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TECHNICAL INFORMATION REPORT
Proposed Valley Medical Center
Medical Office Building Addition
Valley Medical Center Complex
Renton, Washington
Prepared for:
Valley Medical Center
June 12, 2017
Revised September 27, 2017
Revised November 2, 2017
Revised December 21, 2017
Revised January 15, 2017
Our Job No. 18092
18215 72ND AVENUE SOUTH KENT, WA 98032 (425) 251-6222 (425) 251-8782 FAX
BRANCH OFFICES TUMWATER, WA KLAMATH FALLS, OR LONG BEACH, CA ROSEVILLE, CA SAN DIEGO, CA
www.barghausen.com
01/15/18
DEVELOPMENT ENGINEERING
IFitz-James 01/19/2018
SURFACE WATER UTILITY
rstraka 01/22/2018
PLR-3964
TABLE OF CONTENTS
1.0 PROJECT OVERVIEW
Figure 1 – Technical Information Report (TIR) Worksheet
Figure 2 – Site Location
Figure 3 – Drainage Basins, Subbasins, and Site Characteristics
Figure 4 – Soils
2.0 CONDITIONS AND REQUIREMENTS SUMMARY
2.1 Analysis of the Core Requirements
2.2 Analysis of the Special Requirements
3.0 OFF-SITE ANALYSIS
4.0 FLOW CONTROL, LOW IMPACT DEVELOPMENT, 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
F. Flow Control BMP Analysis and Design
5.0 CONVEYANCE SYSTEM ANALYSIS AND DESIGN
6.0 SPECIAL REPORTS AND STUDIES
7.0 OTHER PERMITS
8.0 CONSTRUCTION STORMWATER POLLUTION PREVENTION PLAN ANALYSIS AND DESIGN
9.0 BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
10.0 OPERATIONS AND MAINTENANCE MANUAL
Tab 1.0
1.0 PROJECT OVERVIEW
The project site is located within the Northeast quarter of Section 31, Township 23 North, Range 5
East, Willamette Meridian, City of Renton, King County, Washington. More particularly, the site
lies slightly to the west of Talbot Road South, north of South 43rd Street, and easterly of SR-167.
The total area of redevelopment on this project site, the Medical Office Building (MOB), including
new landscape area, totals 1.96 acres. The on-site landscaping total is 0.142 acres, with total
impervious including building and parking of 1.68 acres, resulting in an impervious coverage of
~86%. There are several areas, both on and off-site, totaling to 0.337 acres, which bypass the
detention vaults on-site. A combination of mitigation trades and bypass areas are proposed to deal
with the runoff from these areas. There is a 0.123 acre green roof on-site as well. There are two
areas of asphalt overlay in the southeastern portion of the site, totaling to 0.055 acres.
A road improvement project is taking place on the access road to the immediate north of the project
site, as well as portions of Talbot Road South, and S. 43rd Street. The detention and water quality
vaults for these improvements will be placed in the northeastern corner of the MOB project site.
There are multiple off-site areas which cannot be drained into the vault. A mitigation trade is
proposed for these areas. Additionally, this vault will mitigate some of the on-site bypass area,
totaling to 0.059 acres. The water quality, conveyance and flow control sizing methodologies for
this associated road improvement are included in this report.
The project site drains to the west down a drive aisle within an existing pipe conveyance system
which is well documented through recent projects having occurred on this drive aisle, and courses
through a biofiltration swale at the northwest end of the Valley Medical Center and discharges from
that swale into Panther Creek located on the north side of Valley Medical Center. Panther Creek
drains northerly from that point through the Panther Creek wetlands area of the City of Renton with
an ultimate discharge to Springbrook Creek.
For purposes of sizing flow control and water quality, the City of Renton has indicated that the
duration standard, predeveloped forested, is the required means of providing flow control for this
project, with Enhanced Water Quality being the water quality menu to be followed. The proposal
for this development is to provide an underground detention vault sized for the area contributing
from the building roof and green-roof, with a pre-developed condition of till forest. The remaining
area will drain to a site detention vault (mostly impervious). A separate detention vault will be
provided for the associated road improvements.
Downstream of both the site detention vault, and the road detention vault, both of which collect
runoff from pollution generating impervious surfaces (PGIS), there will be modular wetland vaults,
which are proprietary devices with General Use Level Designation for Basic, Enhanced, and
Phosphorus Water Quality treatment through the Department of Ecology. The City of Renton is
well aware of the capability of these modular wetland systems as they have recently been reviewed
and approved on the Renton Marriott Inn Residence Inn project also located in Renton.
The SEPA Review determination has been issued. With this Final Technical Information Report,
the conveyance systems have been sized. Additionally, a Bond Quantity Worksheet, a Declaration
of Covenant, and an Operation and Maintenance Manual have been provided.
CITY OF RENTON SURFACE WATER DESIGN MANUAL
2017 City of Renton Surface Water Design Manual 12/12/2016 8-A-1
REFERENCE 8-A
TECHNICAL INFORMATION REPORT (TIR)
WORKSHEET
Part 1 PROJECT OWNER AND
PROJECT ENGINEER Part 2 PROJECT LOCATION AND
DESCRIPTION
Project Owner _____________________________
Phone ___________________________________
Address __________________________________
_________________________________________
Project Engineer ___________________________
Company _________________________________
Phone ___________________________________
Project Name __________________________
CED Permit # ________________________
Location Township ________________
Range __________________
Section _________________
Site Address __________________________
_____________________________________
Part 3 TYPE OF PERMIT APPLICATION Part 4 OTHER REVIEWS AND PERMITS
Land Use (e.g., Subdivision / Short Subd.)
Building (e.g., M/F / Commercial / SFR)
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 Site Improvement Plan (Engr. Plans)
Type of Drainage Review
(check one):
Date (include revision
dates):
Date of Final:
Full
Targeted
Simplified
Large Project
Directed
____________________________________
__________________
Plan Type (check
one):
Date (include revision
dates):
Date of Final:
Full
Modified
Simplified
____________________________________
__________________
Valley Medical Center
Ali Sadr
Barghausen Consulting Engineers, Inc.
(425) 251-6222
Medical Office Building
23N
5E
31
NWC - Talbot Road South
and South 43rd Street
June 12, 2017
Revised September 18,2017
REFERENCE 8: PLAN REVIEW FORMS AND WORKSHEET
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
12/12/2016 2017 City of Renton Surface Water Design Manual 8-A-2
Part 6 SWDM ADJUSTMENT APPROVALS
Type (circle one): Standard / Blanket
Description: (include conditions in TIR Section 2)
____________________________________________________________________________________
____________________________________________________________________________________
____________________________________________________________________________________
Approved Adjustment No. ______________________ Date of Approval: _______________________
Part 7 MONITORING REQUIREMENTS
Monitoring Required: Yes / No
Start Date: _______________________
Completion Date: _______________________
Describe: _________________________________
_________________________________________
_________________________________________
Re: SWDM Adjustment No. ________________
Part 8 SITE COMMUNITY AND DRAINAGE BASIN
Community Plan: ____________________________________________________________________
Special District Overlays: ______________________________________________________________
Drainage 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 ______________________
_____________________________________
Turbidity monitoring is required for
discharges leaving the site.
Renton
Panther Creek / Black River
REFERENCE 8-A: TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2017 City of Renton Surface Water Design Manual 12/12/2016 Ref 8-A-3
Part 10 SOILS
Soil Type
______________________
______________________
______________________
______________________
Slopes
________________________
________________________
________________________
________________________
Erosion Potential
_________________________
_________________________
_________________________
_________________________
High Groundwater Table (within 5 feet)
Other ________________________________
Sole Source Aquifer
Seeps/Springs
Additional Sheets Attached
Part 11 DRAINAGE DESIGN LIMITATIONS
REFERENCE
Core 2 – Offsite Analysis_________________
Sensitive/Critical Areas__________________
SEPA________________________________
LID Infeasibility________________________
Other________________________________
_____________________________________
LIMITATION / SITE CONSTRAINT
_______________________________________
_______________________________________
_______________________________________
_______________________________________
_______________________________________
_______________________________________
Additional Sheets Attached
Part 12 TIR SUMMARY SHEET (provide one TIR Summary Sheet
per Threshold Discharge Area)
Threshold Discharge Area:
(name or description)
Core Requirements (all 8 apply):
Discharge at Natural Location Number of Natural Discharge Locations:
Offsite Analysis Level: 1 / 2 / 3 dated:__________________
Flow Control (include facility
summary sheet)
Standard: _______________________________
or Exemption Number: ____________
On-site BMPs: _______________________________
Conveyance System Spill containment located at: _____________________________
Erosion and Sediment Control /
Construction Stormwater Pollution
Prevention
CSWPP/CESCL/ESC Site Supervisor: _____________________
Contact Phone: _________________________
After Hours Phone: _________________________
Alderwood Gravelly
Sandy Loam
Insufficient infiltration capacity.
Duration Standard - Predeveloped Forested
Green Roof, Soil Amendment.
June 12, 2017
REFERENCE 8: PLAN REVIEW FORMS AND WORKSHEET
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
12/12/2016 2017 City of Renton Surface Water Design Manual 8-A-4
Part 12 TIR SUMMARY SHEET (provide one TIR Summary Sheet
per Threshold Discharge Area)
Maintenance and Operation Responsibility (circle one): Private / Public
If Private, Maintenance Log Required: Yes / No
Financial Guarantees and Liability Provided: Yes / No
Water Quality (include facility
summary sheet)
Type (circle one): Basic / Sens. Lake / Enhanced Basic / Bog
or Exemption No. _______________________
Special Requirements (as applicable):
Area Specific Drainage
Requirements
Type: SDO / MDP / BP / Shared Fac. / None
Name: ________________________
Floodplain/Floodway Delineation Type (circle one): Major / Minor / Exemption / None
100-year Base Flood Elevation (or range): _______________
Datum:
Flood Protection Facilities Describe:
Source Control
(commercial / industrial land use)
Describe land use:
Describe any structural controls:
Oil Control High-Use Site: Yes / No
Treatment BMP: _________________________________
Maintenance Agreement: Yes / No
with whom? _____________________________________
Other Drainage Structures
Describe:
Roof over dumpster area.
None
REFERENCE 8-A: TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2017 City of Renton Surface Water Design Manual 12/12/2016 Ref 8-A-5
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 Collection
Dewatering Control
Dust Control
Flow Control
Control Pollutants
Protect Existing and Proposed BMPs/Facilities
Maintain Protective BMPs / Manage Project
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 BMPs/Facilities, restore
operation of BMPs/Facilities as necessary
Flag limits of sensitive areas 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
On-site BMPs
Other
________________
________________
________________
________________
________________
________________
Vegetated Flowpath
Wetpool
Filtration
Oil Control
Spill Control
On-site BMPs
Other
________________
________________
________________
________________
________________
________________
________________
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 _______________________________
Vault/Level 2
Modular Wetland
REFERENCE 8: PLAN REVIEW FORMS AND WORKSHEET
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
12/12/2016 2017 City of Renton Surface Water Design Manual 8-A-6
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.
____________________________________________________________________________________ Signed/Date
9/27/2017
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DN UPDNUP400LOBBY401STORSTAIR 8 STAIR 7ELEV 4ELEV 5403STORAGEELEV 3 UW MEDICINE - VALLEY MEDICAL CENTERROAD IMPROVEMENTS
Tab 2.0
2.0 CONDITIONS AND REQUIREMENTS SUMMARY
2.1 Analysis of the Eight Core Requirements
Core Requirement No. 1: Discharge at the Natural Location.
Response: This site will continue to discharge to the west down a drive aisle through a
pipe conveyance system previously sized for the runoff from this area without detention;
however, detention will be provided. The discharge locations for the road improvements
will also remain the same as existing.
Core Requirement No. 2: Off-Site Analysis.
Response: Please refer to Section 3.0 of this report for the Off-Site Analysis prepared for
this project site.
Core Requirement No. 3: Flow Control.
Response: Per City of Renton requirements on adopting the 2017 Renton Surface Water
Design Manual, which is an amendment to the 2016 King County Surface Water Design
Manual, the Flow Control Duration Standard, "matching durations with predeveloped
forested conditions," is assumed to be the level of flow control that is required for this site.
This standard was applied to all vaults associated with this project, including the road
improvement vaults. For the site detention vault, bypass areas were included in the sizing
calculations. For the road improvement vault, a mitigation trade is proposed to treat an
equivalent amount of runoff as the areas which cannot be directed into the vault. The
Western Washington Hydrology Model (WWHM) was utilized to size the flow control
facilities for this development.
Core Requirement No. 4: Conveyance System.
Response: The conveyance system has been sized based on the modified Rational
Method, designed to convey the 100-year runoff from the developed site.
Core Requirement No. 5: Erosion and Sediment Control.
Response: This project will concur with all erosion and sediment control requirements of
the 2017 Renton Surface Water Design Manual.
Core Requirement No. 6: Maintenance and Operations.
Response: A Maintenance and Operations Manual consistent with the City of Renton
requirements has been prepared for this project. See section 10.
Core Requirement No. 7: Financial Guarantees and Liability.
Response: This project will concur with all financial guarantees and liabilities requirements
of the City of Renton for projects of this nature.
Core Requirement No. 8: Water Quality.
Response: This project is providing a modular wetland system (MWS) to treat runoff from
PGIS for both the site and associated road improvements. This system which has
Department of Ecology approval for General Use Level Designation for Enhanced, Basic,
and Phosphorus Water Quality treatment capabilities.
Core Requirement No. 9: On-Site BMPs.
Response: According to section 1.2.9.2.2.5, since the development will result in an
impervious surface coverage greater than 65% on the buildable portion of the site, flow
control BMP's must be applied to 20% of the target impervious surfaces or to an impervious
area equal to at least 10% of the site/lot, whichever is less (RSWDM, 2017). The 1.96 acre
site contains 0.142 acres of landscaping, not including that in bypass areas. Consequently,
10% of the site (0.10 x 1.96 ac = 0.196 ac) is less than 20% of the target impervious
surfaces [(0.20 x (1.96 ac - 0.142 ac)) = 0.36 ac]. Therefore, BMP's must be applied to an
area equal to 0.196 acres
The use of a 0.123 acre vegetated roof is utilized to fulfill this requirement to the maximum
extent feasible. While the surface area of the green roof totals to 6.3% of the total site area,
the depth of water storage in the growing medium provides approximately twice the
minimum amount (3 inches) specified in the Vegetated Roof design section (C.2.15.1). See
section 4-F for calculations.
The road improvements are subject to on-site BMP requirements per section 1.2.9.3.2:
Small Road Improvement and Urban Road Improvement Projects BMP Requirements
(RSWDM, 2017). All road improvements BMPs area infeasible due to lack of infiltration
capacity of adequate vegetated area, per section 4-F.
2.2 Analysis of the Six Special Requirements
Special Requirement No. 1: Other Adopted Area-Specific Requirements.
Response: There are no known area-specific requirements applicable to this area of the
City of Renton, beyond those specified previously for flow-control and water quality.
Special Requirement No. 2: Flood Hazard Area Delineation.
Response: This project is not located in a flood hazard area as the site is over 30 feet
higher in elevation than Panther Creek lying northerly of the project site. Panther Creek
never would overtop that ravine to flood this project.
Special Requirement No. 3: Flood Protection Facilities.
Response: This project does not rely on an existing flood protection facility nor does it
propose to modify or construct a new flood protection facility; therefore, this Special
Requirement does not apply.
Special Requirement No. 4: Source Control.
Response: This project will provide Source Control in accordance with the King County
pollution prevention manual and King County Code Section 9.12 such that the owner will
be educated about the proper use of pesticides and fertilizers and the parking lot will be
swept on a regular basis. The roof over the dumpster area at the site will also function as
a source control by preventing runoff from coming into contact with potential contaminants
in the dumpster area. The runoff from the yard drain in the dumpster area will also flow into
the sanitary sewer system, rather than the storm drainage system.
Special Requirement No. 5: Oil Control.
Response: This project does not meet the requirements for a high-use site, therefore oil
control is not a requirement for this project. See the excerpt from the ITE manual below for
verification that the average daily traffic count for hospitals is less than 100 per 1,000
square feet of gross building area.
Special Requirement No. 6: Aquifer Protection Area.
Response: Per the City of Renton maps, the Valley Medical Center is not located in an
Aquifer Protection Area; therefore, this special requirement is not applicable to this site.
Tab 3.0
3.0 OFF-SITE ANALYSIS
The ultimate discharge location for this project site is into Panther Creek located northerly from the
project site; however, runoff from this project site will be treated through a modular wetland system
and discharged to the northwest down a drive aisle which courses westerly through the Valley
Medical Center development, ultimately draining into a biofiltration swale for additional water quality
treatment prior to discharge to Panther Creek which courses for over one (1) mile due north through
the Panther Creek wetland area of the City of Renton. From there, the Panther Creek flows into the
Black River, which flows into the Green River several miles downstream from the project site.
There is a 20 acre basin upstream of the project site that consists of various storm drainage
systems of the east side of Talbot Road S. and along S. Carr Road. There is also a 1.3 acre portion
of the parking lot to the immediate East, which is draining onto the project site. The runoff from
these basins is routed through the project site via an existing 30", concrete storm drainage pipe.
The 20 acre basin is composed of more than 20% pervious surfaces (Exhibit C). To be
conservative, the land cover in this basin was still estimated as 80% impervious. To simplify the
calculations, the 1.3 acre basin was also estimated as 80% impervious. This is a conservative
estimate since the 20 acre basin has greater than 20% pervious surfaces.
Stormshed3G was utilized to model the runoff from these areas. The proposed 30" CPEP pipe is
sufficient to convey the runoff from these upstream areas, in addition to the runoff from the
developed site. See the following model report for verification.
LEVEL 1 OFF-SITE DRAINAGE ANALYSIS
Proposed Valley Medical Center
Medical Office Building Addition
Valley Medical Center Complex
Renton, Washington
Prepared for:
Valley Medical Center
Renton, Washington
June 12, 2017
Revised September 27, 2017
Our Job No. 18092
18215 72ND AVENUE SOUTH KENT, WA 98032 (425) 251-6222 (425) 251-8782 FAX
BRANCH OFFICES TUMWATER, WA KLAMATH FALLS, OR LONG BEACH, CA ROSEVILLE, CA SAN DIEGO, CA
www.barghausen.com
LEVEL 1 OFF-SITE DRAINAGE ANALYSIS Proposed Valley Medical Center Medical Office Building Addition Renton Washington Our Job No. 18092
TABLE OF CONTENTS
1.0 TASK 1 – STUDY AREA DEFINITION AND MAPS
1.1 EXHIBIT A – Vicinity Map
1.2 EXHIBIT B – Downstream Drainage Course Map
1.3 EXHIBIT C – Upstream Basin Map
2.0 TASK 2 – RESOURCE REVIEW
2.1 EXHIBIT D – FEMA Map
2.2 EXHIBIT E – Sensitive Areas Folios
2.3 EXHIBIT F – SCS Soils Map
2.4 EXHIBIT G – Assessor's Map
2.5 EXHIBIT H – Wetland Inventory Map
3.0 TASK 3 – FIELD INSPECTION
3.1 Conveyance System Nuisance Problems (Type 1)
3.2 Severe Erosion Problems (Type 2)
3.3 Severe Flooding Problems (Type 3)
3.4 EXHIBIT I – Off-Site Analysis Drainage System Table
4.0 TASK 4 – DRAINAGE SYSTEM DESCRIPTION AND PROBLEM DESCRIPTIONS
5.0 TASK 5 – MITIGATION OF EXISTING OR POTENTIAL PROBLEMS
TASK 1
Study Area Definition and Maps
1.0 TASK 1 – STUDY AREA DEFINITION AND MAPS
The proposed Medical Office Building Addition is an approximately 2-acre redevelopment project
project located within the Northeast quarter of Section 31, Township 23 North, Range 5 East,
Willamette Meridian, City of Renton, King County, Washington. More particularly, the site lies
slightly to the west of Talbot Road South, north of South 43rd Street, and easterly of SR-167.
Please refer to the enclosed Exhibit A – Vicinity Map, which depicts the approximate location of
the proposed site.
The project site drains to the west down a drive aisle, which is well documented by recent
projects located along it, courses through a biofiltration swale at the end of the Valley Medical
Center, and discharges into Panther Creek almost immediately after the bioswale, which is
located on the north side of the Valley Medical Center. Panther Creek drains northerly from that
point through the Panther Creek wetlands area of the City of Renton, with an ultimate discharge
into Springbrook Creek, and then into the Black River further downstream.
The existing topography of the site is such that it drains from east to west at a fairly constant
slope. The area of redevelopment on this project lies at the north end of the overall Valley
Medical Center complex. One building and the existing parking lot will be removed in order to
construct this parking garage and provide access to it from Talbot Road South. There is one
downstream drain across from this project site, which drains immediately to the west into large-
diameter pipes flowing westerly. Please refer to the Off-Site Analysis Drainage System Table for
descriptions of the downstream drainage.
EXHIBIT A
Vicinity Map
EXHIBIT B
Downstream Drainage Course Map
WWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWNEW SDMH #4 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #1 TYPE 1,W/ VANED GRATENEW SDMH #1 TYPE 2-60"W/ SOLID LOCKING LIDNEW CB #2 TYPE 1,W/ SOLID LOCKING LIDFOOTING DRAIN CO #1EX. CB #570 TYPE 1,W/STANDARD GRATENEW CB #5 TYPE 1,W/ VANED GRATEEX. CB TYPE 2-72"w/ SOLID LOCKING LIDEX. CB TYPE 2-54"w/ SOLID LOCKING LIDNEW CB #4 TYPE 1,W/HERRINGBONE GRATEROOF DRAIN CO #1ROOF DRAIN CO #4ROOF DRAIN CO #5NEW SDMH #2 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #7 TYPE 1,W/ SOLID LOCKING LIDNEW SDMH #3 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #3 TYPE 1,W/ SOLID LOCKING LIDNEW CB #8 TYPE 2-48"W/ VANED GRATEINSTALL RISER TEEDETAIL PER SHEET C23NEW SDMH #7 TYPE 2-48"W/ SOLID LOCKING LIDNEW SDMH #6 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #9NEW CB #10 TYPE 1,W/ SOLID LOCKING LIDNEW CB #11 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #2ROOF DRAIN CO #3EX. CB #569 TYPE 1,W/ NEW SOLID LOCKING LIDMODULAR WETLAND #2NEW SDMH #5 TYPE 2-54"W/ SOLID LOCKING LIDMODULAR WETLAND #1ROOF DRAIN CO #7ROOF DRAIN CO #8UW MEDICINE - VALLEY MEDICAL CENTERMEDICAL OFFICE BUILDING EXPANSION1"=40'DOWNSTREAMDRAINAGE COURSEMAP 1/21234
1" = 40'10 NOTSHOWN56789DOWNSTREAM DRAINAGECOURSE MAP 2/2456781"=40'56789
EXHIBIT C
Upstream Basin Map
3,600600
This map is a user generated static output from an Internet mapping site and is for
reference only. Data layers that appear on this map may or may not be accurate,
current, or otherwise reliable.
