information illustrated
is largely based on data provided by the client at the time of our
study.ESNW cannot be responsible for subsequent design changes
or interpretation of the data by others.
LEGEND
Approximate Location of
ESNW Test Pit,Proj.No.
ES-3633.03,Nov.2016
Approximate Location of
AESI Exploration Pit,
Proj.No.KE120359A,
Sept.2012
Subject Site
Proposed Lot Number
Wetland (Delineated
by Others)
MERCER ISLAND PIPELINE R/W
TP-1
TP-2
TP-3
TP-4
EP-1
EP-2
EP-3
EP-4
EP-5
EP-6
EP-7
EP-8EP-9
EP-10
EP-11
TP-1
EP-12
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16 17
18
19
20
21 22 23 24 25 26 27 28 29
30 31 32 33 34
35 36 37 38
39
40
414243
44
45
46
47
484950515253
54555657
58
59 60 61 62 63 64
65
66
676869707172
73
74
75
76
7778
79
80
81
82
83
84
85
86
87
88
89
90
91
92
93
94
Tract A
Tract B
Tract C
Tract D
Tract E
Tract F
Tract H
Tract I
Tract J
Tract K
Tract L
Tract M
Tract G
Drainage,Landscaping &Utilities
EP-1
39
S .E . 1 5 8 T H S T R E E T
1
2
4
T
H
P
L
A
C
E
S.
E
.
S .E . 1 8 T H S T R E E T
S.E. 18TH STREET
ROAD A
Drwn.
Checked Date
Date Proj.No.
Plate
Earth Solutions NWLLC
Geotechnical Engineering,Construction MonitoringandEnvironmentalSciences
EarthSolutionsNWLLC
EarthSolutionsNWLLC
RETAINING WALL DRAINAGE DETAIL
NOTES:
Free-Draining Backfill should consist
of soil having less than 5 percent fines.
Percent passing #4 should be 25 to
75 percent.
Sheet Drain may be feasible in lieu
of Free-Draining Backfill,per ESNW
recommendations.
Drain Pipe should consist of perforated,
rigid PVC Pipe surrounded with 1-inch
Drain Rock.
LEGEND:
Free-Draining Structural Backfill
1-inch Drain Rock
18"Min.
Structural
Fill
Perforated Drain Pipe
(Surround In Drain Rock)
SCHEMATIC ONLY -NOT TO SCALE
NOT A CONSTRUCTION DRAWING
Sheet Drain
(See Note)
Floor Slab
(Where Applicable)
Allura at Tiffany Park
Renton,Washington
MRS
KDH
11/11/2016
Nov.2016
3633.03
3
Drwn.
Checked Date
Date Proj.No.
Plate
Earth Solutions NWLLC
Geotechnical Engineering,Construction Monitoring
and Environmental Sciences
EarthSolutionsNWLLC
EarthSolutionsNWLLC
FOOTING DRAIN DETAIL
Slope
Perforated Rigid Drain Pipe
(Surround with 1"Rock)
18"(Min.)
NOTES:
Do NOT tie roof downspouts
to Footing Drain.
Surface Seal to consist of
12"of less permeable,suitable
soil.Slope away from building.
LEGEND:
Surface Seal;native soil or
other low permeability material.
1"Drain Rock
SCHEMATIC ONLY -NOT TO SCALE
NOT A CONSTRUCTION DRAWING
Allura at Tiffany Park
Renton,Washington
MRS
KDH
11/11/2016
Nov.2016
3633.03
4
Tab 7.0
16055.016.doc
7.0 OTHER PERMITS
7.1 Postmaster / Mailbox Locations Approval
7.2 Roadway Easement and Agreement for 124th Pl S.E.
7.3 NPDES Permit dated March 22, 2017
Postmaster / Mailbox
Locations Approval dated
February 23, 2017
7.1
Roadway Easement
and Agreement for
124th Place SE
7.2
NPDES Permit dated
March 23, 2017
7.3
Tab 8.0
16055.016.doc
8.0 CONSTRUCTION STORMWATER POLLUTION PREVENTION PLAN (CSWPP) ANALYSIS
AND DESIGN
A. Erosion and Sediment Control (ESC) Plan Analysis and Design
The erosion and sediment control plans were prepared in accordance with the 2009 King
County Surface Water Design Manual, 2010 City of Renton Amendments to the
KCSWDM, and standard industry practices throughout the construction process to limit
the amount of sediment traveling into the downstream systems. The permanent drainage
facility in Tract A will be constructed to provide sediment retention on site. Prior To its
construction a large sediment pond may be used.