WGS_1984_Web_Mercator_Auxiliary_Sphere
Notes
None
6/13/2017
Legend
408 204
THIS MAP IS NOT TO BE USED FOR NAVIGATION
Feet408
Information Technology - GIS
0
RentonMapSupport@Rentonwa.gov
Network Structures
Inlet
Manhole
Utility Vault
Unknown Structure
Control Structure
Pump Station
Discharge Point
Water Quality
Detention Facilities
Pond
Tank
Vault
Wetland
Stormwater Main
Culvert
Open Drains
Facility Outline
Private Network Structures
Inlet
Manhole
Utility Vault
Unknown Structure
Private Control Structure
Private Discharge Point
Private Water Quality
Private Detention Facilities
Pond
Tank
Vault
Wetland
Private Pipe
Private Culvert
Private Open Drains
Private Facility Outline
Fence
20 ac
UPSTREAM BASIN MAP
PROJECT SITE
EX. 30" STORM
DRAIN LINE
UPSTREAM BASIN MAP provide a breakdown of theland coverage in the upstreambasin (pervious, impervious, etc.)1.3
ac
1.47
AC.
0.65
AC.
U3
U2
U1
OFFSITE CONVEYANCE CALCULATIONS
WWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWNEW SDMH #4 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #1 TYPE 1,W/ VANED GRATENEW SDMH #1 TYPE 2-60"W/ SOLID LOCKING LIDNEW CB #2 TYPE 1,W/ SOLID LOCKING LIDFOOTING DRAIN CO #1EX. CB #570 TYPE 1,W/STANDARD GRATENEW CB #5 TYPE 1,W/ VANED GRATEEX. CB TYPE 2-72"w/ SOLID LOCKING LIDEX. CB TYPE 2-54"w/ SOLID LOCKING LIDNEW CB #4 TYPE 1,W/HERRINGBONE GRATEROOF DRAIN CO #1ROOF DRAIN CO #4ROOF DRAIN CO #5NEW SDMH #2 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #7 TYPE 1,W/ SOLID LOCKING LIDNEW SDMH #3 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #3 TYPE 1,W/ SOLID LOCKING LIDNEW CB #8 TYPE 2-48"W/ VANED GRATEINSTALL RISER TEEDETAIL PER SHEET C23NEW SDMH #7 TYPE 2-48"W/ SOLID LOCKING LIDNEW SDMH #6 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #8NEW CB #10 TYPE 1,W/ VANED GRATENEW CB #11 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #2ROOF DRAIN CO #3EX. CB #569 TYPE 1,W/ NEW SOLID LOCKING LIDMODULAR WETLAND #2NEW SDMH #5 TYPE 2-54"W/ SOLID LOCKING LIDMODULAR WETLAND #1ROOF DRAIN CO #6ROOF DRAIN CO #7UW MEDICINE - VALLEY MEDICAL CENTERMEDICAL OFFICE BUILDING EXPANSIONP-001P-002P-003P-004P-00525 LF 30" CPEP SD @ 0.48%NOTE:Pipe slopes and lengthsshown on plans areapproximate. Moreaccurate values areused for the upstreambasin conveyancecalculations.P-008P-007P-0060.50%4.67%
402'-8"
EX. UPSTREAM CB
RIM = 104.83'
I.E. OUT = 95.83'
REPLACE W/
NEW SDMH #1
100'-0"
Appended on: Friday, January 19, 2018 6:48:17 AM
ROUTEHYD [] THRU [MOB] USING [100 year] AND [TYPE1A.RAC] NOTZERO
RELATIVE SCS/SBUH
Gravity Analysis using 24 hr duration storm
HGL Analysis
Conduit Notes
Reach
ID
Area
(ac)
Flow
(cfs)
Full Q
(cfs)
Full
ratio
nDepth
(ft)
Depth
ratio Size nVel
(ft/s)
fVel
(ft/s)
Infil
Vol
(cf)
CBasin / Hyd
P-008 0.758 0.6628 2.3456 0.2826 0.3637 0.3637 12 in
Diam 2.5678 2.9865 0.00 ROAD
IMPROVEMENTS
P-007 0.758 0.6628 2.5044 0.2646 0.3511 0.3511 12 in
Diam 2.6939 3.1888 0.00
P-006 0.844 0.5987 4.0628 0.1474 0.2587 0.2587 12 in
Diam 3.7151 5.1729 0.00 MOB ROOFS
Upstream 20.00 16.6546 60.9022 0.2735 0.8934 0.3574 30 in
Diam 10.5739 12.4069 0.00 UPSTREAM 20 AC
BASIN
P-001 21.30 17.7891 96.2869 0.1848 0.7281 0.2912 30 in
Diam 14.9665 19.6154 0.00 UPSTREAM 1.3 AC
PARKING LOT
P-002 21.30 17.7891 31.5491 0.5639 1.3436 0.5374 30 in
Diam 6.6175 6.4271 0.00
P-003 22.144 18.3878 31.505 0.5836 1.3722 0.5489 30 in
Diam 6.6635 6.4182 0.00
P-004 22.144 18.3878 31.8777 0.5768 1.3622 0.5449 30 in
Diam 6.7244 6.4941 0.00
P-005 25.768 21.0356 26.4587 0.795 1.684 0.6736 30 in
Diam 5.9808 5.3901 0.00 Existing;PROTOTYPE
From Node To Node HG El
(ft)
App
(ft)
Bend
(ft)
Junct Loss
(ft)
Adjusted HG
El (ft)
Max El
(ft)
87.994
NEW SDHM #5 EX CB
DOWNSTREAM 88.7805 0.7021 0.0073 0.0210 88.1068 95.1600
MWS NEW SDHM #5 88.1310 --na----na----na--88.1310 98.1700
ROAD VAULT MWS 88.1563 --na----na----na--88.1563 94.7500
NEW SDMH #4 NEW SDHM #5 88.8843 0.6895 0.0381 ------88.2329 97.0300
NEW SDMH #3 NEW SDMH #4 89.2256 ------0.0296 0.0191 89.2743 97.0600
ROOF VAULT NEW SDMH #3 89.2873 --na----na----na--89.2873 94.7500
NEW SDMH #2 NEW SDMH #3 90.0720 3.4782 0.5134 ------87.1072 96.0100
NEW SDHM #1 NEW SDMH #2 91.5572 ------0.9244 ------92.4817 94.9500
EX UPSTREAM
CB NEW SDHM #1 97.8380 ------------------97.8380 104.8300
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Reach HW Depth (ft)HW/D ratio Q (cfs)TW Depth (ft)Dc (ft)Dn (ft)Comment
P-005 2.3505 0.9402 21.04 1.6840 1.5586 1.6840 Outlet Control M1 Backwater
P-007 1.7020 1.7020 0.66 1.6768 0.3394 0.3511 Outlet Control
P-008 1.0563 1.0563 0.66 1.0310 0.3394 0.3637 Outlet Control
P-004 2.3143 0.9257 18.39 1.6768 1.4537 1.3622 Outlet Control M1 Backwater
Subcritical, S-1 Profile
Subcritical flow starts at downstream end and progresses upstream until critical depth is reached.
y ft A sf R V ft Eft dEft Sf ft Savg ft So-Sf ft dx ft Station ft Elev ft
1.6768 3.5002 0.7295 5.2533 2.105318 0.00 0.002726 0.00 0.00 0.00 27.35 88.1068
1.6679 3.4792 0.728 5.285 2.101582 0.003736 0.002766 0.002746 0.002373 1.574658 25.7753 88.1059
1.6589 3.4582 0.7265 5.3172 2.097955 0.003627 0.002808 0.002787 0.002332 1.555611 24.2197 88.105
1.65 3.4371 0.7249 5.3499 2.094439 0.003515 0.002851 0.002829 0.00229 1.535405 22.6843 88.1039
1.6411 3.4159 0.7233 5.383 2.091039 0.003401 0.002895 0.002873 0.002246 1.513927 21.1704 88.1027
1.6322 3.3947 0.7217 5.4167 2.087756 0.003283 0.00294 0.002917 0.002202 1.49105 19.6794 88.1014
1.6232 3.3734 0.72 5.4508 2.084594 0.003162 0.002986 0.002963 0.002156 1.46663 18.2127 88.10
1.6143 3.3521 0.7184 5.4855 2.081556 0.003038 0.003034 0.00301 0.002109 1.440504 16.7722 88.0985
1.6054 3.3307 0.7166 5.5207 2.078645 0.002911 0.003083 0.003058 0.002061 1.412482 15.3597 88.0968
1.5965 3.3093 0.7149 5.5564 2.075865 0.00278 0.003133 0.003108 0.002011 1.38235 13.9774 88.0949
1.5875 3.2878 0.7131 5.5927 2.073219 0.002646 0.003184 0.003159 0.00196 1.349858 12.6275 88.0929
1.5786 3.2663 0.7113 5.6295 2.07071 0.002509 0.003237 0.003211 0.001908 1.314717 11.3128 88.0907
1.5697 3.2448 0.7095 5.6669 2.068343 0.002367 0.003292 0.003265 0.001854 1.276588 10.0362 88.0883
1.5608 3.2232 0.7076 5.7048 2.066121 0.002222 0.003348 0.00332 0.001799 1.235075 8.8011 88.0857
1.5518 3.2016 0.7057 5.7434 2.064049 0.002073 0.003406 0.003377 0.001742 1.189707 7.6114 88.0829
1.5429 3.1799 0.7038 5.7825 2.062129 0.001919 0.003465 0.003435 0.001684 1.139923 6.4715 88.0798
1.534 3.1582 0.7018 5.8223 2.060367 0.001762 0.003526 0.003495 0.001624 1.085048 5.3865 88.0764
1.5251 3.1364 0.6998 5.8627 2.058767 0.0016 0.003588 0.003557 0.001562 1.024264 4.3622 88.0727
1.5161 3.1146 0.6978 5.9037 2.057334 0.001434 0.003653 0.00362 0.001499 0.956568 3.4056 88.0687
1.5072 3.0928 0.6958 5.9453 2.056071 0.001262 0.003719 0.003686 0.001433 0.880718 2.5249 88.0643
1.4983 3.071 0.6937 5.9876 2.054985 0.001086 0.003787 0.003753 0.001366 0.795157 1.7298 88.0594
1.4894 3.0491 0.6916 6.0306 2.05408 0.000905 0.003857 0.003822 0.001297 0.697905 1.0319 88.0541
1.4804 3.0272 0.6895 6.0743 2.053361 0.000719 0.003929 0.003893 0.001226 0.586407 0.4454 88.0482
1.4715 3.0052 0.6873 6.1186 2.052834 0.000527 0.004003 0.003966 0.001153 0.457306 -0.0119 88.0416
The depth of flow at the upper end of the reach is 1.4717 ft.
Flow has returned to critical. The flow depth returned to critical 0.00 ft from the downstream lower end of reach.
P-003 2.1556 0.8622 18.39 1.6628 1.4537 1.3722 SuperCrit flow, Inlet end controls
P-006 2.1372 2.1372 0.60 2.1243 0.3218 0.2587 Outlet Control
P-002 2.2720 0.9088 17.79 2.2043 1.4284 1.3436 Outlet Control M1 Backwater
Subcritical, S-1 Profile
Subcritical flow starts at downstream end and progresses upstream until critical depth is reached.
y ft A sf R V ft Eft dEft Sf ft Savg ft So-Sf ft dx ft Station ft Elev ft
2.2043 4.582 0.7513 3.8824 2.438306 0.00 0.001431 0.00 0.00 0.00 145.59 89.2743
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Node and Reach invert report
2.1732 4.5307 0.7546 3.9263 2.412595 0.025711 0.001456 0.001444 0.00357 7.201099 138.3889 89.2793
2.1422 4.4774 0.7571 3.9731 2.387298 0.025297 0.001484 0.00147 0.003544 7.137441 131.2515 89.2841
2.1111 4.4221 0.7589 4.0228 2.362433 0.024865 0.001516 0.0015 0.003514 7.076292 124.1752 89.2885
2.0801 4.365 0.7601 4.0754 2.33802 0.024413 0.001553 0.001535 0.003479 7.016678 117.1585 89.2927
2.0491 4.3061 0.7607 4.1311 2.314083 0.023937 0.001594 0.001574 0.00344 6.957715 110.2008 89.2965
2.018 4.2457 0.7607 4.1899 2.290649 0.023434 0.00164 0.001617 0.003397 6.89856 103.3022 89.3001
1.987 4.1837 0.7602 4.252 2.267747 0.022902 0.00169 0.001665 0.003349 6.838372 96.4638 89.3033
1.956 4.1204 0.7592 4.3173 2.245412 0.022335 0.001746 0.001718 0.003296 6.776277 89.6876 89.3063
1.9249 4.0557 0.7577 4.3862 2.223683 0.02173 0.001807 0.001776 0.003238 6.711327 82.9762 89.3089
1.8939 3.9898 0.7557 4.4586 2.2026 0.021083 0.001873 0.00184 0.003174 6.642463 76.3338 89.3112
1.8629 3.9227 0.7532 4.5349 2.182211 0.020389 0.001946 0.00191 0.003104 6.568455 69.7653 89.3131
1.8318 3.8546 0.7503 4.615 2.162569 0.019642 0.002026 0.001986 0.003028 6.487843 63.2775 89.3146
1.8008 3.7854 0.747 4.6994 2.14373 0.018838 0.002114 0.00207 0.002944 6.398844 56.8786 89.3156
1.7698 3.7153 0.7432 4.788 2.12576 0.01797 0.002209 0.002161 0.002853 6.299225 50.5794 89.3162
1.7387 3.6443 0.739 4.8813 2.10873 0.01703 0.002313 0.002261 0.002753 6.186131 44.3933 89.3162
1.7077 3.5725 0.7345 4.9794 2.092719 0.016011 0.002427 0.00237 0.002644 6.055819 38.3375 89.3155
1.6767 3.50 0.7295 5.0826 2.077816 0.014903 0.002552 0.002489 0.002525 5.903251 32.4342 89.3141
1.6456 3.4267 0.7241 5.1913 2.064118 0.013697 0.002688 0.00262 0.002394 5.721461 26.7127 89.3117
1.6146 3.3528 0.7184 5.3057 2.051737 0.012381 0.002838 0.002763 0.002251 5.500504 21.2122 89.3083
1.5836 3.2783 0.7123 5.4263 2.040795 0.010942 0.003002 0.00292 0.002094 5.225637 15.9866 89.3034
1.5525 3.2033 0.7059 5.5534 2.031431 0.009365 0.003183 0.003093 0.001921 4.874 11.1126 89.2968
1.5215 3.1278 0.699 5.6875 2.023799 0.007632 0.003382 0.003283 0.001731 4.408092 6.7045 89.2879
1.4905 3.0518 0.6919 5.829 2.018072 0.005726 0.003602 0.003492 0.001522 3.76177 2.9427 89.2757
1.4594 2.9755 0.6844 5.9785 2.014449 0.003623 0.003844 0.003723 0.001291 2.806371 0.1364 89.2588
1.4284 2.8989 0.6765 6.1366 2.013151 0.001298 0.004113 0.003979 0.001035 1.253888 -1.1175 89.234
The depth of flow at the upper end of the reach is 1.456 ft.
Flow has returned to critical. The flow depth returned to critical 0.00 ft from the downstream lower end of reach.
P-001 2.0572 0.8229 17.79 1.4284 1.4284 0.7281 SuperCrit flow, Inlet end controls
Upstream 2.0080 0.8032 16.65 2.9817 1.3801 0.8934 SuperCrit flow, Inlet end controls
Node and Reach invert report
Node ROAD VAULT Out ie 87.25 ft
Reach P-008 I.E. Out 87.25 ft
Node MWS Out ie 86.60 ft
Reach P-008 I.E. In 87.10 ft
Reach P-007 I.E. Out 86.60 ft
Node ROOF VAULT Out ie 87.25 ft
Reach P-006 I.E. Out 87.25 ft
Node EX UPSTREAM CB Out ie 95.83 ft
Reach Upstream I.E. Out 95.83 ft
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Licensed to: Engenious Systems, Inc.
Node NEW SDHM #1 Out ie 89.50 ft
Reach Upstream I.E. In 89.50 ft
Reach P-001 I.E. Out 89.50 ft
Node NEW SDMH #2 Out ie 87.80 ft
Reach P-001 I.E. In 87.80 ft
Reach P-002 I.E. Out 87.80 ft
Node NEW SDMH #3 Out ie 87.07 ft
Reach P-006 I.E. In 87.15 ft
Reach P-002 I.E. In 87.07 ft
Reach P-003 I.E. Out 87.07 ft
Node NEW SDMH #4 Out ie 86.57 ft
Reach P-003 I.E. In 86.5701 ft
Reach P-004 I.E. Out 86.57 ft
Node NEW SDHM #5 Out ie 86.43 ft
Reach P-007 I.E. In 86.43 ft
Reach P-004 I.E. In 86.43 ft
Reach P-005 I.E. Out 86.43 ft
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Appended on: Friday, January 19, 2018 6:44:46 AM
Layout Report: MOB
Reach Records
Record Id: P-001
Record Id: P-002
Event Precip (in)
2 yr 24 hr 2.00
5 year 2.50
10 year 2.90
25 year 3.40
100 year 3.90
Section Shape:Circular
Uniform Flow Method:Manning's Coefficient:0.012
Routing Method:Travel Time Shift Contributing Hyd
DnNode NEW SDMH #2 UpNode NEW SDHM #1
Material unspecified Size 30 in Diam
Ent Losses Groove End w/Headwall
Length 36.40 ft Slope 4.67%
Up Invert 89.50 ft Dn Invert 87.80 ft
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
Section Shape:Circular
Uniform Flow Method:Manning's Coefficient:0.012
Routing Method:Travel Time Shift Contributing Hyd
DnNode NEW SDMH #3 UpNode NEW SDMH #2
Material unspecified Size 30 in Diam
Ent Losses Groove End w/Headwall
Length 145.59 ft Slope 0.50%
Up Invert 87.80 ft Dn Invert 87.07 ft
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Record Id: P-003
Record Id: P-004
Record Id: P-005
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
Section Shape:Circular
Uniform Flow Method:Manning's Coefficient:0.012
Routing Method:Travel Time Shift Contributing Hyd
DnNode NEW SDMH #4 UpNode NEW SDMH #3
Material unspecified Size 30 in Diam
Ent Losses Groove End w/Headwall
Length 101.00 ft Slope 0.50%
Up Invert 87.07 ft Dn Invert 86.5701 ft
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
Section Shape:Circular
Uniform Flow Method:Manning's Coefficient:0.012
Routing Method:Travel Time Shift Contributing Hyd
DnNode NEW SDHM #5 UpNode NEW SDMH #4
Material unspecified Size 30 in Diam
Ent Losses Groove End w/Headwall
Length 27.35 ft Slope 0.51%
Up Invert 86.57 ft Dn Invert 86.43 ft
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
Section Shape:Circular
Page 2 of 11
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Record Id: P-006
Record Id: P-007
Uniform Flow Method:Manning's Coefficient:0.014
Routing Method:Travel Time Shift Contributing Hyd
DnNode EX CB DOWNSTREAM UpNode NEW SDHM #5
Material unspecified Size 30 in Diam
Ent Losses Groove End w/Headwall
Length 25.00 ft Slope 0.48%
Up Invert 86.43 ft Dn Invert 86.31 ft
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
Section Shape:Circular
Uniform Flow Method:Manning's Coefficient:0.014
Routing Method:Travel Time Shift Roof Vault FC
DnNode NEW SDMH #3 UpNode ROOF VAULT
Material unspecified Size 12 in Diam
Ent Losses Groove End w/Headwall
Length 6.66 ft Slope 1.50%
Up Invert 87.25 ft Dn Invert 87.15 ft
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
Section Shape:Circular
Uniform Flow Method:Manning's Coefficient:0.014
Routing Method:Travel Time Shift Contributing Hyd
DnNode NEW SDHM #5 UpNode MWS
Material unspecified Size 12 in Diam
Ent Losses Groove End w/Headwall
Length 30.00 ft Slope 0.57%
Up Invert 86.60 ft Dn Invert 86.43 ft
Page 3 of 11
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Record Id: P-008
Record Id: Upstream
Node Records
Record Id: EX CB DOWNSTREAM
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
Section Shape:Circular
Uniform Flow Method:Manning's Coefficient:0.014
Routing Method:Travel Time Shift Road Vault FC
DnNode MWS UpNode ROAD VAULT
Material unspecified Size 12 in Diam
Ent Losses Groove End w/Headwall
Length 30.00 ft Slope 0.50%
Up Invert 87.25 ft Dn Invert 87.10 ft
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
Section Shape:Circular
Uniform Flow Method:Manning's Coefficient:0.011
Routing Method:Travel Time Shift Contributing Hyd
DnNode NEW SDHM #1 UpNode EX UPSTREAM CB
Material unspecified Size 30 in Diam
Ent Losses Groove End w/Headwall
Length 402.67 ft Slope 1.57%
Up Invert 95.83 ft Dn Invert 89.50 ft
Conduit Constraints
Min Vel Max Vel Min Slope Max Slope Min Cover
2.00 ft/s 15.00 ft/s 0.50%2.00%3.00 ft
Drop across MH 0.00 ft Ex/Infil Rate 0.00 in/hr
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Record Id: EX UPSTREAM CB
Record Id: MWS
Record Id: NEW SDHM #1
Record Id: NEW SDHM #5
Descrip:Increment 0.10 ft
Start El.86.31 ft Max El.94.46 ft
Void Ratio 100.00
Condition Existing Structure Type CB-TYPE 2-54
Channelization No Special Shape
Catch 0.00 ft Bottom Area 15.904 sf
MH/CB Type Node
Descrip:Increment 0.10 ft
Start El.95.83 ft Max El.104.83 ft
Void Ratio 100.00
Condition Existing Structure Type CB-TYPE 2-54
Channelization No Special Shape
Catch 0.00 ft Bottom Area 15.904 sf
MH/CB Type Node
Descrip:Water Quality Increment 0.10 ft
Start El.86.60 ft Max El.98.17 ft
Void Ratio 100.00
Length 8.00 ft Width 4.00 ft
Vault Type Node
Descrip:Increment 0.10 ft
Start El.89.50 ft Max El.94.95 ft
Void Ratio 100.00
Condition Existing Structure Type CB-TYPE 2-60
Channelization No Special Shape
Catch 0.00 ft Bottom Area 19.634 sf
MH/CB Type Node
Descrip:Increment 0.10 ft
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Record Id: NEW SDMH #2
Record Id: NEW SDMH #3
Record Id: NEW SDMH #4
Record Id: ROAD VAULT
Start El.86.43 ft Max El.95.16 ft
Void Ratio 100.00
Condition Existing Structure Type CB-TYPE 2-54
Channelization No Special Shape
Catch 0.00 ft Bottom Area 15.904 sf
MH/CB Type Node
Descrip:Increment 0.10 ft
Start El.87.80 ft Max El.96.01 ft
Void Ratio 100.00
Condition Existing Structure Type CB-TYPE 2-54
Channelization No Special Shape
Catch 0.00 ft Bottom Area 15.904 sf
MH/CB Type Node
Descrip:Increment 0.10 ft
Start El.87.07 ft Max El.97.06 ft
Void Ratio 100.00
Condition Existing Structure Type CB-TYPE 2-54
Channelization No Special Shape
Catch 0.00 ft Bottom Area 15.904 sf
MH/CB Type Node
Descrip:Increment 0.10 ft
Start El.86.57 ft Max El.97.03 ft
Void Ratio 100.00
Condition Existing Structure Type CB-TYPE 2-54
Channelization No Special Shape
Catch 0.00 ft Bottom Area 15.904 sf
MH/CB Type Node
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Record Id: ROOF VAULT
Contributing Drainage Areas
Record Id: Existing
Record Id: MOB ROOFS
Descrip:Increment 0.10 ft
Start El.87.25 ft Max El.94.75 ft
Void Ratio 100.00
Length 100.00 ft Width 19.00 ft
Vault Type Node
Descrip:Increment 0.10 ft
Start El.87.25 ft Max El.94.75 ft
Void Ratio 100.00
Length 124.00 ft Width 20.00 ft
Vault Type Node
Design Method SBUH Rainfall type TYPE1.RAC
Hyd Intv 10.00 min Peaking Factor 484.00
Storm Duration 24.00 hrs Abstraction Coeff 0.20
Pervious Area 0.866 ac DCIA 0.00 ac
Pervious CN 80.00 DC CN 0.00
Pervious TC 5.00 min DC TC 5.00 min
Pervious CN Calc
Description SubArea Sub cn
Open spaces, lawns,parks (>75% grass)0.866 ac 80.00
Pervious Composited CN (AMC 2)80.00
Pervious TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
DCI - TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
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Record Id: PROTOTYPE
Design Method SBUH Rainfall type TYPE1.RAC
Hyd Intv 10.00 min Peaking Factor 484.00
Storm Duration 24.00 hrs Abstraction Coeff 0.20
Pervious Area 0.844 ac DCIA 0.00 ac
Pervious CN 90.00 DC CN 0.00
Pervious TC 5.00 min DC TC 5.00 min
Pervious CN Calc
Description SubArea Sub cn
Impervious surfaces (pavements, roofs, etc)0.844 ac 90.00
Pervious Composited CN (AMC 2)90.00
Pervious TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
DCI - TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
Design Method SBUH Rainfall type TYPE1.RAC
Hyd Intv 10.00 min Peaking Factor 484.00
Storm Duration 24.00 hrs Abstraction Coeff 0.20
Pervious Area 1.00 ac DCIA 1.00 ac
Pervious CN 90.00 DC CN 98.00
Pervious TC 5.00 min DC TC 5.00 min
Pervious CN Calc
Description SubArea Sub cn
Open spaces, lawns, parks (50-75% grass)1.00 ac 90.00
Pervious Composited CN (AMC 2)90.00
Pervious TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
DCI - CN Calc
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Record Id: ROAD IMPROVEMENTS
Record Id: UPSTREAM 1.3 AC PARKING LOT
Description SubArea Sub cn
Impervious surfaces (pavements, roofs, etc)1.00 ac 98.00
DC Composited CN (AMC 2)98.00
DCI - TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
Design Method SBUH Rainfall type TYPE1.RAC
Hyd Intv 10.00 min Peaking Factor 484.00
Storm Duration 24.00 hrs Abstraction Coeff 0.20
Pervious Area 0.043 ac DCIA 0.715 ac
Pervious CN 86.00 DC CN 98.00
Pervious TC 5.00 min DC TC 5.00 min
Pervious CN Calc
Description SubArea Sub cn
Open spaces, lawns,parks (>75% grass)0.043 ac 86.00
Pervious Composited CN (AMC 2)86.00
Pervious TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
DCI - CN Calc
Description SubArea Sub cn
Roads (hard surface - includes right of way)0.715 ac 98.00
DC Composited CN (AMC 2)98.00
DCI - TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
Design Method SBUH Rainfall type TYPE1.RAC
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Record Id: UPSTREAM 20 AC BASIN
Hyd Intv 10.00 min Peaking Factor 484.00
Storm Duration 24.00 hrs Abstraction Coeff 0.20
Pervious Area 0.13 ac DCIA 1.17 ac
Pervious CN 90.00 DC CN 98.00
Pervious TC 5.00 min DC TC 5.00 min
Pervious CN Calc
Description SubArea Sub cn
Open spaces, lawns, parks (50-75% grass)0.13 ac 90.00
Pervious Composited CN (AMC 2)90.00
Pervious TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
DCI - CN Calc
Description SubArea Sub cn
Impervious surfaces (pavements, roofs, etc)1.17 ac 98.00
DC Composited CN (AMC 2)98.00
DCI - TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
Design Method SBUH Rainfall type TYPE1.RAC
Hyd Intv 10.00 min Peaking Factor 484.00
Storm Duration 24.00 hrs Abstraction Coeff 0.20
Pervious Area 4.00 ac DCIA 16.00 ac
Pervious CN 86.00 DC CN 98.00
Pervious TC 5.00 min DC TC 5.00 min
Pervious CN Calc
Description SubArea Sub cn
Open spaces, lawns,parks (>75% grass)4.00 ac 86.00
Pervious Composited CN (AMC 2)86.00
Pervious TC Calc
Type Description Length Slope Coeff Misc TT
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Licensed to: Engenious Systems, Inc.
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
DCI - CN Calc
Description SubArea Sub cn
Impervious surfaces (pavements, roofs, etc)16.00 ac 98.00
DC Composited CN (AMC 2)98.00
DCI - TC Calc
Type Description Length Slope Coeff Misc TT
Sheet 0.00 ft 0.0%5.0 0.00 in 5.00 min
Pervious TC 5.00 min
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Pipe and Structure Labels
Structure Rim Elevations
and Pipe Slopes
In-Structure Hydraulic Grade Line
and Pipe Discharge
Structure Labels
and Pipe Diameters
Structure Labels
and Pipe Lengths
Contributing Areas
TASK 2
Resource Review
2.0 TASK 2 – RESOURCE REVIEW
Adopted Basin Plans:
There are no available adopted basin plans for this area of King County. However, the
City of Renton has indicated that Level 2 flow control is required, also known as the Flow
Control Duration standard (predeveloped forested condition). This is a conservative
sizing methodology, particularly since no detention is currently available on this
redeveloped area. The impacts from the project site should be minimal after the project is
constructed.
Finalized Drainage Studies:
This is not applicable.
Critical Drainage Area Maps:
The City maps indicate that we have to design to enhanced water quality standards and
Level 2 flow control.
Floodplain and Floodway FEMA Maps:
Please see the enclosed Exhibit D - FEMA Map utilized for this analysis, which is Panel
No. 979 of 1,725, Map No. 53033C0979 F, revised in May 1995. As indicated by this
map, the project site is not located within a floodway or floodplain of a stream or river.
Please refer to that exhibit for the exact location of the project site.
Other Off-Site Analysis Reports:
There have been several projects of new construction within the medical complex to
expand the services of a regional hospital serving the community. However, the
downstream drainage course passes through a well-documented area of the medical
center.
Sensitive Areas Folios:
The King County Sensitive Areas Map Folios were reviewed for this site, and the only
sensitive areas that were found on the project were Panther Creek, lying northerly of the
site, and a heavily vegetated area along the Panther Creek stream path, which is
considered an erosion hazard. But there is no part of the on-site development that could
be considered an erosion hazard. The erosion hazard area is completely off site from the
medical center.
Road Drainage Problems:
This is not applicable.
United States Department of Agriculture King County Soils Survey:
Based on the Soils Survey for this portion of King County, the entire site lies within
Alderwood gravelly sandy loam with 8 percent to 15 percent slopes, which is a Type C
soil that does not infiltrate very readily.
Wetland Inventory Map:
There are no mapped wetlands on this site.
Migrating River Studies:
This is not applicable.
EXHIBIT D
FEMA Map
EXHIBIT E
Sensitive Areas Folios
EXHIBIT F
SCS Soils Map
EXHIBIT G
Assessor's Map
EXHIBIT H
Wetland Inventory Map
There are no wetlands on this project site.
TASK 3
Field Inspection
3.0 TASK 3 – FIELD INSPECTION
There were no problems reported or observed during the resource review, nor did the field
reconnaissance find any potential constrictions or lack of capacity in the existing drainage system
proposed for use downstream from this project site.
3.1 Conveyance System Nuisance Problems (Type 1)
Conveyance system nuisance problems are minor but chronic flooding or erosion
problems caused by overflow from 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.
Based on the resource review and site visit, the entire downstream drainage course
passes through a pipe conveyance system, and there is no evidence of conveyance
system nuisance problems occurring.
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.
Per the resource review and our site visit, there was no erosion occurring in the
downstream drainage course. The runoff characteristics from this portion of the medical
center should actually lessen impacts on the downstream drainage course, since flow
control is being provided for this entire site. Previously there was no on-site detention for
the building or for the former parking lot that exists there.
3.3 Severe Flooding Problems (Type 3)
Severe flooding problems, i.e., a severe building flooding problem or severe roadway
flooding problem can be caused by conveyance system overflows or the elevated water
surfaces of ponds, lakes, wetlands, or closed depressions. Severe flooding problems
warrant additional attention because they pose a significant threat either to health and
safety or to public or private property.
There are no current problems occurring with the downstream drainage course, since the
downstream drainage course consists chiefly of pipes and swales, which appear to be
sized adequately for all runoff contributing to them. There is no history of flooding on this
project site, and it is not anticipated that there will be any after development.
The site was visited on February 15, 2017. The sky was cloudy with rain and the high
temperature was 52º. See the following pages for photos of the site.
EXHIBIT I
Off-Site Analysis
Drainage System Table
OFF-SITE ANALYSIS DRAINAGE SYSTEM TABLE
Surface Water Design Manual, Core Requirement #2
Basin: Black River Subbasin Name: Panther Creek Subbasin Number:
Symbol
Drainage Component
Type, Name, and Size
Drainage Component
Description Slope
Distance from
Site Discharge
Existing
Problems
Potential
Problems
Observations of Field Inspector,
Resource Reviewer, or Resident
See Map
Type: sheet flow, swale, stream,
channel, pipe, pond; size,
diameter, surface area
Drainage basin, vegetation, cover,
depth, volume,
type of sensitive area % Feet.
Constrictions, under capacity,
ponding, overtopping, flooding,
habitat or organism destruction,
scouring, bank sloughing,
sedimentation, incision,
other erosion
Tributary area, likelihood of problem,
overflow pathways, potential impacts
U1 30-inch concrete pipe Flows from 20 acre basin
upstream onto project site.
0 ft upstream none noted none noted
U2 6-inch concrete pipe Flows from adjacent 1.3 acre
basin onto project site.
0 ft upstream none noted none noted
U3 8-inch concrete pipe Flows from adjacent 1.3 acre
basin onto project site.
0 ft upstream none noted none noted
U4 Existing SDMH Receives runoff from 20 acre
basin upstream. Flows into 30
inch concrete pipe.
415 ft upstream none noted none noted
1 30-inch CPEP Flows N. Connection to existing
30" SD on Talbot Rd. South.
0.5 0 ft none noted none noted
2 12-inch CPEP Flows North MWS to Ex. CB 1.0 0 feet - 34 feet none noted none noted
3 30-inch CMP Flows NW 2.7 34 feet - 48 feet none noted none noted
4 30-inch CMP Flows NW 8.81 48 feet - 148 feet none noted none noted
5 30-inch CMP Flows NW --- 148 feet - 254 feet none noted none noted
6 30-inch CMP Flows NW --- 254 feet - 359 feet none noted none noted
7 30-inch CMP Flows NW --- 359 feet - 489 feet none noted none noted
8 30-inch CMP Flows NW, outlets to Bio-swale --- 489 feet - 609 feet none noted none noted
9 Bio-swale Flows west then north, outfalls to
Panther Creek
--- 609 feet - 809 feet none noted none noted
10 Panther Creek Follows SR 167 for over 1/2 mile --- 809 feet - 2900 feet none noted none noted
TASK 4
Drainage System Description
and Problem Descriptions
4.0 TASK 4 – DRAINAGE SYSTEM DESCRIPTION AND PROBLEM
DESCRIPTIONS
Runoff from the project site will be routed to the major conveyance element on the north side of
the medical center complex. This downstream drainage course consists chiefly of 30-inch
diameter CMP culverts. As mentioned previously, the release rate from the detention vault
proposed for this project site is much less than current site conditions allow, which currently
discharges runoff without providing detention. In addition, water quality will be provided for this
project site in the form of a modular wetland system. Therefore, there shouldn't be any problems
occurring from this new development.
TASK 5
Mitigation of Existing
or Potential Problems
5.0 TASK 5 – MITIGATION OF EXISTING OR POTENTIAL PROBLEMS
Since flow control will be provided by this project, which was not provided previously for this
portion of the medical center, the proposed flow control and water quality standards should
mitigate any impacts from new development in this portion of the redevelopment project. This
project will also provide enhanced water quality, for which modular wetland systems have GULD
from the Department of Ecology. In addition, a coalescing plate oil/water separator at the outlet to
the garage will collect any oil and keep it from being discharged into the downstream drainage
course. This is over and above what currently exists on this project site. Therefore, runoff
characteristics should actually improve quite a bit.
Tab 4.0
4.0 FLOW CONTROL, LOW IMPACT DEVELOPMENT, AND WATER QUALITY FACILITY
ANALYSIS AND DESIGN
A. Existing Site Hydrology
Since the City has indicated that the Duration Standard – predeveloped forested – is the
required flow control menu to be followed for this site, the pre-developed condition must be
modeled as till forest. However, there are portions of the existing pre-developed conditions
that consist of impervious surface as well as landscape areas. These will be ripped out
with new impervious surface to replace most of the existing development on the site, with
the exception of 0.055 acres of asphalt which will be overlain, and thus does not count as
new or replaced impervious surface. See the tables in Section B, below, for the
predeveloped conditions which were modelled for each vault.
B. Developed Site Hydrology
The total area of development on this site is 1.96 acres. Two separate detention vaults are
required to treat the runoff from this site, one for the pollution generating impervious
surfaces (including the bypass areas) and landscaping, and the other for roof runoff,
including the green-roof. These are respectively referred to as the "roof vault" and the "site
vault". The site vault will discharge into a MWS for enhanced treatment, whereas the roof
vault will discharge directly to the existing storm drainage system. There will be another
vault on-site which receive runoff from the road improvements. This will be followed by a
MWS as well.
There are two areas on-site, totaling to 0.117 acres. These areas will be divided between
the vaults intended for PGIS, the site vault and the road vault. The road vault is proposing
a mitigation trade for its respective portion of bypass area, since there is additional,
undisturbed, upstream area contributing to the vault. The land cover of the contributing
upstream area is a pollution generating impervious surface, whereas not all of the bypass
areas are pollution generating, i.e. the multiple ADA ramps on Talbot Rd. S. and S 43rd St.
Therefore, treatment of this mitigation trade area will provide more water quality benefits
than required.
The site vault is sized to compensate for the bypass area by detaining the flows contributing
to it so the net effect of flow control downstream is if the vault were able to capture runoff
from the bypass area. This is achieved by detaining the runoff for a longer period of time.
The green roof was modelled as 50% impervious and 50% pasture since the growing
medium is greater than 8 inches in depth, per table 1.2.9.A (RSWDM, 2017).
Acreage
1.051
1.051
Pre-
developed
Land Cover
Forested
Total
Site Detention Vault
Landscape 0.016
Impervious 0.042 0.058
0.142
0.851
1.051DevelopedLandscape
Impervious
Bypass
Total
C. Performance Standards
The area-specific flow control facility standard determined from the City of Renton is the
Duration Standard – which requires the predeveloped site conditions to be modeled as till
forest. The conveyance system capacity standard for this development will be the Modified
Rational Method as adopted by the City of Renton. The area-specific water quality
treatment menu to be followed for this project site is the Enhanced Water Quality Menu,
which is met with a modular wetland system for the pollution generating impervious
surfaces associated with both the on-site improvements as well as the road improvements.
D. Flow Control System
The flow control duration standard of matching forested site conditions requires that the
developed discharge durations shall not exceed predeveloped durations for the range of
predeveloped discharge rates from 50% of the 2-year peak flow up to the full 50-year peak
flow. WWHM automatically applies the duration standard to each vault. Furthermore, flow
control duration standard requires that developed peak discharge rates shall not exceed
predeveloped peak discharge rates for the 2- and 10- year return periods. The figure below
shows that the release rates from the detention vaults on-site do not exceed the
predeveloped discharge rates for the 2- and 10- year return periods. This data is also
included in the following WWHM reports.
0.844
0.844
Acreage
Roof Detention Vault
Land Cover
Pre-
developed
Forested
Total
Pasture 0.0615
Impervious 0.0615 0.123
0.721
0.844DevelopedRooftop
Green-
roof
Total
Acreage
Threshold Discharge Area 0.428
Mitigation Area 0.279 0.707
Road Improvement Detention Vault
Land Cover
0.051
Total
Impervious (Excess Mitigation Area)
Pre-
developed
Forested
0.758
DevelopedLandscape
Impervious
Total 0.758
0.043
0.715
Predeveloped
Flow (cfs)
Developed
Flow (cfs)
Excursion
(%)
Predeveloped
Flow (cfs)
Developed
Flow (cfs)
Excursion
(%)
Predeveloped
Flow (cfs)
Developed
Flow (cfs)
Excursion
(%)
2 year 0.057 0.033 -42%0.025 0.015 -40%0.034 0.017 -50%
10 year 0.108 0.054 -50%0.047 0.028 -40%0.059 0.031 -47%
Detention Vault Performance Results
Return
Period
Site Detention Vault Roof Detention Vault Road Improvement Vault
Each on-site detention vault is equipped with a 12" riser, which is capable of conveying
flows of ~2.7 cfs with 0.5 feet of head (see figure 3.2.16 below). The 100-year discharge
from the vaults range from 0.06 to 0.1 cubic feet per second. Thus, the risers are effectively
designed as bypasses for the 100-year event.
There is 0.058 acres of bypass area that has been compensated for in the Site Detention
Vault. These areas have been mitigated per section 1.2.3.2.E of the 2017 RSWDM as
follows:
1. The point of convergence for runoff from the bypass areas and the discharge from
the detention vault is located within a quarter-mile downstream of the project site's
discharge point.
2. The increase in the existing site conditions 100-year peak discharge from the 0.058
acre area of bypassed target surfaces does not exceed 0.4 cfs, as the runoff from
the developed site during the 100-year storm is only 0.04 cfs. See the associated
WWHM report on the following pages for verification.
3. No significant adverse impacts to downstream drainage systems are caused by
runoff from these bypass areas
4. Water quality requirements for the bypass area is achieved due to a bioswale
downstream which has been previously sized for this development. See Drainage
Component #9 in the Off-Site analysis.
5. The bypass areas have been compensated for by decreasing the release from the
detention vault. Compensatory mitigation is provided by a detention vault so that
the net discharge at the point of convergence downstream is less than pre-
developed flows, even considering the uncontrolled discharge from the bypass
areas.
The road improvement detention vault is designed to handle the runoff from road
improvements in the North Access Road, and Talbot Road South. Since there are several
areas offsite which cannot be detained in this vault, a mitigation trade is proposed. The
road vault will also mitigate 0.059 acres of area from the Eastern corner of the MOB site.
There is approximately 0.279 acres of offsite area, runoff from which will bypass the facility.
However, an additional 0.33 acres of area from Talbot Rd. S. which is not being disturbed
will flow into the detention vault. The runoff from this area will be detained and treated
instead. The additional 0.051 acre area (0.33 - 0.279 ac) has been modelled as existing
impervious. These mitigation trade areas are designed according per section 1.2.3.2.G of
the 2017 RSWDM as follows:
1. The existing developed non-target surface area does have runoff characteristics
equivalent to those of the target surface area for which mitigation is being traded
and is not currently mitigated to the same flow control performance requirement
as the target surface area. The mitigated areas being treated area roadway similar
to those areas which bypass the facility.
2. Runoff from both the target surface area being traded and the flow control facility
converge before discharge from the Valley Medical Center.
3. The net effect in terms of flow control at the point of convergence downstream is
the same as without the mitigation trade due to sizing the vault for an equivalent
amount of area.
4. The un-detained runoff from the target surface area being traded does not create
a significant adverse impact to downstream drainage systems, salmonid habitat,
or properties prior to convergence with runoff from the flow control facility.
5. Consideration of an offsite area to be mitigated for must take into account the
likelihood of that area redeveloping in the future, and since this is a road
improvement project, it is unlikely that mitigation of these surfaces will be
provided in the future beyond this mitigation trade.
E. Water Quality System
The site is located in a Basic Water Quality Treatment Area, but the City of Renton has
indicated that it is required to choose a treatment option from the Enhanced Water Quality
Menu. The treatment option utilized for this project, Modular Wetlands from BioClean, have
received General Use Level Designation for Basic, Enhanced, and Phosphorus Water
Quality treatment capabilities through the Department of Ecology.
The following pages contain construction details of the proposed water quality facilities
used to treat runoff from both on-site pollution generating impervious surfaces (PGIS) and
from the road improvements. This section also shows the calculations and sizing
requirements that are being provided for this project by BioClean for the modular wetland
system.
No Low-Impact Development BMPs are feasible for this site per the Soils Engineer, who
determined that the on-site soils are not capable of infiltrating. Please refer to the soils
report in Section 6.0, SPECIAL REPORTS AND STUDIES.
F. Flow Control BMP Analysis and Design
The Geotechnical Engineer has prepared a report that indicates that the infiltration rate of
the soils at the site is less than 1/100th of a foot in a four-hour period, which makes many
of the required BMP's infeasible. See bullet list below for BMP selection process based
upon feasibility.
Full dispersion - This BMP is not feasible because there is no native vegetated surfaces
on site to disperse the required runoff from the target surfaces.
Full infiltration of roof runoff - This BMP is infeasible because the measured infiltration
rate is less than 0.3 inches per hour. See attached Addendum to Geotechnical Report
No. 1.
Full infiltration - This BMP is infeasible because the measured infiltration rate is less
than 0.3 inches per hour. See attached Addendum to Geotechnical Report No. 1.
Limited Infiltration - This BMP is infeasible because the measured infiltration rate is
less than 0.3 inches per hour. See attached Addendum to Geotechnical Report No. 1.
Bio-retention - This BMP is infeasible because the measured infiltration rate is less
than 0.3 inches per hour. See attached Addendum to Geotechnical Report No. 1.
Permeable Pavement - This BMP is infeasible because the measured infiltration rate
is less than 0.3 inches per hour.
Basic Dispersion - There is not sufficient vegetated areas on site to allow for the
vegetated flow-path lengths required for basic dispersion of the target surfaces.