Additional BMPs that are proposed include a rock construction entrance located at the
roadway stub for SE 18th Street in the North West Corner of the Site, silt fence where
needed, straw mulch for the areas that reach final grade in the lot areas, V-ditches with
rock check dams, and hydroseeding. Clearing limits have been established as shown on
the engineering plans.
Sizing Calculations for the Sediment Ponds shown on the plans are included within this
section of the report.
B. Stormwater Pollution Prevention and Spill (SWPPS) Plan Design
A SWPPS plan has been submitted as a separate document under the Early Clear and
Grad permit application. A copy of the NPDES Permit has been included within section
7.3 of this report.
Tab 9.0
16055.016.doc
9.0 BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
9.1 Bond Quantities
9.2 Facility Summary Form
Bond Quantities9.1
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41
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55
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15
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0
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l
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P
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4
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3
10
.
0
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$
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l
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P
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6
"
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2
4
13
.
0
0
$
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Cu
l
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t
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P
V
C
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8
"
(N
o
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2
5
15
.
0
0
$
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Cu
l
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P
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1
2
"
(N
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2
6
23
.
0
0
$
LF
Cu
l
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,
P
V
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,
1
5
"
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o
t
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2
7
35
.
0
0
$
LF
Cu
l
v
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t
,
P
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1
8
"
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2
8
41
.
0
0
$
LF
Cu
l
v
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t
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P
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2
4
"
(
N
o
t
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2
9
56
.
0
0
$
LF
Cu
l
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P
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,
3
0
"
(N
o
t
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)
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3
0
78
.
0
0
$
LF
Cu
l
v
e
r
t
,
P
V
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,
3
6
"
(N
o
t
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l
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3
1
13
0
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
M
P
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8
"
D-
3
2
19
.
0
0
$
LF
Cu
l
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C
M
P
,
1
2
"
D-
3
3
29
.
0
0
$
LF
SU
B
T
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T
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T
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A
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:
20
,
2
4
0
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0
0
23
8
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3
6
0
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0
0
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0
4
0
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0
0
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(C
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(E
)
SI
T
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f
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4
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H
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p
d
a
t
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d
:
0
6
/
1
4
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2
0
1
6
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r
s
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n
:
0
6
/
1
4
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2
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1
6
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n
t
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d
1
2
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5
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2
0
1
6
CE
D
P
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m
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t
#
:
U
1
6
0
0
6
3
6
8
Ex
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s
t
i
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g
Fu
t
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p
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(
E
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)
DR
A
I
N
A
G
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(
C
o
n
t
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d
)
Cu
l
v
e
r
t
,
C
M
P
,
1
5
"
D-
3
4
35
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
M
P
,
1
8
"
D-
3
5
41
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
M
P
,
2
4
"
D-
3
6
56
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
M
P
,
3
0
"
D-
3
7
78
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
M
P
,
3
6
"
D-
3
8
13
0
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
M
P
,
4
8
"
D-
3
9
19
0
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
M
P
,
6
0
"
D-
4
0
27
0
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
M
P
,
7
2
"
D-
4
1
35
0
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
8
"
D-
4
2
42
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
1
2
"
D-
4
3
48
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
1
5
"
D-
4
4
78
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
1
8
"
D-
4
5
48
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
2
4
"
D-
4
6
78
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
3
0
"
D-
4
7
12
5
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
3
6
"
D-
4
8
15
0
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
4
2
"
D-
4
9
17
5
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
o
n
c
r
e
t
e
,
4
8
"
D-
5
0
20
5
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
P
E
,
6
"
(N
o
t
a
l
l
o
w
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d
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n
R
O
W
)
D-
5
1
14
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
P
E
,
8
"
(N
o
t
a
l
l
o
w
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d
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n
R
O
W
)
D-
5
2
16
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
P
E
,
1
2
"
(N
o
t
a
l
l
o
w
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d
i
n
R
O
W
)
D-
5
3
24
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
P
E
,
1
5
"
(N
o
t
a
l
l
o
w
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d
i
n
R
O
W
)
D-
5
4
35
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
P
E
,
1
8
"
(N
o
t
a
l
l
o
w
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d
i
n
R
O
W
)
D-
5
5
41
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
P
E
,
2
4
"
(
N
o
t
a
l
l
o
w
e
d
i
n
R
O
W
)
D-
5
6
56
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
P
E
,
3
0
"
(N
o
t
a
l
l
o
w
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d
i
n
R
O
W
)
D-
5
7
78
.
0
0
$
LF
Cu
l
v
e
r
t
,
C
P
E
,
3
6
"
(N
o
t
a
l
l
o
w
e
d
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n
R
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W
)
D-
5
8
13
0
.
0
0
$
LF
Cu
l
v
e
r
t
,
L
C
P
E
,
6
"
D-
5
9
60
.
0
0
$
LF
53
0
0
31
8
,
0
0
0
.
0
0
Cu
l
v
e
r
t
,
L
C
P
E
,
8
"
D-
6
0
72
.
0
0
$
LF
Cu
l
v
e
r
t
,
L
C
P
E
,
1
2
"
D-
6
1
84
.
0
0
$
LF
18
5
7
15
5
,
9
8
8
.
0
0
12
8
10
,
7
5
2
.
0
0
Cu
l
v
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t
,
L
C
P
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,
1
5
"
D-
6
2
96
.
0
0
$
LF
Cu
l
v
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t
,
L
C
P
E
,
1
8
"
D-
6
3
10
8
.
0
0
$
LF
57
0
61
,
5
6
0
.
0
0
61
3
66
,
2
0
4
.
0
0
46
6
50
,
3
2
8
.
0
0
Cu
l
v
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,
L
C
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,
2
4
"
D-
6
4
12
0
.
0
0
$
LF
52
7
63
,
2
4
0
.
0
0
Cu
l
v
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t
,
L
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,
3
0
"
D-
6
5
13
2
.
0
0
$
LF
41
3
54
,
5
1
6
.
0
0
45
6
60
,
1
9
2
.
0
0
Cu
l
v
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t
,
L
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,
3
6
"
D-
6
6
14
4
.
0
0
$
LF
Cu
l
v
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t
,
L
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,
4
8
"
D-
6
7
15
6
.
0
0
$
LF
Cu
l
v
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t
,
L
C
P
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,
5
4
"
D-
6
8
16
8
.
0
0
$
LF
SU
B
T
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T
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:
61
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5
6
0
.
0
0
33
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,
9
4
8
.
0
0
43
9
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2
7
2
.