Vegetated Roofs - There is a 0.123 AC vegetated roof on this site, which totals to
6.3% of the total site area. The roof will be waterproofed with appropriate materials
by the general contractor per the architectural plans. An underdrain system will be
provided in the form of three-dimensional, molded panels of recycled polyethylene
with drainage channels top and bottom sides and water retention reservoirs top side
(American Hydrotech, Inc. Gardendrain GR30). Gardenedge by American Hydrotech
will be supplemented by 8' leveling stripes where needed to provide soil containment.
The structural foundation has been verified to be capable of supporting the green
roof. The plant community on the green roof has been designed to withstand harsh
roof conditions by licensed Landscape Architects. The growing medium will be
composed of a 12-18" thick layer of American Hydrotech Intensive LiteTop Growing
Media, which has a saturated water capacity of ~40% which will provide sufficient
capacity to store 3" of water, allowing for full BMP credit. Thus, the vegetated roof
fulfills core requirement #9. See the following calculations for verification.
Reduced impervious surface credit: Not sought because Vegetated Roofs are all that
is required. However, these BMP options are also infeasible.
o Restricted footprint: This project requires a certain size building, 0.81 acre
in size. Therefore, there is no way to restrict the footprint.
o Wheel strip driveways: This project relies upon asphalt driveways to
access the site, not wheel strip driveways.
o Minimum disturbance foundation: The entire foundation of this building
will be disturbed under construction to the extent feasible.
o Open grid decking over pervious surface: Porous concrete will be the
means of providing a stable surface for the sidewalks. The owner of this
project does not intend to use open grid decking over previous surface.
Native growth retention credit: This project is not seeking credits for this BMP.
Tree Retention Credit: There are nine deciduous trees 6-12" in diameter, and seven
coniferous trees which will be retained on the site. However, this site is not seeking
this credit.
Establishing a minimum soil quality and depth: The soil amendment is not the same
as preservation of naturally occurring soil and vegetation. However, establishing a
minimum soil quality and depth will provide improved on-site management of storm
water flow and water quality. Therefore, minimum soil quality and depth must be
instituted on this project site, in accordance with the notes on the plans submitted
herewith.
Perforated pipe connection: Perforated pipe connection is considered infeasible, see
attached Addendum to Geotechnical Report No. 1.
Conclusion: It is up to interpretation of the vegetated roof sizing calculations in C.2.15.2 whether
or not this project fully satisfies the BMP requirements. Nevertheless, BMP's were utilized to the
Maximum extent feasible. All BMPs are infeasible for the road improvement project due to lack of
infiltration capacity or adequate vegetated area.
Green Roof BMP Calculations
The Green Roof will be supplied with American Hydrotech's Gardendrain GR 30, and a 12-14"
thick layer of American Hydrotech's Intensive Litetop growing media. The GR30 provides 0.05 ft3
of water storage per square foot. The Intensive Litetop growing media exhibits a saturated water
capacity of greater than 40%. See the following vegetated roof covering specifications sheet for
verification.
Given:
Water storage in underdrain = 0.05 ft3/ft2
12" thick growing medium w/ saturated water capacity >40%
0.123 acre green roof (see plans)
Find:
The provided water storage, and consequent amount of target surface mitigated by the
GreenRoof BMP.
Solution:
0.123 acre green roof * 12 in * |1 𝑐𝑟
12 𝑖𝑙|43560 𝑐𝑟2
𝑎𝑐𝑟𝑐|0.40 𝑖𝑙3 𝑟𝑎𝑟𝑐𝑟
𝑖𝑙3 𝑟𝑙𝑖𝑙| = 2143 ft3 water
The growing media will provide ~2100 cubic feet of water storage.
0.123 𝑎𝑐𝑟𝑒 𝑒𝑟𝑒𝑒𝑚𝑟𝑚𝑚𝑒∗|0.05 𝑐𝑟3 𝑟𝑎𝑟𝑐𝑟
𝑐𝑟2 𝑐𝑎𝑟𝑐𝑐𝑙 𝑐𝑟𝑎𝑖𝑙|∗|43560 𝑐𝑟2
𝑎𝑐𝑟𝑐| = 268 ft3 water
The garden drain will provide ~270 cubic feet of water storage.
The minimum storage volume required by the RSWDM is 3 inches. Since the target impervious
surfaces on-site are 0.196 acres, the minimum storage volume required for Vegetated Roof BMP is:
0.196 𝑎𝑐𝑟𝑒 𝑟𝑎𝑟𝑒𝑒𝑟 𝑖𝑚𝑚𝑒𝑟𝑟𝑖𝑚𝑟𝑟∗|3 𝑖𝑙 𝑟𝑎𝑟𝑐𝑟 𝑟𝑟𝑙𝑟𝑎𝑐𝑐
𝑎𝑐𝑟𝑐 𝑟𝑎𝑟𝑐𝑐𝑟 𝑖𝑙𝑙𝑐𝑟𝑟𝑖𝑙𝑟𝑟|∗|43560 𝑐𝑟2
𝑎𝑐𝑟𝑐|∗|𝑐𝑟
12 𝑖𝑙| = 2134 ft3 water
The growing media and garden drain will provide a total of 2100 cf + 270 cf = 2,370 cubic feet of
water storage. Although the surface area of the green roof is less than the area of target impervious
surfaces, the storage provided by the green roof is greater than the minimum storage required for
Vegetated Roof BMPs given the target impervious surface area on this site.
Detention Volume Required = 2,134 ft3
Detention Volume Provided = 2,370 ft3
Volume III – Hydrologic Analysis and Flow Control BMPs – December 2014
3-57
Riser Overflow. The nomograph in Figure 3.2.16 can be used to
determine the head (in feet) above a riser of given diameter and for a given
flow (usually the 100-year peak flow for developed conditions).
Figure 3.2.16 - Riser Inflow Curves
A 12" overflow riser with
0.5' of freeboard can
handle flows up to ~2.7
cfs, which is much greater
than the 100-year runoff
for any basin on this
project.
VEGETATIVE ROOF DETAIL
GREEN ROOF SPECIFICATIONS SHEET
Healthcare Realty Trust Section 073363
VMC Medical Office Building VEGETATED ROOF COVERING
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PART 1 - GENERAL
1.1 SUMMARY
A. Basis of Design: Membrane/green roof system, including Green Roof systems for
steep slopes and flat slopes. Refer to drawings for locations of 'level' and 'sloped'
roof assemblies.
1. Approved system manufacturers
a. American Hydrotech, Inc.
1.2 RELATED SECTIONS
A. Section 328000 — Landscape Irrigation
B. Section 329000 — Landscape Planting
1.3 REFERENCES
A. American Society for Testing and Materials (ASTM).
B. Underwriters Laboratories (UL) Class A.
C. ANSI/SPRI VR-1 2011 "Procedure for Investigating Resistance to Root Penetration
on Vegetative Roofs".
1.4 DEFINITIONS
A. Green Roof -- An area of planting/landscaping, built up on a waterproofed substrate
at any level that is separated from the natural ground by a man-made structure.
B. Steep Slope Green Roof -- Defined as a slope exceeding 3:12 pitch.
C. "C" Factor -- The runoff coefficient used in the Rational Method, "C" represents the
portion of the storm rainfall that becomes runoff.
D. Curve Number (CN) -- A number that is used with Natural Resource Conservation
Service (SCS) methods to convert rainfall depth into runoff volume. The Curve
Number takes into account a site's soil type, plant cover, impervious cover,
interception and surface storage.
1.5 SYSTEM DESCRIPTION
A. Furnish and install a completed green roof including protection course, root barrier
protection, drainage/water retention component, filter/drain fabric, lightweight
engineered growing medium and vegetation.
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B. Furnish and install a completed green roof system for steep slopes and flat slopes,
including protection course and root barrier protection, soil stabilization, growing
media confinement system, lightweight engineered growing media, and erosion
control mat.
1.6 SUBMITTALS
A. Certification showing full time quality control of production facilities responsible for
the manufacture of the rubberized asphalt and that each batch of material is tested
to insure conformance with the manufacturers published physical properties.
B. Certification showing that all components of the green roof assembly are being
supplied and warranted by a single-source manufacturer.
C. Evidence that the roof membrane assembly is currently Class A listed with
Underwriters Laboratories.
D. Provide product data on all components of the green roof assembly.
E. Evidence indicating that water is available at the roof level to ensure the vegetation
can receive sufficient moisture through proper maintenance of the green roof.
1.7 QUALITY ASSURANCE
A. The Green Roof Installing Contractor shall demonstrate qualifications to perform the
work of this Section by submitting the following documentation:
1. Certification or license by the green roof assembly supplier as a locally based,
authorized applicator of the products the installer intends to use, for a minimum
of five (5) years.
2. List of at least three (3) projects, satisfactorily completed within the past five (5)
years, of similar scope and complexity to this project. Previous experience
submittal shall correspond to specific membrane system proposed for use by
applicator.
B. The Green Roof Maintenance Contractor shall demonstrate qualifications to perform
the work of this Section by submitting the following documentation:
1. List of at least three (3) green roof projects, satisfactorily completed within the
past five (5) years, of similar scope and complexity to this project. Previous
experience submittal shall correspond to specific membrane system proposed for
use by applicator.
C. Green Roof Supplier shall show evidence that the specified green roof assembly has
been developed, marketed, supported and installed for a minimum of fifteen (15)
years on projects of similar complexity.
D. Growing Media Confinement System:
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1. Submit current product quality assurance test data and independent laboratory
test results indicating compliance with specified performance. No material shall
be considered as an equivalent to the GardenEdge® material unless it meets all
areas of this section without exception.
2. Growing media and growing media confinement system shall be supplied by
same manufacturer.
3. Green Roof Manufacturer will provide load calculations for growing media
confinement system. All structural load calculations for the growing media
confinement system shall be verified by the Project's structural engineer or
architect.
4. The attachment or anchoring of the growing media confinement system to the
building structure shall be designed and verified by the Project's structural
engineer as adequate for the application.
E. Green roof supplier shall provide data and calculations, specific to the products
being submitted, that verify the green roof assembly specified meets the project
criteria for storm water runoff volume and rate control.
1. Calculations shall be based on actual testing of supplier's green roof components
to be used for the project including but not limited to the regionally specific
growing media formulation and water retention/drainage materials.
2. Calculations shall account for vegetated and un-vegetated portions of the roof as
well as local climatic conditions including rainfall depth, intensity, duration, and
timing.
F. Green roof supplier shall provide data demonstrating that the composite C-factor
and Curve Number parameters for the specified green roof assembly are less than
or equal to those factors used in the engineering design and analysis for the projects
drainage and storm water systems analysis.
G. Pre-Construction Conferences. The manufacturer shall meet with the necessary
parties at the jobsite to review and discuss project conditions as it relates to the
integrity of the roofing assembly.
1.8 DELIVERY, STORAGE AND HANDLING
A. Deliver materials in original unopened containers of packaging clearly labeled with
manufacturer's name, brand name, instruction for use, all identifying numbers, and
U.L. labels.
B. Materials shall be stored in a neat, safe manner, not to exceed the allowable
structural capacity of the storage area.
C. Store materials in a clean, dry area protected from water and direct sunlight.
1.9 WARRANTY
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A. Upon completion of the work, the contractor shall supply the owner with a warranty
of U.S. origin direct from the manufacturer.
PART 2 - PRODUCTS
2.1 MATERIALS
A. Air Layer
1. Required air space over insulation when moisture mat is required shall be
composed of a crush-proof core and non-woven filter fabric similar to the
following
a. American Hydrotech, Inc. Hydrodrain 300
B. Drainage/Water Retention Component
1. Three-dimensional, molded panels of recycled polyethylene with drainage
channels top and bottom sides and water retention reservoirs top side shall meet
the following physical properties.
a. American Hydrotech, Inc. Gardendrain GR30
C. Filter Fabric
1. Non-woven, needle punched, geotextile filter sheet, made of non-rotting,
polypropylene fibers. It is made to be highly resistant to all natural acids and
alkalis and is chemically neutral.
a. American Hydrotech, Inc. Systemfilter
D. Drainage/Soil Confinement Components
1. Extruded aluminum perforated to allow water flow as shown on plans and details.
a. Strip sheet heights available: 8.5 inches
b. Additional leveling strips: 8.0 inches
c. Strip sheet thickness: 0.1 inch
d. Various accessories: corner sections, clips and connection bolts.
E. Growing Media
1. Custom growing media mix capable of supporting vigorous growth of the
specified vegetation, complying with the following specification.
a. American Hydrotech Intensive LiteTop Growing Media
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2. Expanded lightweight aggregate for use as fill material for drainage/water
retention component as required.
- Lightweight Aggregate
a. 5/16" - 3/8" expanded, lightweight aggregate
F. Vegetation/Plantings
1. Refer to Section 329000.
G. Miscellaneous
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1. Inspection Chambers: Aluminum and stainless steel over drain chambers
perforated to allow water flow as shown on manufacturer's standard plans and
details.
2.2 RELATED MATERIALS
A. Intensive plant materials and shall be as shown on plans.
B. Metal counterflashing is typically required to provide protection to vulnerable flashing
materials from damage due to gardening activities.
PART 3 - EXECUTION
3.1 INSPECTION
A. The roofing contractor shall not proceed with the installation of the roof membrane
assembly until all roof defects have been corrected.
3.2 PREPARATION
A. All surfaces shall be dry, smooth, free of depressions, voids, protrusions, clean and
free of unapproved curing compounds, form release agents and other surface
contaminants.
3.3 GREEN ROOF COMPONENTS INSTALLATION
A. All garden roof components shall be installed per manufacturer's requirements.
B. Air Layer: When insulation are specified an air layer shall be required between the
surface of the insulation and the water retention mat. A layer of Hydrodrain 300 shall
be installed over the insulation. The 4 inch (100 mm) salvage edge of the geotextile
fabric overlaps adjoining sheets and can be held in place with duct tape.
C. Drainage/Water Retention Component. Gardendrain GR30 shall be installed with
holes up, over the air layer. Adjacent panels shall be butt together. Gardendrain
shall be cut to fit around penetrations, etc. with a heavy-duty utility knife or small
toothed saw.
D. Filter fabric. A layer of Systemfilter shall be laid over the Gardendrain, lapping
adjacent rolls a minimum of 12 inches (300 mm). Enough material shall be left to be
drawn up above the anticipated growing media level. Any excess shall be trimmed
down to the level of the growing media.
E. Manufacturer's growing media confinement system installation guidelines and
standard details shall be strictly followed.
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3.4 HARDSCAPE/ACCESSORY INSTALLATION
A. Metal edge restraints, curbing and all specified edging materials shall be installed as
shown on plans and details.
B. All drains shall be fitted with inspection chambers built up to with the proper number
of extensions to ensure access at top of growing media level and as shown on the
manufacturers standard plans and details for the installation type.
3.5 GROWING MEDIA INSTALLATION
A. Growing media shall be placed carefully once the drainage/growing media
confinement components are in place and all anchoring work is complete.
B. Growing media shall be placed carefully to avoid damage or displacement of other
materials such as walls, paving, drainage components, filter fabric and roofing
membrane.
C. Growing media shall be placed 1"-2" over the top of the drainage/soil confinement
component and lightly tamped, rolled or water jetted to leave the growing media a
minimum of 1/2" over the top.
D. Erosion Control Mat.
1. The erosion control mat shall be installed directly over the growing media and
properly staked into place.
a. Stake fastening pattern is based on local wind speed, building height
and roof.
3.6 VEGETATION INSTALLATION
A. Vegetation planting shall be installed in accordance with the manufacturer's
recommendations for a seeded grass installation and per Section 329200.
B. Plant materials shall not be installed between the fall frost date and the following
spring frost date as identified in Section 329200.
3.7 VEGETATION MAINTENANCE
A. Contractor/Installer shall maintain plantings in accordance with the Hydrotech
Extensive Garden Roof Plant Installation and Maintenance Guideline. Contact
Hydrotech for specific maintenance requirements.
B. Maintenance activities shall include, but are not limited to, the following:
1. Periodic on-roof monitoring of vegetation
2. Watering to maintain proper growing media moisture content (especially during
periods of hot and dry weather)
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3. Weeding to remove unwanted vegetation from planted areas and vegetation free
zones.
4. Removal of debris
5. Reporting and photo-documentation of progress of vegetation during
maintenance and warranty period.
C. Maintenance shall begin immediately after vegetation installation and shall continue
for three months after the date of substantial completion of the entire project, per the
requirements of Section 329200.
END OF SECTION 328000
ADDENDUM TO GEOTECHNICAL REPORT NO. 1
8410 154th Avenue NE
Redmond, Washington 98052
425.861.6000
June 5, 2017
Valley Medical Center
400 South 43rd Street
Renton, Washington 98005
Attention: Becky Hardi
Subject: Addendum to Geotechnical Report No. 1
Valley Medical Center – Medical Office Building
400 South 43rd Street
Renton, Washington
GeoEngineers File No. 2202-024-00
INTRODUCTION
The purpose of this letter is to provide updated recommendations regarding stormwater infiltration in
accordance with the 2017 City of Renton Stormwater Design Manual (2017 RSWDM). This letter is being
submitted as Addendum No. 1 to our geotechnical report dated September 16, 2016, and is subject to the
limitations described therein.
GeoEngineers, Inc. (GeoEngineers) previously provided geotechnical engineering design for the project,
which included an infiltration evaluation in accordance with the 2009 King County Stormwater Design
Manual (2009 KCSWDM), the results of which were presented in our geotechnical report dated
September 16, 2016. More recently, we provided additional services in an infiltration letter, documenting
the results of pilot infiltration testing (PITs), on December 20, 2016, in accordance with the 2014
Stormwater Management Manual for Western Washington (2014 SWMMWW).
Our project understanding is based on discussions with the project architect (NBBJ), civil engineer
(Barghausen Consulting Engineers), and representatives of Valley Medical Center. We understand that a
large below-grade vault is planned to manage the stormwater for the new Medical Office Building (MOB).
The City of Renton’s Hearing Examiner issued a Final Decision dated April 5, 2017 for the Valley Medical
Center MOB project, and as part of that decision it requires that the project team provide a more robust
infiltration evaluation of the Best Management Practices (BMPs) that are provided in the 2017 Renton
Storm Water Design Manual (RSWDM).
Valley Medical Center. | June 5, 2017 Page 2
File No. 2202-024-00
CONCLUSIONS AND RECOMMENDATIONS
Infiltration
Subsurface explorations described in our geotechnical report dated September 16, 2016 and in our
infiltration letter dated December 20, 2016 consist of four geotechnical borings, depths ranging from 15½
to 35¾ feet below the ground surface (bgs) and four test pits, depths ranging from 3 to 4 feet bgs. Small
scale PITs were conducted in two of the test pits.
Based on these explorations, our evaluation of the feasibility of the infiltrative Best Management Practices
(BMPs) is described below per the requirements of the 2017 RSWDM:
■ Full Infiltration is considered infeasible because the existing soils consist of fill, glacially
consolidated soils, and bedrock. These soils have a low infiltration rate which is shown in the results
of our PITs for the project. These soils are considered impractical for infiltration due to the low
infiltration rate.
■ Limited Infiltration is considered infeasible because the existing soils consist of fill, glacially
consolidated soils, and bedrock. These soils have a low infiltration rate which is shown in the results
of our PITs for the project. These soils are considered impractical for infiltration due to the low
infiltration rate.
■ Bioretention is considered infeasible because the existing soils do not meet the minimum design
requirement for infiltration rate. The measured infiltration rate is less than 0.30 inches per hour,
as described in our infiltration letter dated December 20, 2016.
■ Permeable Pavement is considered infeasible because the existing soils do not meet the minimum
design requirement for infiltration rate. The measured infiltration rate is less than 0.30 inches per
hour, as described in our infiltration letter dated December 20, 2016.
■ Perforated Pipe Connection is considered infeasible because the existing soils do not meet the
minimum design requirement for infiltration rate. The measured infiltration rate is less than
0.30 inches per hour, as described in our infiltration letter dated December 20, 2016.
■ Rain Gardens are considered infeasible because the existing soils do not meet the minimum
design requirement for infiltration rate. The measured infiltration rate is less than 0.30 inches per
hour, as described in our infiltration letter dated December 20, 2016.
LIMITATIONS
We have prepared this letter for Valley Medical Center and members of the design team for use in design
of the Valley Medical Center MOB project in Renton, Washington. The data should be provided to
prospective contractors for their bidding and estimating purposes, but our report and interpretations should
not be construed as a warranty of the subsurface conditions.
Within the limitations of scope, schedule and budget, our services have been executed in accordance with
generally accepted practices in the field of geotechnical engineering in this area at the time this report was
prepared. No warranty or other conditions, express or implied, should be understood.
SITE DETENTION VAULT BYPASS AREA
RUNOFF CALCULATIONS
WWHM2012
PROJECT REPORT
MOB Site Detention Vault
Bypass Area
01/15/2017
18092-Road with Bypass 1/15/2018 11:41:48 AM Page 2
General Model Information
Project Name:18092-Road with Bypass
Site Name:Road Vault
Site Address:MOB
City:Renton
Report Date:1/15/2018
Gage:Seatac
Data Start:1948/10/01
Data End:2009/09/30
Timestep:15 Minute
Precip Scale:1.000
Version Date:2017/04/14
Version:4.2.13
POC Thresholds
Low Flow Threshold for POC1:50 Percent of the 2 Year
High Flow Threshold for POC1:50 Year
18092-Road with Bypass 1/15/2018 11:41:48 AM Page 3
Landuse Basin Data
Predeveloped Land Use
Basin 1
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Forest, Flat 0.058
Pervious Total 0.058
Impervious Land Use acre
Impervious Total 0
Basin Total 0.058
Element Flows To:
Surface Interflow Groundwater
18092-Road with Bypass 1/15/2018 11:41:48 AM Page 4
Mitigated Land Use
Basin 1
Bypass:No
GroundWater:No
Pervious Land Use acre
Pervious Total 0
Impervious Land Use acre
ROADS FLAT 0.058
Impervious Total 0.058
Basin Total 0.058
Element Flows To:
Surface Interflow Groundwater
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Analysis Results
POC 1
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #1
Total Pervious Area:0.058
Total Impervious Area:0
Mitigated Landuse Totals for POC #1
Total Pervious Area:0
Total Impervious Area:0.058
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.001705
5 year 0.002678
10 year 0.00323
25 year 0.003814
50 year 0.004175
100 year 0.004483
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.022113
5 year 0.027932
10 year 0.031885
25 year 0.037013
50 year 0.040938
100 year 0.044958
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.002 0.029
1950 0.002 0.031
1951 0.004 0.018
1952 0.001 0.016
1953 0.001 0.017
1954 0.001 0.018
1955 0.002 0.020
1956 0.002 0.020
1957 0.002 0.023
1958 0.002 0.018
18092-Road with Bypass 1/15/2018 11:42:21 AM Page 8
1959 0.001 0.019
1960 0.003 0.018
1961 0.001 0.019
1962 0.001 0.017
1963 0.001 0.019
1964 0.002 0.018
1965 0.001 0.023
1966 0.001 0.016
1967 0.002 0.027
1968 0.001 0.031
1969 0.001 0.021
1970 0.001 0.021
1971 0.001 0.025
1972 0.003 0.025
1973 0.001 0.015
1974 0.001 0.022
1975 0.002 0.026
1976 0.001 0.017
1977 0.000 0.019
1978 0.001 0.023
1979 0.001 0.031
1980 0.003 0.028
1981 0.001 0.023
1982 0.002 0.033
1983 0.002 0.027
1984 0.001 0.017
1985 0.001 0.023
1986 0.003 0.020
1987 0.003 0.031
1988 0.001 0.019
1989 0.001 0.023
1990 0.005 0.039
1991 0.003 0.031
1992 0.001 0.017
1993 0.001 0.014
1994 0.000 0.016
1995 0.002 0.020
1996 0.004 0.022
1997 0.003 0.021
1998 0.001 0.021
1999 0.003 0.044
2000 0.001 0.022
2001 0.000 0.024
2002 0.001 0.028
2003 0.002 0.022
2004 0.002 0.041
2005 0.002 0.019
2006 0.002 0.017
2007 0.004 0.038
2008 0.005 0.031
2009 0.003 0.029
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.0055 0.0439
2 0.0052 0.0411
3 0.0041 0.0394
18092-Road with Bypass 1/15/2018 11:42:21 AM Page 9
4 0.0040 0.0384
5 0.0038 0.0326
6 0.0033 0.0315
7 0.0033 0.0315
8 0.0031 0.0309
9 0.0030 0.0309
10 0.0028 0.0308
11 0.0027 0.0307
12 0.0026 0.0286
13 0.0026 0.0286
14 0.0025 0.0282
15 0.0024 0.0280
16 0.0023 0.0270
17 0.0023 0.0265
18 0.0021 0.0258
19 0.0020 0.0254
20 0.0020 0.0246
21 0.0019 0.0240
22 0.0019 0.0234
23 0.0019 0.0234
24 0.0018 0.0231
25 0.0018 0.0231
26 0.0017 0.0230
27 0.0017 0.0228
28 0.0017 0.0224
29 0.0016 0.0219
30 0.0015 0.0218
31 0.0015 0.0218
32 0.0015 0.0215
33 0.0014 0.0214
34 0.0014 0.0212
35 0.0014 0.0206
36 0.0014 0.0205
37 0.0014 0.0204
38 0.0014 0.0201
39 0.0013 0.0200
40 0.0013 0.0194
41 0.0013 0.0188
42 0.0013 0.0188
43 0.0012 0.0188
44 0.0012 0.0187
45 0.0012 0.0187
46 0.0012 0.0185
47 0.0012 0.0184
48 0.0012 0.0184
49 0.0011 0.0180
50 0.0011 0.0179
51 0.0011 0.0174
52 0.0010 0.0172
53 0.0010 0.0169
54 0.0009 0.0167
55 0.0008 0.0166
56 0.0007 0.0166
57 0.0007 0.0159
58 0.0007 0.0157
59 0.0004 0.0156
60 0.0002 0.0154
61 0.0002 0.0143
WWHM2012
PROJECT REPORT
MOB Roof Detention Vault
09/27/2017
roof detention 09-14-17 9/18/2017 11:53:23 AM Page 2
General Model Information
Project Name:roof detention 09-14-17
Site Name:
Site Address:180th/ Talbot
City:Renton
Report Date:9/18/2017
Gage:Seatac
Data Start:1948/10/01
Data End:2009/09/30
Timestep:15 Minute
Precip Scale:1.000
Version Date:2017/04/14
Version:4.2.13
POC Thresholds
Low Flow Threshold for POC1:50 Percent of the 2 Year
High Flow Threshold for POC1:50 Year
roof detention 09-14-17 9/18/2017 11:53:23 AM Page 3
Landuse Basin Data
Predeveloped Land Use
Basin 1
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Forest, Flat 0.844
Pervious Total 0.844
Impervious Land Use acre
Impervious Total 0
Basin Total 0.844
Element Flows To:
Surface Interflow Groundwater
roof detention 09-14-17 9/18/2017 11:53:23 AM Page 4
Mitigated Land Use
.1
Bypass:No
GroundWater:No
Pervious Land Use acre
A B, Pasture, Flat 0.0615
Pervious Total 0.0615
Impervious Land Use acre
ROOF TOPS FLAT 0.7825
Impervious Total 0.7825
Basin Total 0.844
Element Flows To:
Surface Interflow Groundwater
Vault 1 Vault 1
roof detention 09-14-17 9/18/2017 11:53:23 AM Page 6
Mitigated Routing
Vault 1
Width:20 ft.
Length:124 ft.
Depth:8 ft.
Discharge Structure
Riser Height:7 ft.
Riser Diameter:12 in.
Orifice 1 Diameter:0.5 in.Elevation:0 ft.
Orifice 2 Diameter:0.6875 in.Elevation:4.21 ft.
Orifice 3 Diameter:0.5 in.Elevation:4.79 ft.
Element Flows To:
Outlet 1 Outlet 2
Vault Hydraulic Table
Stage(feet)Area(ac.)Volume(ac-ft.)Discharge(cfs)Infilt(cfs)
0.0000 0.056 0.000 0.000 0.000
0.0889 0.056 0.005 0.002 0.000
0.1778 0.056 0.010 0.002 0.000
0.2667 0.056 0.015 0.003 0.000
0.3556 0.056 0.020 0.004 0.000
0.4444 0.056 0.025 0.004 0.000
0.5333 0.056 0.030 0.005 0.000
0.6222 0.056 0.035 0.005 0.000
0.7111 0.056 0.040 0.005 0.000
0.8000 0.056 0.045 0.006 0.000
0.8889 0.056 0.050 0.006 0.000
0.9778 0.056 0.055 0.006 0.000
1.0667 0.056 0.060 0.007 0.000
1.1556 0.056 0.065 0.007 0.000
1.2444 0.056 0.070 0.007 0.000
1.3333 0.056 0.075 0.007 0.000
1.4222 0.056 0.081 0.008 0.000
1.5111 0.056 0.086 0.008 0.000
1.6000 0.056 0.091 0.008 0.000
1.6889 0.056 0.096 0.008 0.000
1.7778 0.056 0.101 0.009 0.000
1.8667 0.056 0.106 0.009 0.000
1.9556 0.056 0.111 0.009 0.000
2.0444 0.056 0.116 0.009 0.000
2.1333 0.056 0.121 0.009 0.000
2.2222 0.056 0.126 0.010 0.000
2.3111 0.056 0.131 0.010 0.000
2.4000 0.056 0.136 0.010 0.000
2.4889 0.056 0.141 0.010 0.000
2.5778 0.056 0.146 0.010 0.000
2.6667 0.056 0.151 0.011 0.000
2.7556 0.056 0.156 0.011 0.000
2.8444 0.056 0.161 0.011 0.000
2.9333 0.056 0.167 0.011 0.000
3.0222 0.056 0.172 0.011 0.000
3.1111 0.056 0.177 0.012 0.000
3.2000 0.056 0.182 0.012 0.000
3.2889 0.056 0.187 0.012 0.000
roof detention 09-14-17 9/18/2017 11:53:23 AM Page 7
3.3778 0.056 0.192 0.012 0.000
3.4667 0.056 0.197 0.012 0.000
3.5556 0.056 0.202 0.012 0.000
3.6444 0.056 0.207 0.013 0.000
3.7333 0.056 0.212 0.013 0.000
3.8222 0.056 0.217 0.013 0.000
3.9111 0.056 0.222 0.013 0.000
4.0000 0.056 0.227 0.013 0.000
4.0889 0.056 0.232 0.013 0.000
4.1778 0.056 0.237 0.013 0.000
4.2667 0.056 0.242 0.017 0.000
4.3556 0.056 0.248 0.019 0.000
4.4444 0.056 0.253 0.020 0.000
4.5333 0.056 0.258 0.021 0.000
4.6222 0.056 0.263 0.022 0.000
4.7111 0.056 0.268 0.023 0.000
4.8000 0.056 0.273 0.025 0.000
4.8889 0.056 0.278 0.027 0.000
4.9778 0.056 0.283 0.029 0.000
5.0667 0.056 0.288 0.030 0.000
5.1556 0.056 0.293 0.032 0.000
5.2444 0.056 0.298 0.033 0.000
5.3333 0.056 0.303 0.034 0.000
5.4222 0.056 0.308 0.035 0.000
5.5111 0.056 0.313 0.036 0.000
5.6000 0.056 0.318 0.037 0.000
5.6889 0.056 0.323 0.038 0.000
5.7778 0.056 0.328 0.039 0.000
5.8667 0.056 0.334 0.040 0.000
5.9556 0.056 0.339 0.040 0.000
6.0444 0.056 0.344 0.041 0.000
6.1333 0.056 0.349 0.042 0.000
6.2222 0.056 0.354 0.043 0.000
6.3111 0.056 0.359 0.044 0.000
6.4000 0.056 0.364 0.044 0.000
6.4889 0.056 0.369 0.045 0.000
6.5778 0.056 0.374 0.046 0.000
6.6667 0.056 0.379 0.046 0.000
6.7556 0.056 0.384 0.047 0.000
6.8444 0.056 0.389 0.048 0.000
6.9333 0.056 0.394 0.049 0.000
7.0222 0.056 0.399 0.084 0.000
7.1111 0.056 0.404 0.440 0.000
7.2000 0.056 0.409 0.958 0.000
7.2889 0.056 0.415 1.499 0.000
7.3778 0.056 0.420 1.931 0.000
7.4667 0.056 0.425 2.191 0.000
7.5556 0.056 0.430 2.401 0.000
7.6444 0.056 0.435 2.582 0.000
7.7333 0.056 0.440 2.751 0.000
7.8222 0.056 0.445 2.911 0.000
7.9111 0.056 0.450 3.062 0.000
8.0000 0.056 0.455 3.205 0.000
8.0889 0.056 0.460 3.343 0.000
8.1778 0.000 0.000 3.475 0.000
roof detention 09-14-17 9/18/2017 11:53:23 AM Page 8
Analysis Results
POC 1
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #1
Total Pervious Area:0.844
Total Impervious Area:0
Mitigated Landuse Totals for POC #1
Total Pervious Area:0.0615
Total Impervious Area:0.7825
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.024814
5 year 0.038972
10 year 0.046995
25 year 0.055495
50 year 0.060755
100 year 0.065229
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.014653
5 year 0.022097
10 year 0.028139
25 year 0.037192
50 year 0.045068
100 year 0.054003
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.024 0.011
1950 0.030 0.013
1951 0.055 0.037
1952 0.017 0.010
1953 0.014 0.013
1954 0.021 0.012
1955 0.034 0.012
1956 0.027 0.021
1957 0.022 0.012
1958 0.025 0.012
Developed, Un-Mitigated Flows
roof detention 09-14-17 9/18/2017 11:53:55 AM Page 9
1959 0.021 0.011
1960 0.037 0.030
1961 0.021 0.014
1962 0.013 0.010
1963 0.018 0.012
1964 0.023 0.013
1965 0.017 0.018
1966 0.016 0.012
1967 0.034 0.013
1968 0.021 0.012
1969 0.021 0.011
1970 0.017 0.012
1971 0.018 0.012
1972 0.041 0.030
1973 0.018 0.018
1974 0.020 0.012
1975 0.027 0.011
1976 0.020 0.012
1977 0.002 0.011
1978 0.017 0.013
1979 0.010 0.009
1980 0.039 0.034
1981 0.015 0.012
1982 0.030 0.024
1983 0.027 0.012
1984 0.016 0.010
1985 0.010 0.011
1986 0.043 0.013
1987 0.038 0.027
1988 0.015 0.011
1989 0.010 0.011
1990 0.080 0.029
1991 0.048 0.031
1992 0.018 0.013
1993 0.019 0.010
1994 0.006 0.009
1995 0.028 0.014
1996 0.058 0.035
1997 0.049 0.037
1998 0.011 0.010
1999 0.046 0.031
2000 0.019 0.013
2001 0.003 0.009
2002 0.021 0.014
2003 0.027 0.012
2004 0.035 0.040
2005 0.025 0.012
2006 0.029 0.022
2007 0.059 0.045
2008 0.076 0.034
2009 0.037 0.017
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.0795 0.0451
2 0.0762 0.0395
3 0.0590 0.0369
roof detention 09-14-17 9/18/2017 11:53:55 AM Page 10
4 0.0581 0.0369
5 0.0546 0.0353
6 0.0486 0.0340
7 0.0479 0.0339
8 0.0456 0.0315
9 0.0430 0.0305
10 0.0407 0.0305
11 0.0386 0.0300
12 0.0380 0.0286
13 0.0374 0.0273
14 0.0369 0.0243
15 0.0347 0.0220
16 0.0341 0.0214
17 0.0337 0.0180
18 0.0304 0.0175
19 0.0296 0.0175
20 0.0294 0.0138
21 0.0276 0.0135
22 0.0272 0.0135
23 0.0271 0.0134
24 0.0268 0.0133
25 0.0266 0.0133
26 0.0249 0.0131
27 0.0247 0.0128
28 0.0244 0.0128
29 0.0234 0.0127
30 0.0219 0.0126
31 0.0214 0.0125
32 0.0212 0.0124
33 0.0210 0.0124
34 0.0210 0.0123
35 0.0208 0.0120
36 0.0206 0.0120
37 0.0201 0.0119
38 0.0197 0.0119
39 0.0192 0.0119
40 0.0192 0.0119
41 0.0185 0.0118
42 0.0185 0.0116
43 0.0182 0.0116
44 0.0178 0.0116
45 0.0172 0.0115
46 0.0172 0.0115
47 0.0170 0.0115
48 0.0168 0.0113
49 0.0164 0.0111
50 0.0161 0.0108
51 0.0154 0.0108
52 0.0150 0.0108
53 0.0139 0.0107
54 0.0130 0.0102
55 0.0110 0.0101
56 0.0104 0.0100
57 0.0098 0.0100
58 0.0097 0.0097
59 0.0065 0.0093
60 0.0034 0.0091
61 0.0023 0.0089
roof detention 09-14-17 9/18/2017 11:53:55 AM Page 12
Duration Flows
The Facility PASSED
Flow(cfs)Predev Mit Percentage Pass/Fail
0.0124 17575 16072 91 Pass
0.0129 16170 10940 67 Pass
0.0134 14970 7174 47 Pass
0.0139 13854 4485 32 Pass
0.0144 12810 4353 33 Pass
0.0148 11822 4235 35 Pass
0.0153 10904 4128 37 Pass
0.0158 10123 4019 39 Pass
0.0163 9388 3921 41 Pass
0.0168 8731 3824 43 Pass
0.0173 8143 3709 45 Pass
0.0178 7602 3561 46 Pass
0.0183 7069 3407 48 Pass
0.0188 6592 3275 49 Pass
0.0192 6149 3125 50 Pass
0.0197 5777 2939 50 Pass
0.0202 5431 2808 51 Pass
0.0207 5103 2667 52 Pass
0.0212 4808 2541 52 Pass
0.0217 4528 2408 53 Pass
0.0222 4254 2257 53 Pass
0.0227 4017 2102 52 Pass
0.0232 3782 1938 51 Pass
0.0236 3551 1779 50 Pass
0.0241 3339 1658 49 Pass
0.0246 3138 1557 49 Pass
0.0251 2952 1467 49 Pass
0.0256 2785 1402 50 Pass
0.0261 2597 1345 51 Pass
0.0266 2449 1283 52 Pass
0.0271 2308 1215 52 Pass
0.0275 2162 1154 53 Pass
0.0280 2026 1093 53 Pass
0.0285 1898 1017 53 Pass
0.0290 1790 928 51 Pass
0.0295 1689 860 50 Pass
0.0300 1590 783 49 Pass
0.0305 1483 715 48 Pass
0.0310 1381 662 47 Pass
0.0315 1292 592 45 Pass
0.0319 1217 548 45 Pass
0.0324 1155 507 43 Pass
0.0329 1098 462 42 Pass
0.0334 1048 418 39 Pass
0.0339 997 351 35 Pass
0.0344 930 323 34 Pass
0.0349 883 299 33 Pass
0.0354 837 271 32 Pass
0.0358 789 251 31 Pass
0.0363 743 231 31 Pass
0.0368 713 206 28 Pass
0.0373 668 185 27 Pass
0.0378 630 173 27 Pass
roof detention 09-14-17 9/18/2017 11:53:55 AM Page 13
0.0383 595 158 26 Pass
0.0388 566 146 25 Pass
0.0393 539 129 23 Pass
0.0398 497 115 23 Pass
0.0402 473 111 23 Pass
0.0407 434 106 24 Pass
0.0412 399 100 25 Pass
0.0417 367 82 22 Pass
0.0422 348 65 18 Pass
0.0427 323 57 17 Pass
0.0432 296 49 16 Pass
0.0437 272 42 15 Pass
0.0442 256 36 14 Pass
0.0446 235 28 11 Pass
0.0451 217 3 1 Pass
0.0456 195 0 0 Pass
0.0461 180 0 0 Pass
0.0466 158 0 0 Pass
0.0471 145 0 0 Pass
0.0476 129 0 0 Pass
0.0481 119 0 0 Pass
0.0485 109 0 0 Pass
0.0490 97 0 0 Pass
0.0495 91 0 0 Pass
0.0500 82 0 0 Pass
0.0505 76 0 0 Pass
0.0510 69 0 0 Pass
0.0515 61 0 0 Pass
0.0520 54 0 0 Pass
0.0525 48 0 0 Pass
0.0529 41 0 0 Pass
0.0534 38 0 0 Pass
0.0539 33 0 0 Pass
0.0544 27 0 0 Pass
0.0549 22 0 0 Pass
0.0554 21 0 0 Pass
0.0559 20 0 0 Pass
0.0564 19 0 0 Pass
0.0568 17 0 0 Pass
0.0573 14 0 0 Pass
0.0578 12 0 0 Pass
0.0583 8 0 0 Pass
0.0588 4 0 0 Pass
0.0593 3 0 0 Pass
0.0598 3 0 0 Pass
0.0603 3 0 0 Pass
0.0608 3 0 0 Pass
DEVELOPED BASIN MAP
WWWWWWWWWWWWWWSDSDWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWSDSDWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWNEW SDMH #4 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #1 TYPE 1,W/ VANED GRATENEW SDMH #1 TYPE 2-60"W/ SOLID LOCKING LIDNEW CB #2 TYPE 1,W/ SOLID LOCKING LIDFOOTING DRAIN CO #1EX. CB #570 TYPE 1,W/STANDARD GRATEMODULAR WETLAND #1NEW CB #5 TYPE 1,W/ VANED GRATEEX. CB TYPE 2-72"w/ SOLID LOCKING LIDEX. CB TYPE 2-54"w/ SOLID LOCKING LIDNEW CB #4 TYPE 1,W/HERRINGBONE GRATEROOF DRAIN CO #1ROOF DRAIN CO #4ROOF DRAIN CO #5NEW SDMH #2 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #7 TYPE 1,W/ SOLID LOCKING LIDNEW SDMH #3 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #3 TYPE 1,W/ SOLID LOCKING LIDNEW CB #8 TYPE 2-48"W/ VANED GRATEINSTALL RISER TEEDETAIL PER SHEET C23NEW SDMH #7 TYPE 2-48"W/ SOLID LOCKING LIDNEW SDMH #6 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #9NEW CB #10 TYPE 1,W/ SOLID LOCKING LIDNEW CB #11 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #2ROOF DRAIN CO #3EX. CB #569 TYPE 1,W/ NEW SOLID LOCKING LIDROOF DRAIN CO #6UW MEDICINE - VALLEY MEDICAL CENTERMEDICAL OFFICE BUILDING EXPANSIONIN COMPLIANCE WITH CITY OF RENTON STANDARDS
ROOF DETENTION VAULT DETAIL
UW MEDICINE - VALLEY MEDICAL CENTER
MEDICAL OFFICE BUILDING EXPANSION
IN COMPLIANCE WITH CITY OF RENTON STANDARDS
WWHM2012
PROJECT REPORT
MOB Site Detention Vault
12/21/2017
18092-Site Vault no Bypass 12/20/2017 5:23:13 PM Page 2
General Model Information
Project Name:18092-Site Vault no Bypass
Site Name:Site Vault
Site Address:MOB
City:Renton
Report Date:12/20/2017
Gage:Seatac
Data Start:1948/10/01
Data End:2009/09/30
Timestep:15 Minute
Precip Scale:1.167
Version Date:2017/04/14
Version:4.2.13
POC Thresholds
Low Flow Threshold for POC1:50 Percent of the 2 Year
High Flow Threshold for POC1:50 Year
(Reduced Bypass)
18092-Site Vault no Bypass 12/20/2017 5:23:13 PM Page 3
Landuse Basin Data
Predeveloped Land Use
Basin 1
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Forest, Flat 0.938
Pervious Total 0.938
Impervious Land Use acre
PARKING FLAT 0.055
Impervious Total 0.055
Basin Total 0.993
Element Flows To:
Surface Interflow Groundwater
18092-Site Vault no Bypass 12/20/2017 5:23:13 PM Page 4
Bypass Area #1
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Forest, Flat 0.058
Pervious Total 0.058
Impervious Land Use acre
Impervious Total 0
Basin Total 0.058
Element Flows To:
Surface Interflow Groundwater
18092-Site Vault no Bypass 12/20/2017 5:23:13 PM Page 5
Mitigated Land Use
Basin 1
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Flat 0.142
Pervious Total 0.142
Impervious Land Use acre
PARKING FLAT 0.851
Impervious Total 0.851
Basin Total 0.993
Element Flows To:
Surface Interflow Groundwater
Vault 1 Vault 1
18092-Site Vault no Bypass 12/20/2017 5:23:13 PM Page 6
Basin 2
Bypass:Yes
GroundWater:No
Pervious Land Use acre
C, Lawn, Flat 0.016
Pervious Total 0.016
Impervious Land Use acre
PARKING FLAT 0.042
Impervious Total 0.042
Basin Total 0.058
Element Flows To:
Surface Interflow Groundwater
18092-Site Vault no Bypass 12/20/2017 5:23:13 PM Page 8
Mitigated Routing
Vault 1
Width:21 ft.
Length:136 ft.
Depth:8.8 ft.
Discharge Structure
Riser Height:7.8 ft.
Riser Diameter:12 in.
Orifice 1 Diameter:0.5 in.Elevation:0 ft.
Orifice 2 Diameter:0.625 in.Elevation:5 ft.
Orifice 3 Diameter:0.5 in.Elevation:6 ft.