0
0
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(C
)
(D
)
(E
)
Pa
g
e
8
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f
1
4
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f
8
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H
B
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d
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c
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Un
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t
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p
d
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:
0
6
/
1
4
/
2
0
1
6
Ve
r
s
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n
:
0
6
/
1
4
/
2
0
1
6
Pr
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n
t
e
d
1
2
/
5
/
2
0
1
6
CE
D
P
e
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m
i
t
#
:
U
1
6
0
0
6
3
6
8
Ex
i
s
t
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n
g
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t
u
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Facility Summary Form9.2
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
2009 Surface Water Design Manual 1/9/2009 1
STORMWATER FACILITY SUMMARY SHEET DDES Permit
Number__________________
(provide one Stormwater Facility Summary Sheet per Natural Discharge Location)
Overview:
Project Name
_______________________________________________________Date___________________
Downstream Drainage Basins
Major Basin Name _____________________________
Immediate Basin Name __________________________
Flow Control:
Flow Control Facility Name/Number ________________________________
Facility
Location________________________________________________________________________
___
If none,
Flow control provided in regional/shared facility (give
location)___________________________________
No flow control required_____________ Exemption number
_______________________________
General Facility Information:
Type/Number of detention facilities: Type/Number of infiltration facilities:
______ ponds ______ ponds
______ vaults ______ tanks
______ tanks ______ trenches
Control Structure Location
_____________________________________________________________________
Type of Control Structure ______________________________ Number of Orifices/Restrictions
_____________
Size of Orifice/Restriction: No. 1 ________________
No. 2 ________________
No. 3 ________________
No. 4 ________________
Flow Control Performance Standard _________________________________
Allura at Tiffany Park 11/11/16
Cedar River
Ginger Creek
Tract A
N/A
N/A
N/A
1
Tract A (Inside Detention Vault)
Dual Orifice Restrictor
2.50 in
3.90 in
Flow Control Duration Standard Matching Forested Site Conditions
16055-F-StormWATR Facility Summary-KC-2016-11-11
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
2009 Surface Water Design Manual 1/9/2009 2
Live Storage Volume __________________ Depth _______________ Volume Factor of Safety
________________
Number of Acres Served ____________________
Number of Lots ____________________
Dam Safety Regulations (Washington State Department of Ecology)
Reservoir Volume above natural grade ________________
Depth of Reservoir above natural grade _______________
Facility Summary Sheet Sketch
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"x17" reduced size plan sheets may be used)
229,130 cf 11 ft
24.48 Acres
94
0 cf
0 ft
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
2009 Surface Water Design Manual 1/9/2009 3
Water Quality:
Type/Number of water quality facilities/BMPs:
______ biofiltration swale ______ sand filter (basic or large)
(regular/wet/ or continuous inflow) ______ sand filter, linear (basic or
large)
______ combined detention/wetpond ______ sand filter vault (basic or
large)
(wetpond portion basic or large) sand bed depth______ (inches)
______ combined detention/wetvault ______ stormwater wetland
______ filter strip ______ storm filter
______ flow dispersion ______ wetpond (basic or large)
______ farm management plan ______ wetvault
______ landscape management plan ______ Is facility Lined?
______ oil/water separator If so, what marker is used
above
(baffle or coalescing plate)
Liner?____________________
______ catch basin inserts:
Manufacturer____________________________________________
______ pre-settling pond
______ pre-settling structure:
Manufacturer__________________________________________
______ high flow bypass structure (e.g., flow-splitter catch basin)
______ source controls
_________________________________________________________
Design Information
Water Quality design flow ______________________________
Water Quality treated volume (sandfilter) ___________________
Water Quality storage volume (wetpool) ___________________
Facility Summary Sheet Sketch
1
0.47 cfs
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
2009 Surface Water Design Manual 1/9/2009 4
All detention, infiltration and water quality facilities must include a detailed sketch.
(11"x17" reduced size plan sheets may be used)
ALLURA AT TIFFANY PARK
AL
L
U
R
A
A
T
T
I
F
F
A
N
Y
P
A
R
K
TE
D
-
4
0
-
3
9
2
3
5/4/17
ALLURA AT TIFFANY PARK
AL
L
U
R
A
A
T
T
I
F
F
A
N
Y
P
A
R
K
TE
D
-
4
0
-
3
9
2
3
5/4/17
ALLURA AT TIFFANY PARK
AL
L
U
R
A
A
T
T
I
F
F
A
N
Y
P
A
R
K
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D
-
4
0
-
3
9
2
3
5/4/17
800-338-1122 513-645-7000 513-645-7993 FAX
9025 Centre Pointe Dr., Suite 400, West Chester, OH 45069
SF0822
STORMFILTER
STANDARD DETAILTHIS PRODUCT MAY BE PROTECTED BY ONE OR MORE OF THE FOLLOWINGU.S. PATENTS: 5,322,629; 5,524,576; 5,707,527; 5,985,157; 6,027,639; 6,649,048;RELATED FOREIGN PATENTS, OR OTHER PATENTS PENDING.
STORMFILTER TREATMENT CAPACITY IS A FUNCTION OF THE CARTRIDGE SELECTION AND THE NUMBER OF CARTRIDGES. THE STANDARD VAULTSTYLE IS SHOWN WITH THE MAXIMUM NUMBER OF CARTRIDGES (56). VAULT STYLE OPTIONS INCLUDE INLET BAY (49), INLET BAY/OUTLET BAY (46),
OUTLET BAY (51), NLET BAY/FULL HEIGHT BAFFLE WALL (41), FULL HEIGHT BAFFLE WALL (46). STORMFILTER 8X22 PEAK HYDRAULIC CAPACITY IS 1.8
CFS. IF THE SITE CONDITIONS EXCEED 1.8 CFS AN UPSTREAM BYPASS STRUCTURE IS REQUIRED.
F
OR
MAINTENANCE CALL 1.800.338.1 122
C l ean water starts here
GENERAL NOTES
1.CONTECH TO PROVIDE ALL MATERIALS UNLESS NOTED OTHERWISE.
2.DIMENSIONS MARKED WITH ( ) ARE REFERENCE DIMENSIONS. ACTUAL DIMENSIONS MAY VARY.3.FOR SITE SPECIFIC DRAWINGS WITH DETAILED VAULT DIMENSIONS AND WEIGHTS, PLEASE CONTACT YOUR CONTECH ENGINEERED SOLUTIONSLLC REPRESENTATIVE. www.ContechES.com
4.STORMFILTER WATER QUALITY STRUCTURE SHALL BE IN ACCORDANCE WITH ALL DESIGN DATA AND INFORMATION CONTAINED IN THIS
DRAWING.5.STRUCTURE SHALL MEET AASHTO HS20 LOAD RATING, ASSUMING EARTH COVER OF 0' - 5' AND GROUNDWATER ELEVATION AT, OR BELOW, THEOUTLET PIPE INVERT ELEVATION. ENGINEER OF RECORD TO CONFIRM ACTUAL GROUNDWATER ELEVATION. CASTINGS SHALL MEET AASHTO
M306 AND BE CAST WITH THE CONTECH LOGO.
6.FILTER CARTRIDGES SHALL BE MEDIA-FILLED, PASSIVE, SIPHON ACTUATED, RADIAL FLOW, AND SELF CLEANING. RADIAL MEDIA DEPTH SHALLBE 7-INCHES. FILTER MEDIA CONTACT TIME SHALL BE AT LEAST 38 SECONDS.
7.SPECIFIC FLOW RATE IS EQUAL TO THE FILTER TREATMENT CAPACITY (gpm) DIVIDED BY THE FILTER CONTACT SURFACE AREA (sq ft).
8.STORMFILTER STRUCTURE SHALL BE PRECAST CONFORMING TO ASTM C-857 AND AASHTO LOAD FACTOR DESIGN METHOD.
INSTALLATION NOTES
A.ANY SUB-BASE, BACKFILL DEPTH, AND/OR ANTI-FLOTATION PROVISIONS ARE SITE-SPECIFIC DESIGN CONSIDERATIONS AND SHALL BE
SPECIFIED BY ENGINEER OF RECORD.
B.CONTRACTOR TO PROVIDE EQUIPMENT WITH SUFFICIENT LIFTING AND REACH CAPACITY TO LIFT AND SET THE STORMFILTER VAULT (LIFTINGCLUTCHES PROVIDED).
C.CONTRACTOR TO INSTALL JOINT SEALANT BETWEEN ALL VAULT SECTIONS AND ASSEMBLE VAULT.
D.CONTRACTOR TO PROVIDE, INSTALL, AND GROUT PIPES. MATCH OUTLET PIPE INVERT WITH OUTLET BAY FLOOR.