Element Flows To:
Outlet 1 Outlet 2
Vault Hydraulic Table
Stage(feet)Area(ac.)Volume(ac-ft.)Discharge(cfs)Infilt(cfs)
0.0000 0.065 0.000 0.000 0.000
0.0978 0.065 0.006 0.002 0.000
0.1956 0.065 0.012 0.003 0.000
0.2933 0.065 0.019 0.003 0.000
0.3911 0.065 0.025 0.004 0.000
0.4889 0.065 0.032 0.004 0.000
0.5867 0.065 0.038 0.005 0.000
0.6844 0.065 0.044 0.005 0.000
0.7822 0.065 0.051 0.006 0.000
0.8800 0.065 0.057 0.006 0.000
0.9778 0.065 0.064 0.006 0.000
1.0756 0.065 0.070 0.007 0.000
1.1733 0.065 0.076 0.007 0.000
1.2711 0.065 0.083 0.007 0.000
1.3689 0.065 0.089 0.007 0.000
1.4667 0.065 0.096 0.008 0.000
1.5644 0.065 0.102 0.008 0.000
1.6622 0.065 0.109 0.008 0.000
1.7600 0.065 0.115 0.009 0.000
1.8578 0.065 0.121 0.009 0.000
1.9556 0.065 0.128 0.009 0.000
2.0533 0.065 0.134 0.009 0.000
2.1511 0.065 0.141 0.010 0.000
2.2489 0.065 0.147 0.010 0.000
2.3467 0.065 0.153 0.010 0.000
2.4444 0.065 0.160 0.010 0.000
2.5422 0.065 0.166 0.010 0.000
2.6400 0.065 0.173 0.011 0.000
2.7378 0.065 0.179 0.011 0.000
2.8356 0.065 0.185 0.011 0.000
2.9333 0.065 0.192 0.011 0.000
3.0311 0.065 0.198 0.011 0.000
3.1289 0.065 0.205 0.012 0.000
3.2267 0.065 0.211 0.012 0.000
3.3244 0.065 0.218 0.012 0.000
3.4222 0.065 0.224 0.012 0.000
3.5200 0.065 0.230 0.012 0.000
3.6178 0.065 0.237 0.012 0.000
Detention Provided:
21' x 136' x 7.8' = 22,276.8 cf
18092-Site Vault no Bypass 12/20/2017 5:23:13 PM Page 9
3.7156 0.065 0.243 0.013 0.000
3.8133 0.065 0.250 0.013 0.000
3.9111 0.065 0.256 0.013 0.000
4.0089 0.065 0.262 0.013 0.000
4.1067 0.065 0.269 0.013 0.000
4.2044 0.065 0.275 0.013 0.000
4.3022 0.065 0.282 0.014 0.000
4.4000 0.065 0.288 0.014 0.000
4.4978 0.065 0.294 0.014 0.000
4.5956 0.065 0.301 0.014 0.000
4.6933 0.065 0.307 0.014 0.000
4.7911 0.065 0.314 0.014 0.000
4.8889 0.065 0.320 0.015 0.000
4.9867 0.065 0.326 0.015 0.000
5.0844 0.065 0.333 0.018 0.000
5.1822 0.065 0.339 0.020 0.000
5.2800 0.065 0.346 0.021 0.000
5.3778 0.065 0.352 0.022 0.000
5.4756 0.065 0.359 0.023 0.000
5.5733 0.065 0.365 0.024 0.000
5.6711 0.065 0.371 0.024 0.000
5.7689 0.065 0.378 0.025 0.000
5.8667 0.065 0.384 0.026 0.000
5.9644 0.065 0.391 0.027 0.000
6.0622 0.065 0.397 0.029 0.000
6.1600 0.065 0.403 0.031 0.000
6.2578 0.065 0.410 0.032 0.000
6.3556 0.065 0.416 0.033 0.000
6.4533 0.065 0.423 0.034 0.000
6.5511 0.065 0.429 0.035 0.000
6.6489 0.065 0.435 0.036 0.000
6.7467 0.065 0.442 0.037 0.000
6.8444 0.065 0.448 0.038 0.000
6.9422 0.065 0.455 0.039 0.000
7.0400 0.065 0.461 0.040 0.000
7.1378 0.065 0.468 0.040 0.000
7.2356 0.065 0.474 0.041 0.000
7.3333 0.065 0.480 0.042 0.000
7.4311 0.065 0.487 0.043 0.000
7.5289 0.065 0.493 0.043 0.000
7.6267 0.065 0.500 0.044 0.000
7.7244 0.065 0.506 0.045 0.000
7.8222 0.065 0.512 0.081 0.000
7.9200 0.065 0.519 0.483 0.000
8.0178 0.065 0.525 1.065 0.000
8.1156 0.065 0.532 1.641 0.000
8.2133 0.065 0.538 2.051 0.000
8.3111 0.065 0.544 2.300 0.000
8.4089 0.065 0.551 2.507 0.000
8.5067 0.065 0.557 2.698 0.000
8.6044 0.065 0.564 2.875 0.000
8.7022 0.065 0.570 3.043 0.000
8.8000 0.065 0.577 3.201 0.000
8.8978 0.065 0.530 3.352 0.000
18092-Site Vault no Bypass 12/20/2017 5:23:13 PM Page 10
Analysis Results
POC 1
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #1
Total Pervious Area:0.996
Total Impervious Area:0.055
Mitigated Landuse Totals for POC #1
Total Pervious Area:0.158
Total Impervious Area:0.893
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.056778
5 year 0.08592
10 year 0.108165
25 year 0.139737
50 year 0.16585
100 year 0.194254
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.033214
5 year 0.044942
10 year 0.053873
25 year 0.066565
50 year 0.0771
100 year 0.088613
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.080 0.038
1950 0.081 0.037
1951 0.093 0.055
1952 0.041 0.022
1953 0.032 0.029
1954 0.043 0.028
1955 0.062 0.031
1956 0.058 0.041
1957 0.063 0.033
1958 0.047 0.026
Developed, Un-Mitigated Flows
18092-Site Vault no Bypass 12/20/2017 5:23:46 PM Page 11
1959 0.041 0.025
1960 0.083 0.042
1961 0.049 0.039
1962 0.030 0.022
1963 0.045 0.030
1964 0.053 0.031
1965 0.051 0.033
1966 0.039 0.027
1967 0.086 0.037
1968 0.056 0.037
1969 0.051 0.030
1970 0.050 0.028
1971 0.058 0.033
1972 0.074 0.051
1973 0.039 0.030
1974 0.055 0.033
1975 0.072 0.034
1976 0.053 0.028
1977 0.029 0.026
1978 0.042 0.029
1979 0.036 0.034
1980 0.119 0.045
1981 0.044 0.032
1982 0.095 0.056
1983 0.054 0.032
1984 0.038 0.023
1985 0.028 0.029
1986 0.078 0.031
1987 0.079 0.042
1988 0.034 0.024
1989 0.029 0.024
1990 0.211 0.056
1991 0.111 0.055
1992 0.048 0.025
1993 0.039 0.019
1994 0.023 0.019
1995 0.053 0.034
1996 0.118 0.055
1997 0.089 0.058
1998 0.047 0.029
1999 0.135 0.050
2000 0.047 0.033
2001 0.028 0.031
2002 0.064 0.040
2003 0.081 0.032
2004 0.088 0.056
2005 0.062 0.028
2006 0.059 0.041
2007 0.162 0.140
2008 0.159 0.054
2009 0.083 0.037
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.2106 0.1397
2 0.1624 0.0578
3 0.1585 0.0565
18092-Site Vault no Bypass 12/20/2017 5:23:46 PM Page 12
4 0.1351 0.0562
5 0.1188 0.0561
6 0.1175 0.0549
7 0.1106 0.0549
8 0.0950 0.0547
9 0.0927 0.0540
10 0.0891 0.0505
11 0.0875 0.0497
12 0.0860 0.0448
13 0.0831 0.0424
14 0.0830 0.0418
15 0.0808 0.0410
16 0.0806 0.0406
17 0.0801 0.0401
18 0.0792 0.0392
19 0.0776 0.0377
20 0.0743 0.0373
21 0.0719 0.0371
22 0.0637 0.0369
23 0.0626 0.0368
24 0.0618 0.0339
25 0.0618 0.0337
26 0.0586 0.0336
27 0.0582 0.0334
28 0.0578 0.0327
29 0.0556 0.0326
30 0.0547 0.0326
31 0.0540 0.0325
32 0.0530 0.0324
33 0.0528 0.0320
34 0.0527 0.0319
35 0.0509 0.0309
36 0.0506 0.0307
37 0.0496 0.0307
38 0.0489 0.0306
39 0.0482 0.0302
40 0.0475 0.0298
41 0.0467 0.0297
42 0.0466 0.0292
43 0.0452 0.0291
44 0.0444 0.0289
45 0.0429 0.0287
46 0.0423 0.0284
47 0.0412 0.0283
48 0.0409 0.0279
49 0.0393 0.0278
50 0.0392 0.0275
51 0.0391 0.0261
52 0.0385 0.0259
53 0.0362 0.0255
54 0.0338 0.0245
55 0.0321 0.0240
56 0.0295 0.0235
57 0.0287 0.0231
58 0.0286 0.0225
59 0.0284 0.0223
60 0.0278 0.0193
61 0.0225 0.0192
18092-Site Vault no Bypass 12/20/2017 5:23:46 PM Page 14
Duration Flows
The Facility PASSED
Flow(cfs)Predev Mit Percentage Pass/Fail
0.0284 9586 3942 41 Pass
0.0298 8446 3510 41 Pass
0.0312 7463 3093 41 Pass
0.0326 6618 2721 41 Pass
0.0339 5867 2372 40 Pass
0.0353 5262 2044 38 Pass
0.0367 4721 1706 36 Pass
0.0381 4231 1350 31 Pass
0.0395 3807 1074 28 Pass
0.0409 3422 841 24 Pass
0.0423 3082 636 20 Pass
0.0437 2748 425 15 Pass
0.0451 2460 322 13 Pass
0.0464 2237 255 11 Pass
0.0478 2021 170 8 Pass
0.0492 1823 125 6 Pass
0.0506 1626 90 5 Pass
0.0520 1465 72 4 Pass
0.0534 1320 62 4 Pass
0.0548 1186 56 4 Pass
0.0562 1086 52 4 Pass
0.0575 996 44 4 Pass
0.0589 902 39 4 Pass
0.0603 828 36 4 Pass
0.0617 756 32 4 Pass
0.0631 688 31 4 Pass
0.0645 622 28 4 Pass
0.0659 551 26 4 Pass
0.0673 496 19 3 Pass
0.0687 445 19 4 Pass
0.0700 388 18 4 Pass
0.0714 344 18 5 Pass
0.0728 298 18 6 Pass
0.0742 261 16 6 Pass
0.0756 218 16 7 Pass
0.0770 189 15 7 Pass
0.0784 166 14 8 Pass
0.0798 145 14 9 Pass
0.0812 126 13 10 Pass
0.0825 112 13 11 Pass
0.0839 94 11 11 Pass
0.0853 83 10 12 Pass
0.0867 71 9 12 Pass
0.0881 62 8 12 Pass
0.0895 52 8 15 Pass
0.0909 49 6 12 Pass
0.0923 43 6 13 Pass
0.0936 35 6 17 Pass
0.0950 31 6 19 Pass
0.0964 27 6 22 Pass
0.0978 27 6 22 Pass
0.0992 25 6 24 Pass
0.1006 24 6 25 Pass
18092-Site Vault no Bypass 12/20/2017 5:23:46 PM Page 15
0.1020 23 6 26 Pass
0.1034 20 3 15 Pass
0.1048 20 3 15 Pass
0.1061 18 3 16 Pass
0.1075 15 3 20 Pass
0.1089 12 3 25 Pass
0.1103 12 3 25 Pass
0.1117 11 3 27 Pass
0.1131 11 3 27 Pass
0.1145 10 3 30 Pass
0.1159 10 3 30 Pass
0.1173 10 3 30 Pass
0.1186 8 3 37 Pass
0.1200 7 2 28 Pass
0.1214 7 2 28 Pass
0.1228 7 2 28 Pass
0.1242 7 2 28 Pass
0.1256 7 1 14 Pass
0.1270 7 1 14 Pass
0.1284 7 1 14 Pass
0.1297 7 1 14 Pass
0.1311 7 1 14 Pass
0.1325 7 1 14 Pass
0.1339 7 1 14 Pass
0.1353 6 1 16 Pass
0.1367 5 1 20 Pass
0.1381 5 1 20 Pass
0.1395 5 1 20 Pass
0.1409 5 0 0 Pass
0.1422 4 0 0 Pass
0.1436 4 0 0 Pass
0.1450 4 0 0 Pass
0.1464 4 0 0 Pass
0.1478 4 0 0 Pass
0.1492 4 0 0 Pass
0.1506 4 0 0 Pass
0.1520 4 0 0 Pass
0.1534 4 0 0 Pass
0.1547 3 0 0 Pass
0.1561 3 0 0 Pass
0.1575 3 0 0 Pass
0.1589 2 0 0 Pass
0.1603 2 0 0 Pass
0.1617 2 0 0 Pass
0.1631 1 0 0 Pass
0.1645 1 0 0 Pass
0.1659 1 0 0 Pass
DEVELOPED BASIN MAP
WWWWWWWWWWWWWWSDSDWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWNEW SDMH #4 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #1 TYPE 1,W/ VANED GRATENEW SDMH #1 TYPE 2-60"W/ SOLID LOCKING LIDNEW CB #2 TYPE 1,W/ SOLID LOCKING LIDFOOTING DRAIN CO #1EX. CB #570 TYPE 1,W/STANDARD GRATEMODULAR WETLAND #1NEW CB #5 TYPE 1,W/ VANED GRATEEX. CB TYPE 2-72"w/ SOLID LOCKING LIDEX. CB TYPE 2-54"w/ SOLID LOCKING LIDNEW CB #4 TYPE 1,W/HERRINGBONE GRATEROOF DRAIN CO #1ROOF DRAIN CO #4ROOF DRAIN CO #5NEW SDMH #2 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #7 TYPE 1,W/ SOLID LOCKING LIDNEW SDMH #3 TYPE 2-54"W/ SOLID LOCKING LIDWWWWWWWWWWWWWWSDSDWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWNEW CB #3 TYPE 1,W/ SOLID LOCKING LIDNEW CB #8 TYPE 2-48"W/ VANED GRATEINSTALL RISER TEEDETAIL PER SHEET C23NEW SDMH #7 TYPE 2-48"W/ SOLID LOCKING LIDNEW SDMH #6 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #9NEW CB #10 TYPE 1,W/ SOLID LOCKING LIDNEW CB #11 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #2ROOF DRAIN CO #3EX. CB #569 TYPE 1,W/ NEW SOLID LOCKING LIDROOF DRAIN CO #6UW MEDICINE - VALLEY MEDICAL CENTERMEDICAL OFFICE BUILDING EXPANSIONIN COMPLIANCE WITH CITY OF RENTON STANDARDS
SITE DETENTION VAULT DETAIL
UW MEDICINE - VALLEY MEDICAL CENTER
MEDICAL OFFICE BUILDING EXPANSION
IN COMPLIANCE WITH CITY OF RENTON STANDARDS
MODULAR WETLAND SYSTEM
SIZING CALCULATIONS
398 Via El Centro, Oceanside, CA 92058
(760) 433-7640 • Fax (760) 433-3176
www.biocleanenvironmental.com
MWS SIZING
Anthony J. Spolar
9/20/2017
398 Via El Centro, Oceanside, CA 92058
(760) 433-7640 • Fax (760) 433-3176
www.biocleanenvironmental.com
Date: 09/20/17
Subject: 4249 – VMC Medical Office Building, Renton, Wa
To Whom It May Concern,
The MWS Linear will be sized in accordance with the TAPE GULD approval for the Modular
Wetland System. The system is sized at a loading rate of (less than or equal to) 1.0 gpm/ sq ft,
where the pre-filter cartridges are sized at a loading rate of less than 2.10 gpm/ sq ft. Design,
sizing, and loading have been reviewed and approved by a Modular Wetland Representative and
is ready for final approval. Shown below are the calculations for this Project:
MWS-L-4-6.33-V-UG
Required Treatment Flow Rate = 0.0499 cfs
MWS-Linear-4-6 Treatment Capacity Provided = 0.0499 cfs or 22.39 gpm at 2.5’ HGL
Pre-filter Cartridge = 1 half size cartridge
Surface Area per Cartridge = 12.8 sq ft
Loading rate (Pre-Filter Cartridge) = 1.7 gpm / sq ft
MWS Wetland Surface Area = 23.25 sf
Loading Rate (Wetland Media) = 1.0 gpm/sf
If you have any questions please feel free to contact us at your convenience.
Sincerely,
Anthony J. Spolar, E.I.T.
Stormwater Engineer
Modular Wetland System, Inc.
398 Via El Centro, Oceanside, CA 92058
(760) 433-7640 • Fax (760) 433-3176
www.biocleanenvironmental.com
𝑪𝑪𝑨𝑪 𝑳𝑹𝑪𝑹 𝑹𝑪𝑪𝑹𝑨𝑳𝑪𝑹𝑳𝑨𝑹 𝑹𝑪𝑪𝑹
𝐺�ℎ𝑟𝑎𝑘 𝑟�𝑎𝑟: 𝑄=𝑉𝐴; 𝑄=𝑘𝑎𝑎𝑘 𝑎𝑘𝑘𝑟 𝑟𝑎𝑟𝑎,𝑉= 𝑎𝑐√2𝑎�,𝐴=𝑉(𝑎�)
𝑎𝑐 �ℎ𝑟 𝑟�𝑎 𝑎�ℎ𝑟𝑎�𝑎𝑟𝑎𝑎 𝑎𝑘𝑎𝑎𝑎�ℎ𝑎𝑎𝑘𝑟,𝑉 �ℎ𝑟 𝑟�𝑎 𝑟�ℎ𝑎𝑟� 𝑘𝑎 𝑟�𝑎 𝑟𝑎�ℎ𝑟 & � �ℎ𝑟 𝑟�𝑎 𝑘𝑎𝑎𝑘 𝐺𝐺𝐿
𝑎𝑄=𝑎𝑐√2𝑎� (𝑉)(𝑎�)
∫𝑎𝑄
𝑄
0
=𝑎𝑐𝑉√2𝑎 ∫�1/2 𝑎�
�
0
𝑄=𝑎𝑐𝑉 √2𝑎 2
3 �3/2
�= (𝑄
2
3 𝑎𝑐𝑉√2𝑎
)
2/3
𝐷𝑎𝑟𝑎𝑟𝑘�ℎ𝑘𝑎 𝑘𝑎𝑎𝑘 𝐺𝐺𝐿 𝑎𝑦 𝑟𝑎𝑘�ℎ𝑘𝑎 𝑟�𝑎 𝑟𝑟𝑘:(𝑘𝑟𝑟𝑘𝑎𝑟 𝑘�ℎ𝑘𝑎 𝑎𝑘𝑎𝑟.)
+(1 �ℎ𝑘𝑎� 𝑎�ℎ𝑎𝑎𝑎𝑟𝑎𝑘𝑟�ℎ𝑎𝑘 𝑎𝑎𝑟𝑟𝑎𝑎𝑘 𝑎�ℎ𝑟𝑎�𝑎𝑟𝑎𝑎 𝑎�𝑎𝑘𝑎𝑎𝑟 𝑎𝑘𝑎 𝑘𝑟𝑎
−𝑟𝑟𝑎𝑎𝑟𝑘𝑎𝑘𝑟 𝑎�𝑎𝑘𝑎𝑎𝑟)+(𝑟𝑎�ℎ𝑟 �𝑎�ℎ𝑎�𝑟)+(�𝑎𝑎𝑎 𝑘𝑟𝑎𝑟 𝑟𝑎�ℎ𝑟)
MWS-4-6.33-V-UG:
𝐺�ℎ𝑟𝑎𝑘 𝑟�𝑎𝑟: 𝑄𝑝𝑐𝑎𝑘=0.33 𝑎𝑎𝑟; 𝑉=3′
�= (0.33
2
3 (0.6076)(3)√2(32.17)
)
2/3
=0.11′
Peak HGL = 69.23’ + 0.08’ + 2.5’ + 0.11’ = 71.92’
398 Via El Centro, Oceanside, CA 92058
(760) 433-7640 • Fax (760) 433-3176
www.biocleanenvironmental.com
𝑳𝑹𝑹 𝑳𝑹𝑪𝑪𝑪𝑪𝑪 𝑹𝑪𝒁𝑪𝑳𝑪
𝐺�ℎ𝑟𝑎𝑘 𝑟�𝑎𝑟: 𝑄=𝑉𝐴; 𝑄=𝑟𝑟𝑎𝑎𝑟𝑘𝑎𝑘𝑟 𝑎𝑘𝑘𝑟 𝑟𝑎𝑟𝑎,𝑉= 𝑎𝑐√2𝑎� ,𝐴= 𝜋𝐷2
4
𝑎𝑐 �ℎ𝑟 𝑟�𝑎 𝑎�ℎ𝑟𝑎�𝑎𝑟𝑎𝑎 𝑎𝑘𝑎𝑎𝑎�ℎ𝑎𝑎𝑘𝑟 & � �ℎ𝑟 𝑟�𝑎 𝑟𝑟𝑎𝑎𝑟𝑘𝑎𝑘𝑟 𝐺𝐺𝐿
𝑄𝑎𝑟𝑟�ℎ𝑟𝑎 𝑟𝑘 𝑟𝑘𝑘𝑟𝑎 𝑎𝑘𝑟 𝑟�𝑎 𝑎�ℎ𝑎𝑘𝑎𝑟𝑎𝑟 𝑘𝑎 𝑟�𝑎 𝑘𝑟�ℎ𝑎�ℎ𝑎𝑎.
[𝐴= 𝑄
𝑉] 𝑟𝑐𝑣𝑟�ℎ𝑡𝑐→ 𝜋𝐷2
4 = 𝑄
𝑎𝑐√2𝑎�
𝐷= √4𝑄
𝜋𝑎𝑐√2𝑎�
; 𝑎𝑐= 𝑎𝑣𝑎𝑐=(0.98)(0.62)=0.6076
MWS-4-6.33-V-UG:
𝐺�ℎ𝑟𝑎𝑘:𝑄=0.0499 𝑎𝑎𝑟 ,�=2.5 𝑎𝑟
𝐷= √
4(0.0499)
𝜋(0.6076)√2(32.17)(2.5)=0.09′=1.09"
𝑄�𝑎 𝑎�ℎ𝑎𝑘𝑎𝑟𝑎𝑟 𝑘𝑎 𝑟�𝑎 𝑘𝑟�ℎ𝑎�ℎ𝑎𝑎 𝑘𝑎𝑎𝑎𝑟 𝑟𝑘 𝑎𝑎 1.09" �ℎ𝑘 𝑘𝑟𝑎𝑎𝑟 𝑟𝑘 𝑘𝑟𝑘𝑎𝑟𝑎𝑎 𝑎 �𝑎𝑎𝑎 𝑘𝑎
2.5′ �ℎ𝑘 𝑟�𝑎 𝐿𝑉𝑄 𝑟𝑘�ℎ𝑟.
MODULAR WETLAND DETAIL
DEVELOPED BASIN MAP
DN UPDNUP400LOBBY401STORSTAIR 8 STAIR 7ELEV 4ELEV 5403STORAGEELEV 3 UW MEDICINE - VALLEY MEDICAL CENTERROAD IMPROVEMENTS
FLOW CONTROL CALCULATIONS
WWHM2012
PROJECT REPORT
MOB Road Improvement
Detention Vault
1/19/2017
18092-Road with Bypass 1/19/2018 6:11:20 AM Page 2
General Model Information
Project Name:18092-Road with Bypass
Site Name:Road Vault
Site Address:MOB
City:Renton
Report Date:1/19/2018
Gage:Seatac
Data Start:1948/10/01
Data End:2009/09/30
Timestep:15 Minute
Precip Scale:1.000
Version Date:2017/04/14
Version:4.2.13
POC Thresholds
Low Flow Threshold for POC1:50 Percent of the 2 Year
High Flow Threshold for POC1:50 Year
18092-Road with Bypass 1/19/2018 6:11:20 AM Page 3
Landuse Basin Data
Predeveloped Land Use
Basin 1
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Forest, Flat 0.707
Pervious Total 0.707
Impervious Land Use acre
ROADS FLAT 0.051
Impervious Total 0.051
Basin Total 0.758
Element Flows To:
Surface Interflow Groundwater
18092-Road with Bypass 1/19/2018 6:11:20 AM Page 4
Mitigated Land Use
Basin 1
Bypass:No
GroundWater:No
Pervious Land Use acre
C, Lawn, Flat 0.043
Pervious Total 0.043
Impervious Land Use acre
ROADS FLAT 0.715
Impervious Total 0.715
Basin Total 0.758
Element Flows To:
Surface Interflow Groundwater
Vault 1 Vault 1
18092-Road with Bypass 1/19/2018 6:11:20 AM Page 6
Mitigated Routing
Vault 1
Width:19 ft.
Length:100 ft.
Depth:8 ft.
Discharge Structure
Riser Height:7 ft.
Riser Diameter:12 in.
Orifice 1 Diameter:0.5625 in.Elevation:0 ft.
Orifice 2 Diameter:0.55 in.Elevation:4 ft.
Orifice 3 Diameter:0.8 in.Elevation:5.8 ft.
Element Flows To:
Outlet 1 Outlet 2
Vault Hydraulic Table
Stage(feet)Area(ac.)Volume(ac-ft.)Discharge(cfs)Infilt(cfs)
0.0000 0.043 0.000 0.000 0.000
0.0889 0.043 0.003 0.002 0.000
0.1778 0.043 0.007 0.003 0.000
0.2667 0.043 0.011 0.004 0.000
0.3556 0.043 0.015 0.005 0.000
0.4444 0.043 0.019 0.005 0.000
0.5333 0.043 0.023 0.006 0.000
0.6222 0.043 0.027 0.006 0.000
0.7111 0.043 0.031 0.007 0.000
0.8000 0.043 0.034 0.007 0.000
0.8889 0.043 0.038 0.008 0.000
0.9778 0.043 0.042 0.008 0.000
1.0667 0.043 0.046 0.008 0.000
1.1556 0.043 0.050 0.009 0.000
1.2444 0.043 0.054 0.009 0.000
1.3333 0.043 0.058 0.009 0.000
1.4222 0.043 0.062 0.010 0.000
1.5111 0.043 0.065 0.010 0.000
1.6000 0.043 0.069 0.010 0.000
1.6889 0.043 0.073 0.011 0.000
1.7778 0.043 0.077 0.011 0.000
1.8667 0.043 0.081 0.011 0.000
1.9556 0.043 0.085 0.012 0.000
2.0444 0.043 0.089 0.012 0.000
2.1333 0.043 0.093 0.012 0.000
2.2222 0.043 0.096 0.012 0.000
2.3111 0.043 0.100 0.013 0.000
2.4000 0.043 0.104 0.013 0.000
2.4889 0.043 0.108 0.013 0.000
2.5778 0.043 0.112 0.013 0.000
2.6667 0.043 0.116 0.014 0.000
2.7556 0.043 0.120 0.014 0.000
2.8444 0.043 0.124 0.014 0.000
2.9333 0.043 0.127 0.014 0.000
3.0222 0.043 0.131 0.014 0.000
3.1111 0.043 0.135 0.015 0.000
3.2000 0.043 0.139 0.015 0.000
3.2889 0.043 0.143 0.015 0.000
18092-Road with Bypass 1/19/2018 6:11:20 AM Page 7
3.3778 0.043 0.147 0.015 0.000
3.4667 0.043 0.151 0.016 0.000
3.5556 0.043 0.155 0.016 0.000
3.6444 0.043 0.159 0.016 0.000
3.7333 0.043 0.162 0.016 0.000
3.8222 0.043 0.166 0.016 0.000
3.9111 0.043 0.170 0.017 0.000
4.0000 0.043 0.174 0.017 0.000
4.0889 0.043 0.178 0.019 0.000
4.1778 0.043 0.182 0.021 0.000
4.2667 0.043 0.186 0.022 0.000
4.3556 0.043 0.190 0.022 0.000
4.4444 0.043 0.193 0.023 0.000
4.5333 0.043 0.197 0.024 0.000
4.6222 0.043 0.201 0.024 0.000
4.7111 0.043 0.205 0.025 0.000
4.8000 0.043 0.209 0.026 0.000
4.8889 0.043 0.213 0.026 0.000
4.9778 0.043 0.217 0.027 0.000
5.0667 0.043 0.221 0.027 0.000
5.1556 0.043 0.224 0.028 0.000
5.2444 0.043 0.228 0.028 0.000
5.3333 0.043 0.232 0.029 0.000
5.4222 0.043 0.236 0.029 0.000
5.5111 0.043 0.240 0.030 0.000
5.6000 0.043 0.244 0.030 0.000
5.6889 0.043 0.248 0.031 0.000
5.7778 0.043 0.252 0.031 0.000
5.8667 0.043 0.255 0.036 0.000
5.9556 0.043 0.259 0.039 0.000
6.0444 0.043 0.263 0.041 0.000
6.1333 0.043 0.267 0.043 0.000
6.2222 0.043 0.271 0.044 0.000
6.3111 0.043 0.275 0.046 0.000
6.4000 0.043 0.279 0.047 0.000
6.4889 0.043 0.283 0.049 0.000
6.5778 0.043 0.286 0.050 0.000
6.6667 0.043 0.290 0.051 0.000
6.7556 0.043 0.294 0.052 0.000
6.8444 0.043 0.298 0.054 0.000
6.9333 0.043 0.302 0.055 0.000
7.0222 0.043 0.306 0.091 0.000
7.1111 0.043 0.310 0.447 0.000
7.2000 0.043 0.314 0.965 0.000
7.2889 0.043 0.317 1.506 0.000
7.3778 0.043 0.321 1.939 0.000
7.4667 0.043 0.325 2.199 0.000
7.5556 0.043 0.329 2.409 0.000
7.6444 0.043 0.333 2.591 0.000
7.7333 0.043 0.337 2.761 0.000
7.8222 0.043 0.341 2.920 0.000
7.9111 0.043 0.345 3.072 0.000
8.0000 0.043 0.348 3.216 0.000
8.0889 0.043 0.352 3.353 0.000
8.1778 0.000 0.000 3.486 0.000
18092-Road with Bypass 1/19/2018 6:11:20 AM Page 8
Analysis Results
POC 1
+ Predeveloped x Mitigated
Predeveloped Landuse Totals for POC #1
Total Pervious Area:0.707
Total Impervious Area:0.051
Mitigated Landuse Totals for POC #1
Total Pervious Area:0.043
Total Impervious Area:0.715
Flow Frequency Method:Log Pearson Type III 17B
Flow Frequency Return Periods for Predeveloped. POC #1
Return Period Flow(cfs)
2 year 0.033613
5 year 0.048144
10 year 0.058784
25 year 0.073405
50 year 0.085163
100 year 0.097677
Flow Frequency Return Periods for Mitigated. POC #1
Return Period Flow(cfs)
2 year 0.017359
5 year 0.024945
10 year 0.031
25 year 0.039951
50 year 0.047647
100 year 0.0563
Annual Peaks
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.045 0.013
1950 0.045 0.016
1951 0.056 0.036
1952 0.025 0.011
1953 0.020 0.014
1954 0.027 0.015
1955 0.038 0.015
1956 0.036 0.017
1957 0.037 0.015
1958 0.029 0.016
18092-Road with Bypass 1/19/2018 6:11:59 AM Page 9
1959 0.025 0.014
1960 0.047 0.030
1961 0.030 0.016
1962 0.018 0.011
1963 0.028 0.015
1964 0.031 0.015
1965 0.031 0.019
1966 0.025 0.014
1967 0.049 0.016
1968 0.033 0.014
1969 0.031 0.014
1970 0.030 0.014
1971 0.033 0.016
1972 0.045 0.026
1973 0.024 0.017
1974 0.031 0.016
1975 0.043 0.015
1976 0.031 0.015
1977 0.017 0.014
1978 0.025 0.016
1979 0.028 0.012
1980 0.056 0.030
1981 0.027 0.014
1982 0.052 0.027
1983 0.032 0.016
1984 0.023 0.013
1985 0.021 0.014
1986 0.046 0.023
1987 0.047 0.029
1988 0.019 0.014
1989 0.021 0.014
1990 0.101 0.029
1991 0.063 0.029
1992 0.028 0.016
1993 0.023 0.013
1994 0.014 0.011
1995 0.032 0.016
1996 0.066 0.036
1997 0.052 0.038
1998 0.024 0.014
1999 0.062 0.028
2000 0.030 0.017
2001 0.022 0.012
2002 0.032 0.025
2003 0.042 0.015
2004 0.047 0.047
2005 0.037 0.015
2006 0.036 0.017
2007 0.079 0.073
2008 0.085 0.042
2009 0.050 0.023
Ranked Annual Peaks
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.1013 0.0729
2 0.0848 0.0468
3 0.0792 0.0424
18092-Road with Bypass 1/19/2018 6:11:59 AM Page 10
4 0.0658 0.0383
5 0.0634 0.0365
6 0.0619 0.0361
7 0.0561 0.0303
8 0.0557 0.0298
9 0.0523 0.0294
10 0.0521 0.0289
11 0.0501 0.0287
12 0.0490 0.0279
13 0.0475 0.0271
14 0.0471 0.0262
15 0.0468 0.0251
16 0.0464 0.0231
17 0.0453 0.0228
18 0.0449 0.0190
19 0.0449 0.0170
20 0.0428 0.0169
21 0.0416 0.0167
22 0.0382 0.0167
23 0.0374 0.0164
24 0.0372 0.0163
25 0.0362 0.0160
26 0.0359 0.0159
27 0.0330 0.0158
28 0.0328 0.0158
29 0.0319 0.0158
30 0.0318 0.0157
31 0.0318 0.0156
32 0.0313 0.0156
33 0.0312 0.0155
34 0.0312 0.0154
35 0.0310 0.0154
36 0.0308 0.0153
37 0.0300 0.0152
38 0.0300 0.0151
39 0.0298 0.0150
40 0.0290 0.0149
41 0.0284 0.0146
42 0.0277 0.0144
43 0.0276 0.0144
44 0.0268 0.0143
45 0.0266 0.0142
46 0.0254 0.0142
47 0.0254 0.0141
48 0.0252 0.0140
49 0.0250 0.0139
50 0.0243 0.0137
51 0.0239 0.0136
52 0.0235 0.0136
53 0.0233 0.0135
54 0.0216 0.0131
55 0.0208 0.0131
56 0.0206 0.0128
57 0.0202 0.0119
58 0.0192 0.0116
59 0.0176 0.0115
60 0.0167 0.0114
61 0.0137 0.0114
18092-Road with Bypass 1/19/2018 6:11:59 AM Page 12
Duration Flows
The Facility PASSED
Flow(cfs)Predev Mit Percentage Pass/Fail
0.0168 8476 5467 64 Pass
0.0175 7636 4361 57 Pass
0.0182 6874 4252 61 Pass
0.0189 6248 4143 66 Pass
0.0196 5685 4010 70 Pass
0.0203 5210 3852 73 Pass
0.0209 4729 3670 77 Pass
0.0216 4295 3471 80 Pass
0.0223 3929 3277 83 Pass
0.0230 3589 3067 85 Pass
0.0237 3292 2840 86 Pass
0.0244 3003 2573 85 Pass
0.0251 2755 2229 80 Pass
0.0258 2494 2018 80 Pass
0.0265 2269 1711 75 Pass
0.0272 2081 1413 67 Pass
0.0279 1899 1166 61 Pass
0.0285 1747 981 56 Pass
0.0292 1601 780 48 Pass
0.0299 1458 585 40 Pass
0.0306 1330 440 33 Pass
0.0313 1196 356 29 Pass
0.0320 1100 311 28 Pass
0.0327 1024 294 28 Pass
0.0334 954 283 29 Pass
0.0341 887 274 30 Pass
0.0348 823 264 32 Pass
0.0354 764 251 32 Pass
0.0361 692 232 33 Pass
0.0368 633 223 35 Pass
0.0375 588 216 36 Pass
0.0382 533 204 38 Pass
0.0389 492 198 40 Pass
0.0396 456 190 41 Pass
0.0403 415 183 44 Pass
0.0410 379 174 45 Pass
0.0417 331 163 49 Pass
0.0424 291 150 51 Pass
0.0430 262 140 53 Pass
0.0437 228 127 55 Pass
0.0444 204 118 57 Pass
0.0451 179 109 60 Pass
0.0458 159 97 61 Pass
0.0465 141 78 55 Pass
0.0472 124 67 54 Pass
0.0479 112 62 55 Pass
0.0486 103 59 57 Pass
0.0493 95 55 57 Pass
0.0499 88 51 57 Pass
0.0506 78 47 60 Pass
0.0513 68 43 63 Pass
0.0520 58 40 68 Pass
0.0527 45 36 80 Pass
18092-Road with Bypass 1/19/2018 6:11:59 AM Page 13
0.0534 41 31 75 Pass
0.0541 35 21 60 Pass
0.0548 34 16 47 Pass
0.0555 32 13 40 Pass
0.0562 27 13 48 Pass
0.0569 24 12 50 Pass
0.0575 24 12 50 Pass
0.0582 23 12 52 Pass
0.0589 22 10 45 Pass
0.0596 22 10 45 Pass
0.0603 17 10 58 Pass
0.0610 16 9 56 Pass
0.0617 14 9 64 Pass
0.0624 11 9 81 Pass
0.0631 11 9 81 Pass
0.0638 10 8 80 Pass
0.0644 9 8 88 Pass
0.0651 8 8 100 Pass
0.0658 7 6 85 Pass
0.0665 6 4 66 Pass
0.0672 6 4 66 Pass
0.0679 6 3 50 Pass
0.0686 6 3 50 Pass
0.0693 6 3 50 Pass
0.0700 6 3 50 Pass
0.0707 6 3 50 Pass
0.0714 6 2 33 Pass
0.0720 6 1 16 Pass
0.0727 6 1 16 Pass
0.0734 6 0 0 Pass
0.0741 5 0 0 Pass
0.0748 5 0 0 Pass
0.0755 5 0 0 Pass
0.0762 4 0 0 Pass
0.0769 4 0 0 Pass
0.0776 4 0 0 Pass
0.0783 4 0 0 Pass
0.0789 4 0 0 Pass
0.0796 3 0 0 Pass
0.0803 3 0 0 Pass
0.0810 3 0 0 Pass
0.0817 3 0 0 Pass
0.0824 2 0 0 Pass
0.0831 2 0 0 Pass
0.0838 2 0 0 Pass
0.0845 2 0 0 Pass
0.0852 1 0 0 Pass
18092-Road with Bypass 12/21/2017 3:22:32 PM Page 17
Appendix
Predeveloped Schematic
18092-Road with Bypass 12/21/2017 3:22:32 PM Page 18
Mitigated Schematic
NORTH ACCESS ROAD
DETENTION VAULT DETAIL
UW MEDICINE - VALLEY MEDICAL CENTERMEDICAL OFFICE BUILDING EXPANSIONIN COMPLIANCE WITH CITY OF RENTON STANDARDS
MODULAR WETLAND DETAIL
Tab 5.0
5.0 CONVEYANCE SYSTEM ANALYSIS
AND DESIGN
5.0 CONVEYANCE SYSTEM ANALYSIS AND DESIGN
The conveyance system for this project site has been sized in accordance with Section 1.2.4.1 of
the 2017 Renton Surface Water Design Manual. For the conveyance sizing an initial time of
concentration of 6.3 minutes, a Manning's 'n' value of 0.014, and a 100-year precipitation of 3.95
inches were used. All pipes conveyed the flow contributing to them without overtopping any catch
basins.
MEDICAL OFFICE BUILDING
CONVEYANCE BASIN MAP
WWWWWWWWWWWWWWSDSDWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWSDSDWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWNEW SDMH #4 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #1 TYPE 1,W/ VANED GRATENEW SDMH #1 TYPE 2-60"W/ SOLID LOCKING LIDNEW CB #2 TYPE 1,W/ SOLID LOCKING LIDFOOTING DRAIN CO #1EX. CB #570 TYPE 1,W/STANDARD GRATEMODULAR WETLAND #1NEW CB #5 TYPE 1,W/ VANED GRATEEX. CB TYPE 2-72"w/ SOLID LOCKING LIDEX. CB TYPE 2-54"w/ SOLID LOCKING LIDNEW CB #4 TYPE 1,W/HERRINGBONE GRATEROOF DRAIN CO #1ROOF DRAIN CO #5ROOF DRAIN CO #4NEW SDMH #2 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #7 TYPE 1,W/ SOLID LOCKING LIDNEW SDMH #3 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #3 TYPE 1,W/ SOLID LOCKING LIDNEW CB #8 TYPE 2-48"W/ VANED GRATEINSTALL RISER TEEDETAIL PER SHEET C23NEW SDMH #7 TYPE 2-48"W/ SOLID LOCKING LIDNEW SDMH #6 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #9NEW CB #10 TYPE 1,W/ SOLID LOCKING LIDNEW CB #11 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #2ROOF DRAIN CO #3EX. CB #569 TYPE 1,W/ NEW SOLID LOCKING LIDROOF DRAIN CO #6UW MEDICINE - VALLEY MEDICAL CENTERMEDICAL OFFICE BUILDING EXPANSIONIN COMPLIANCE WITH CITY OF RENTON STANDARDS
WWWWWWWWWWWWWWSDSDWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWSDSDWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWNEW SDMH #4 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #1 TYPE 1,W/ VANED GRATENEW SDMH #1 TYPE 2-60"W/ SOLID LOCKING LIDNEW CB #2 TYPE 1,W/ SOLID LOCKING LIDFOOTING DRAIN CO #1EX. CB #570 TYPE 1,W/STANDARD GRATEMODULAR WETLAND #1NEW CB #5 TYPE 1,W/ VANED GRATEEX. CB TYPE 2-72"w/ SOLID LOCKING LIDEX. CB TYPE 2-54"w/ SOLID LOCKING LIDNEW CB #4 TYPE 1,W/HERRINGBONE GRATEROOF DRAIN CO #1ROOF DRAIN CO #4ROOF DRAIN CO #5NEW SDMH #2 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #7 TYPE 1,W/ SOLID LOCKING LIDNEW SDMH #3 TYPE 2-54"W/ SOLID LOCKING LIDNEW CB #3 TYPE 1,W/ SOLID LOCKING LIDNEW CB #8 TYPE 2-48"W/ VANED GRATEINSTALL RISER TEEDETAIL PER SHEET C23NEW SDMH #7 TYPE 2-48"W/ SOLID LOCKING LIDNEW SDMH #6 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #9NEW CB #10 TYPE 1,W/ SOLID LOCKING LIDNEW CB #11 TYPE 2-48"W/ SOLID LOCKING LIDROOF DRAIN CO #2ROOF DRAIN CO #3EX. CB #569 TYPE 1,W/ NEW SOLID LOCKING LIDROOF DRAIN CO #6UW MEDICINE - VALLEY MEDICAL CENTERMEDICAL OFFICE BUILDING EXPANSIONIN COMPLIANCE WITH CITY OF RENTON STANDARDS
MEDICAL OFFICE BUILDING
CONVEYANCE CALCULATIONS
KING COUNTY DESIGN FOR 100YEAR STORMJOB NAME: VMC MOBNOTE: ENTER DEFAULTS AND STORM DATA BEFORE BEGINNING JOB#: 18092 DEFAULTS C=0.9n=0.014FILE NO.: 18092-MOB Conveyance Calcs-2017-12-21d=12Tc=6.3A= Contributing Area (Ac)Qd= Design Flow (cfs)COEFFICIENTS FOR THE RATIONAL METHOD "Ir"-EQUATIONC= Runoff Coefficient Qf= Full Capacity Flow (cfs)STORMAr BrTc= Time of Concentration (min)Vd= Velocity at Design Flow (fps)2YR1.580.58I= Intensity at Tc (in/hr)Vf= Velocity at Full Flow (fps)10YR2.440.64PRECIP=3.95d= Diameter of Pipe (in) s= Slope of pipe (%) 25YR 2.66 0.65 Ar=2.61L= Length of Pipe (ft)n= Manning Roughness Coefficient50YR2.750.65Br=0.63D= Water Depth at Qd (in)Tt= Travel Time at Vd (min)100YR2.610.63FROM TO A s L d Tc n C SUM A A*C SUM A*C I Qd QfQd/QfD/d D Vf Vd Tt====== ====== ====== ====== ================== ====== ====== ====== ===================== ====== ====== ====== ====== ====== ====== ====== ======CB1 CB20.31 3.91 62 126.3 0.014 0.9 0.31 0.28 0.28 3.23 0.90 6.540.1380.250 3.00 8.33 5.80 0.18CB2 CB60.31 5.60 170 126.5 0.014 0.9 0.62 0.28 0.56 3.18 1.77 7.830.2270.321 3.85 9.97 8.04 0.35CB6 CB70.23 5.43 44 126.5 0.014 0.9 0.54 0.21 0.49 3.18 1.54 7.710.2000.300 3.60 9.82 7.61 0.10CB7 VAULT0.00 5.04 62 126.6 0.014 0.9 0.54 0.00 0.49 3.15 1.53 7.420.2060.305 3.66 9.46 7.40 0.14EX. CB569 VAULT0.17 2.55 16 126.3 0.014 0.9 0.17 0.15 0.15 3.23 0.49 5.280.0940.205 2.46 6.73 4.14 0.06CB4 VAULT0.31 1.39 3 126.3 0.014 0.9 0.31 0.28 0.28 3.23 0.90 3.900.2310.325 3.90 4.97 4.03 0.01CB5 VAULT0.04 2.53 16 126.3 0.014 0.9 0.04 0.04 0.04 3.23 0.12 5.260.0220.104 1.25 6.70 2.75 0.10RDCO8 CB100.03 7.48 44 86.3 0.014 0.9 0.03 0.03 0.03 3.23 0.09 3.070.0280.117 0.94 8.80 3.91 0.19CB10 CB110.00 4.54 46 86.5 0.014 0.9 0.03 0.00 0.03 3.17 0.09 2.390.0360.132 1.05 6.85 3.05 0.25CB11 VAULT0.00 1.00 30 86.7 0.014 0.9 0.03 0.00 0.03 3.10 0.08 1.120.0750.185 1.48 3.22 1.83 0.27VAULT MWS0.001.372012-- 0.014 -- -- -- -- -- 0.10 3.870.026RDCO #6 RDCO #50.12 1.00 37 86.3 0.014 0.6 0.123 0.07 0.07 3.23 0.24 1.120.2130.310 2.48 3.22 2.54 0.24RDCO #5 RDCO #40.30 1.00 101 86.5 0.014 0.9 0.423 0.27 0.34 3.16 1.09 1.120.9680.788 6.30 3.22 3.63 0.46RDCO #1 RDCO #20.09 1.00 52 86.3 0.014 0.9 0.09 0.08 0.08 3.23 0.26 1.120.2330.327 2.61 3.22 2.62 0.33RDCO #2 RDCO #30.14 0.99 26 86.6 0.014 0.9 0.23 0.13 0.21 3.13 0.65 1.120.5810.546 4.37 3.20 3.31 0.13RDCO #3 RDCO #40.09 0.99 23 86.8 0.014 0.9 0.32 0.08 0.29 3.09 0.89 1.120.7980.675 5.40 3.20 3.55 0.11RDCO #4 VAULT0.221.0037126.6 0.014 0.9 0.22 0.20 0.20 3.13 2.60 3.310.7850.667 8.00 4.21 4.66 0.13Site Detention VaultBARGHAUSEN CONSULTING ENGINEERS - PIPE FLOW CALCULATORusing the Rational Method & Manning FormulaRoof Detention Vault** Flow from Vault to MWS is specified as 0.10 cfs, which isthe 100-year release rate from the site detention vault.The design flow of the pipes (Qd), which is the runoff from the 100-yearevent, is less than the full capacity flow for the pipes in each reach (Qf).