E.CONTRACTOR TO TAKE APPROPRIATE MEASURES TO PROTECT CARTRIDGES FROM CONSTRUCTION-RELATED EROSION RUNOFF.
STORMFILTER DESIGN NOTES
CARTRIDGE HEIGHT
SPECIFIC FLOW RATE (gpm/sf)
CARTRIDGE FLOW RATE (gpm)
RECOMMENDED HYDRAULIC DROP (H)
27"18"LOW DROP
3.05'2.3'1.8'
CARTRIDGE SELECTION
18.79 12.53 8.35
2 gpm/sf
22.5 11.25 15 10 57.5
1.67* gpm/sf 1 gpm/sf 2 gpm/sf 1.67* gpm/sf 1 gpm/sf 2 gpm/sf 1.67* gpm/sf 1 gpm/sf
* 1.67 gpm/sf SPECIFIC FLOW RATE IS APPROVED WITH PHOSPHOSORB® (PSORB) MEDIA ONLY
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SECTION A-A
OUTLET PIPE
OVERFLOW
ASSEMBLY
GRADERING/RISERS
INLET
DISSIPATOR
INLET PIPE
CONTRACTOR TO
GROUT TO FINISHED
GRADE
STORMFILTERCARTRIDGE
FLOW KIT
STEP
OUTLETINLET
PLAN VIEW
VAULT STYLE: OUTLET SUMP (NIB)
INLETDISSIPATOR
(9'-3")
OUTLET SUMP
2'-
0
"
A A
(2'-0")
STORMFILTER CARTRIDGE
22'-0"
8'-
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"
ALTERNATE PIPELOCATION (TYP)
6" CONCRETE
WALL WIDTH
MAY VARYREGIONALLY
**
STRUCTURE ID
WATER QUALITY FLOW RATE (cfs)
PEAK FLOW RATE (cfs)
RETURN PERIOD OF PEAK FLOW (yrs)
NUMBER OF CARTRIDGES REQUIRED
MEDIA TYPE (PERLITE, ZPG, PSORB)
PIPE DATA:I.E.MATERIAL DIAMETER
INLET PIPE #1
INLET PIPE #2
OUTLET PIPE
SITE SPECIFIC
DATA REQUIREMENTS
WIDTH HEIGHTANTI-FLOTATION BALLAST
NOTES/SPECIAL REQUIREMENTS:
DOWNSTREAM RIM ELEVATION
CARTRIDGE FLOW RATE (gpm/f)
* PER ENGINEER OF RECORD
CARTRIDGE HEIGHT (27", 18", LOW DROP(LD))
UPSTREAM RIM ELEVATION
**
402.5
18"CPEP384.60
18"CPEP386.90
ZPG
1.00
53
100
5.53
0.47
SF#1
18"
402.5
ALLURA AT TIFFANY PARK
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ALLURA AT TIFFANY PARK
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Tab 10.0
16055.016.doc
10.0 OPERATIONS AND MAINTENANCE MANUAL
Allura at Tiffany Park has a single Detention Vault and a Contech StormFilter vault located within
Tract A of the proposed plat. Maintenance of these facilities shall be the responsibility of the
individual lot owners within the project development. The onsite conveyance system consists of a
series of catch basins and storm pipes which direct stormwater to the drainage facilities within
Tract A. Onsite Conveyance Systems within the right of way will be inspected and maintained by
the City of Renton. Onsite conveyance systems within the drainage easements or tracts will be
maintained by the property owners through the Homeowners' Association created by the
subdivision (with each property owner having equal responsibility for maintenance). These
conveyance elements include those entering and exiting the tract from/to the public right-of-way.
For conveyance pipes entering the tract from right-of-way, responsibility begins at the last
structure prior to entering the tract. For conveyance pipes exiting the tract to right-of-way,
responsibility ends at the next downstream structure. The easement shall grant the City rights for
inspection. Maintenance of the above listed stormwater facilities shall be conducted on an annual
basis. Please refer to the maintenance requirements within this section.
Tab 11.0
Appendix A