NORTH ACCESS ROAD
CONVEYANCE BASIN MAP
SDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSDSD
SDSDSDSD CB#1 TYPE 1,W/ HERRINGBONE GRATECB#6 TYPE 1, W/ VANED GRATECB#5 TYPE 1, W/ SOLID LOCKING LIDCB#2 TYPE 1,W/ HERRINGBONE GRATECB#3 TYPE 1,W/ HERRINGBONE GRATECB#7 TYPE 1,W/ VANED GRATECB#8 TYPE 1,W/ VANED GRATECB#4 TYPE 1,W/ VANED GRATEMODULAR WETLAND #2UW MEDICINE - VALLEY MEDICAL CENTERNORTH ROAD RELOCATIONKnow what'sbelow.before you dig.CallR
NORTH ACCESS ROAD CONVEYANCE
CALCULATIONS
i will review these when i review
the talbot road plans. i will
provide any comments by email.
KING COUNTY DESIGN FOR 100YEAR STORMJOB NAME: VMC MOBNOTE: ENTER DEFAULTS AND STORM DATA BEFORE BEGINNING JOB#: 18092 DEFAULTS C=0.9n=0.014FILE NO.: 18092-North Access Road Conveyance Calcs-2017-09-27 d=12Tc=6.3`A= Contributing Area (Ac)Qd= Design Flow (cfs)COEFFICIENTS FOR THE RATIONAL METHOD "Ir"-EQUATIONC= Runoff Coefficient Qf= Full Capacity Flow (cfs)STORMAr BrTc= Time of Concentration (min)Vd= Velocity at Design Flow (fps)2YR1.580.58I= Intensity at Tc (in/hr)Vf= Velocity at Full Flow (fps)10YR2.440.64PRECIP=3.95d= Diameter of Pipe (in) s= Slope of pipe (%) 25YR 2.66 0.65 Ar=2.61L= Length of Pipe (ft)n= Manning Roughness Coefficient50YR2.750.65Br=0.63D= Water Depth at Qd (in)Tt= Travel Time at Vd (min)100YR2.610.63FROM TO A s L d Tc n C SUM A A*C SUM A*C I Qd QfQd/QfD/d D Vf Vd Tt=================================================================================================================================CB1 CB20.33 0.50 73 126.3 0.014 0.9 0.33 0.30 0.30 3.23 0.96 2.340.4110.447 5.37 2.98 2.84 0.43CB2 CB40.13 2.92 50 126.3 0.014 0.9 0.13 0.12 0.41 3.23 1.34 5.650.2370.329 3.95 7.20 5.88 0.14CB3 CB40.03 6.37 46 126.3 0.014 0.9 0.03 0.03 0.03 3.23 0.09 8.350.0100.067 0.80 10.64 3.31 0.23CB4 CB50.06 4.20 48 126.4 0.014 0.9 0.06 0.05 0.50 3.19 1.58 6.780.2330.326 3.91 8.64 7.02 0.11CB6 CB50.05 0.50 9 126.3 0.014 0.9 0.05 0.05 0.05 3.23 0.15 2.340.0620.170 2.04 2.98 1.64 0.09CB5 CB80.00 5.92 25 1213.1 0.014 0.9 0.00 0.00 0.54 2.04 1.10 8.050.1370.249 2.99 10.25 7.11 0.06CB7 CB80.08 0.99 22 1213.2 0.014 1.9 0.08 0.15 0.15 2.03 0.31 3.290.0940.205 2.46 4.19 2.58 0.14CB8 VAULT0.04 0.50 37 1213.2 0.014 2.9 0.04 0.12 0.81 2.02 1.64 2.340.7000.616 7.40 2.98 3.23 0.19VAULT MWS-1.00412- 0.014 - - - - - 0.02 3.310.0050.053 0.63 4.21 1.13 0.06BARGHAUSEN CONSULTING ENGINEERS - PIPE FLOW CALCULATORusing the Rational Method & Manning FormulaQd from detentionvault is the full 2 yearrelease rate from thefacility. See WWHMModel.The design flow of the pipes (Qd), which isthe runoff from the 100-year event, is lessthan the full capacity flow for the pipes ineach reach.
Tab 6.0
8410 154th Avenue NE
Redmond, Washington 98052
425.861.6000
August 25, 2017
Valley Medical Center
400 South 43rd Street
Renton, Washington 98005
Attention: Becky Hardi
Subject: Addendum to Geotechnical Report No. 2
Valley Medical Center – Medical Office Building
400 South 43rd Street
Renton, Washington
GeoEngineers File No. 2202-024-00
INTRODUCTION
The purpose of this letter is to provide updated recommendations regarding temporary slope cuts to
complete the construction of the proposed new Medical Office Building (MOB) for the Valley Medical Center
campus in Renton, Washington. This letter is being submitted as Addendum No. 2 to our geotechnical
report dated September 16, 2016, and is subject to the limitations described therein.
Our project understanding is based on discussions with the project architect (NBBJ), civil engineer
(Barghausen Consulting Engineers), and representatives of Valley Medical Center. We understand steeper
slope cuts are required along portions of the site to complete the excavation for the below grade portions
of the building and utilidor.
CONCLUSIONS AND RECOMMENDATIONS
General
GeoEngineers is currently the geotechnical special inspector for the new parking garage that is being
constructed in the northeast portion of the site and is directly north of the proposed new MOB. During
shoring construction, we observed the temporary excavation at the site and based on our observations the
soil conditions are very similar to those observed in the borings for the MOB and consisted of fill overlying
dense to very dense glacially consolidated soils. Based on our observations for the parking garage, the
glacially consolidated soils are considered competent and capable of being excavated steeper than a
1 Horizontal (H):1 Vertical (V) slope without increased instability and sloughing.
Valley Medical Center. | August 25, 2017 Page 2
File No. 2202-024-00
Temporary Slopes
Temporary slopes may be used around the site where space allows. Based on our observations of the soils
on the adjacent site to the north and the boring logs completed onsite, we recommend that temporary
slopes constructed in the glacially consolidated soils be inclined at ¾H:1V. Additional measures, such as
plastic sheet, may be required to protect the slope for precipitation. This will be evaluated by a
representative from GeoEngineers during excavation. Temporary slopes within the fill will still need to be
inclined at 1½H:1V. Flatter slopes may be necessary if seepage is present on the face of the cut slopes or
if localized sloughing occurs. For open cuts at the site, we recommend that:
■ no traffic, construction equipment, stockpiles or building supplies be allowed at the top of the cut
slopes within a distance of at least 5 feet from the top of the cut;
■ exposed soil along the slope be protected from surface erosion by using waterproof tarps or plastic
sheeting;
■ construction activities be scheduled so that the length of time the temporary cut is left open is
reduced to the extent practicable;
■ erosion control measures be implemented as appropriate such that runoff from the site is reduced
to the extent practicable;
■ surface water be diverted away from the slope;
■ the general condition of the slopes be observed periodically by the geotechnical engineer to confirm
adequate stability; and
■ because the contractor has control of the construction operations, the contractor should be made
responsible for the stability of cut slopes, as well as the safety of the excavations. Temporary slopes
must conform to applicable local, state and federal safety regulations.
LIMITATIONS
We have prepared this letter for Valley Medical Center and members of the design team for use in design
of the Valley Medical Center MOB project in Renton, Washington. The data should be provided to
prospective contractors for their bidding and estimating purposes, but our report and interpretations should
not be construed as a warranty of the subsurface conditions.
Within the limitations of scope, schedule and budget, our services have been executed in accordance with
generally accepted practices in the field of geotechnical engineering in this area at the time this report was
prepared. No warranty or other conditions, express or implied, should be understood.
Please refer to the appendix in our September 16, 2016 geotechnical report titled “Report Limitations and
Guidelines for Use” for additional information pertaining to use of this letter.
Tab 7.0
7.0 OTHER PERMITS
Other permits for this site include:
NPDES General Permit from the Department of Ecology for sites with disturbance over 1 acre
Separate buildings permits are required for each detention vault.
Separate permit for shoring (if required).
Tab 8.0
i 18092-R-CSWPPP-2017-09-18
Stormwater Pollution Prevention Plan
For
Valley Medical Center Medical Office Building Addition
Prepared For
Valley Medical Center
Owner Developer Operator/Contractor
Valley Medical Center Valley Medical Center T.B.D.
Project Site Location
Valley Medical Center Complex
Renton, Washington
Certified Erosion and Sediment Control Lead
T.B.D.
SWPPP Prepared By
Barghausen Consulting Engineers, Inc.
18215 72nd Avenue South
Kent, WA 98032
(425) 251-6222
Ali Sadr, Senior Project Engineer
SWPPP Preparation Date
June 12, 2017
Approximate Project Construction Dates
March 2018
March 2019
Stormwater Pollution Prevention Plan
Contents
1.0 Introduction ..................................................................................................................... 1
2.0 Site Description ............................................................................................................... 3
2.1 Existing Conditions .............................................................................................. 3
2.2 Proposed Construction Activities .......................................................................... 3
3.0 Construction Stormwater BMPs ....................................................................................... 5
3.1 The 14 BMP Elements ......................................................................................... 5
3.1.1 Element #1 – Mark Clearing Limits .......................................................... 5
3.1.2 Element #2 – Establish Construction Access .......................................... 5
3.1.3 Element #3 – Control Flow Rates ............................................................ 6
3.1.4 Element #4 – Install Sediment Controls ................................................... 6
3.1.5 Element #5 – Stabilize Soils .................................................................... 7
3.1.6 Element #6 – Protect Slopes ................................................................... 8
3.1.7 Element #7 – Protect Drain Inlets ............................................................ 8
3.1.8 Element #8 – Stabilize Channels and Outlets .......................................... 9
3.1.9 Element #9 – Control Pollutants .............................................................. 9
3.1.10 Element #10 – Control Dewatering ........................................................ 10
3.1.11 Element #11 – Maintain BMPs .............................................................. 11
3.1.12 Element #12 – Manage the Project ....................................................... 11
3.1.13 Element #13 – Construction Stormwater Chemical Treatment .............. 13
3.1.14 Element #14 – Construction Stormwater Filtration ................................. 19
3.2 Site Specific BMPs ............................................................................................. 20
4.0 Construction Phasing and BMP Implementation ............................................................ 21
5.0 Pollution Prevention Team ............................................................................................. 22
5.1 Roles and Responsibilities ................................................................................. 22
5.2 Team Members .................................................................................................. 23
6.0 Site Inspections and Monitoring ..................................................................................... 24
6.1 Site Inspection ................................................................................................... 24
6.1.1 Site Inspection Frequency ..................................................................... 24
6.1.2 Site Inspection Documentation .............................................................. 24
6.2 Stormwater Quality Monitoring ........................................................................... 25
6.2.1 Turbidity Sampling ................................................................................ 25
6.2.2 pH Sampling ......................................................................................... 26
7.0 Reporting and Recordkeeping ....................................................................................... 27
7.1 Recordkeeping ................................................................................................... 27
7.1.1 Site Log Book ........................................................................................ 27
7.1.2 Records Retention ................................................................................ 27
7.1.3 Access to Plans and Records ................................................................ 27
7.1.4 Updating the SWPPP ............................................................................ 27
7.2 Reporting ........................................................................................................... 28
7.2.1 Discharge Monitoring Reports ............................................................... 28
7.2.2 Notification of Noncompliance ............................................................... 28
Stormwater Pollution Prevention Plan
Appendix A Site Plans
Appendix B Construction BMPs
Appendix C Alternative BMPs
Appendix D General Permit
Appendix E Site Inspection Forms (and Site Log)
Appendix F Engineering Calculations
Stormwater Pollution Prevention Plan
1.0 Introduction
This Stormwater Pollution Prevention Plan (SWPPP) has been prepared as part of the
NPDES stormwater permit requirements for the Valley Medical Center Medical Office
Building Addition project in Renton, Washington. The proposed site is located on the
Valley Medical Center Complex in Renton, Washington.
Construction activities will include the addition of one building, asphalt parking lots,
landscaping, utility work, including power, telephone, gas, cable television, water, sewer, and
storm appurtenances with catch basin collection, pipe conveyance, stormwater quality, and flow
control facilities, etc. The purpose of this SWPPP is to describe the proposed construction
activities and all temporary and permanent erosion and sediment control (TESC)
measures, pollution prevention measures, inspection/monitoring activities, and
recordkeeping that will be implemented during the proposed construction project. The
objectives of the SWPPP are to:
1. Implement Best Management Practices (BMPs) to prevent erosion
and sedimentation, and to identify, reduce, eliminate or prevent
stormwater contamination and water pollution from construction
activity.
2. Prevent violations of surface water quality, ground water quality, or
sediment management standards.
3. Prevent, during the construction phase, adverse water quality
impacts including impacts on beneficial uses of the receiving water
by controlling peak flow rates and volumes of stormwater runoff at
the Permittee’s outfalls and downstream of the outfalls.
This SWPPP was prepared using the Ecology SWPPP Template downloaded from the
Ecology website. This SWPPP was prepared based on the requirements set forth in the
Construction Stormwater General Permit, Stormwater Management Manual for Western
Washington. The report is divided into seven main sections with several appendices that
include stormwater related reference materials. The topics presented in the each of the main
sections are:
Section 1 – INTRODUCTION. This section provides a summary
description of the project, and the organization of the SWPPP document.
Section 2 – SITE DESCRIPTION. This section provides a detailed
description of the existing site conditions, proposed construction activities,
and calculated stormwater flow rates for existing conditions and
post-construction conditions.
Section 3 – CONSTRUCTION BMPs. This section provides a detailed
description of the BMPs to be implemented based on the 12 required
elements of the SWPPP.
Stormwater Pollution Prevention Plan
Section 4 – CONSTRUCTION PHASING AND BMP IMPLEMENTATION.
This section provides a description of the timing of the BMP
implementation in relation to the project schedule.
Section 5 – POLLUTION PREVENTION TEAM. This section identifies the
appropriate contact names (emergency and non-emergency), monitoring
personnel, and the onsite temporary erosion and sedimentation control
inspector
Section 6 – INSPECTION AND MONITORING. This section provides a
description of the inspection and monitoring requirements such as the
parameters of concern to be monitored, sample locations, sample
frequencies, and sampling methods for all stormwater discharge locations
from the site.
Section 7 – RECORDKEEPING. This section describes the requirements
for documentation of the BMP implementation, site inspections,
monitoring results, and changes to the implementation of certain BMPs
due to site factors experienced during construction.
Supporting documentation and standard forms are provided in the following Appendices:
Appendix A – Site Plans
Appendix B – Construction BMPs
Appendix C – Alternative BMPs
Appendix D – General Permit
Appendix E – Site Inspection Forms (and Site Log)
Appendix F – Engineering Calculations
Stormwater Pollution Prevention Plan
2.0 Site Description
2.1 Existing Conditions
Since the City has indicated that Conservation Flow Control is the required flow control menu to
be followed for this site, the pre-developed condition regardless of the existing land cover must
be modeled as till forest. However, there are portions of the existing pre developed conditions
that consist of impervious surface as well as landscape areas. These will all be ripped out with
new impervious surface to replace most of the existing development on the site. In addition,
approximately 0.1 acre of new thickly vegetated landscape areas will be also added.
2.2 Proposed Construction Activities
The total area of redevelopment on this project site, including new landscape area, totals 1.96
acres. The landscaping total is 0.24 acres, with total impervious including building and parking
of 1.72 acres.
The project site is located within the Northeast quarter of Section 31, Township 23 North, Range
5 East, Willamette Meridian, City of Renton, King County, Washington. More particularly, the
site lies slightly to the west of Talbot Road South, north of South 43rd Street, and easterly of
SR-167.
The project site drains to the west down a drive aisle within an existing pipe conveyance system
which is well documented through recent projects having occurred on this drive aisle, and
courses through a biofiltration swale at the northwest end of the Valley Medical Center and
discharges from that swale into Panther Creek located on the north side of Valley Medical
Center. Panther Creek drains northerly from that point through the Panther Creek wetlands area
of the City of Renton with an ultimate discharge to Springbrook Creek.
For purposes of sizing flow control and water quality, the City of Renton has indicated that the
duration standard, predeveloped forested, is the required means of providing flow control for this
project, with Enhanced Water Quality being the water quality menu to be followed. The proposal
for this development is to provide an underground detention vault sized for the area contributing
from the roof with a pre-developed condition of till forest, the remaining area draining to a site
detention vault (mostly impervious) with some landscaping totaling 1.15 acres.
Downstream of the detention vault will be located a modular wetland vault which is a proprietary
device with General Use Level Designation for Basic, Enhanced, and Phosphorus Water Quality
treatment capabilities through the Department of Ecology. The City of Renton is well aware of
the capability of these modular wetland systems as they have recently been reviewed and
approved on the Renton Marriott Inn Residence Inn project also located in Renton.
At this time this project is seeking SEPA Review determination. With the Final Technical
Information Report prepared for this project, the conveyance systems on site will be sized as
well as providing a Bond Quantity Worksheet, a Declaration of Covenant, and an Operation and
Maintenance Manual.
Stormwater Pollution Prevention Plan
Construction activities will include site preparation, TESC installation, building construction,
stormwater and utility appurtenance installation, and asphalt paving. The schedule and phasing
of BMPs during construction is provided in Section 4.0.
Stormwater runoff rates and volumes were calculated using the KCRTS hydrology model and
the detention vault was sized by routing the entire range of historic storm events.
The following summarizes details regarding site areas:
Total site area: 1.96 acres
Percent impervious area before construction: 90%
Percent impervious area after construction: 85%
Disturbed area during construction: 2.0 acres
Disturbed area that is characterized as impervious (i.e., access
roads, staging, parking): 0.35 acre
All stormwater flow calculations are provided in Appendix F.
Stormwater Pollution Prevention Plan
3.0 Construction Stormwater BMPs
3.1 The 14 BMP Elements
3.1.1 Element #1 – Mark Clearing Limits
To protect adjacent properties and to reduce the area of soil exposed to construction, the limits
of construction will be clearly marked before land-disturbing activities begin. Areas that are to be
preserved, as well as all sensitive areas and their buffers, shall be clearly delineated, both in the
field and on the plans. The BMPs relevant to marking the clearing limits that will be applied for
this project include:
High Visibility Plastic or Metal Fence (BMP C103)
The clearing limits shall be as shown on the plans and all vegetation outside of the clearing
limits preserved.
Alternate BMPs for marking clearing limits are included in Appendix C as a quick reference tool
for the onsite inspector in the event the BMP(s) listed above are deemed ineffective or
inappropriate during construction to satisfy the requirements set forth in the General NPDES
Permit (Appendix D). To avoid potential erosion and sediment control issues that may cause a
violation(s) of the NPDES Construction Stormwater permit (as provided in Appendix D), the
Certified Erosion and Sediment Control Lead will promptly initiate the implementation of one or
more of the alternative BMPs listed in Appendix C after the first sign that existing BMPs are
ineffective or failing.
3.1.2 Element #2 – Establish Construction Access
Construction access or activities occurring on unpaved areas shall be minimized, yet where
necessary, access points shall be stabilized to minimize the tracking of sediment onto public
roads. Street sweeping and street cleaning shall be employed to prevent sediment from entering
state waters. All wash wastewater shall be controlled on site. The specific BMPs related to
establishing construction access that will be used on this project include:
The roads shall be swept daily should sediment collect on them.
Alternate construction access BMPs are included in Appendix C as a quick reference tool for the
onsite inspector in the event the BMP(s) listed above are deemed ineffective or inappropriate
during construction to satisfy the requirements set forth in the General NPDES Permit
(Appendix D). To avoid potential erosion and sediment control issues that may cause a
violation(s) of the NPDES Construction Stormwater permit (as provided in Appendix D), the
Certified Erosion and Sediment Control Lead will promptly initiate the implementation of one or
more of the alternative BMPs listed in Appendix C after the first sign that existing BMPs are
ineffective or failing.
Stormwater Pollution Prevention Plan
3.1.3 Element #3 – Control Flow Rates
In order to protect the properties and waterways downstream of the project site, stormwater
discharges from the site will be controlled by construction of a sump area pumped to Baker
Tanks as one of the first items of construction.
Alternate flow control BMPs are included in Appendix C as a quick reference tool for the onsite
inspector in the event the BMP(s) listed above are deemed ineffective or inappropriate during
construction to satisfy the requirements set forth in the General NPDES Permit (Appendix D).
To avoid potential erosion and sediment control issues that may cause a violation(s) of the
NPDES Construction Stormwater permit (as provided in Appendix D), the Certified Erosion and
Sediment Control Lead will promptly initiate the implementation of one or more of the alternative
BMPs listed in Appendix C after the first sign that existing BMPs are ineffective or failing.
The project site is located west of the Cascade Mountain Crest. As such, the project must
comply with Minimum Requirement 7 (Ecology 2005).
In general, discharge rates of stormwater from the site will be controlled where increases in
impervious area or soil compaction during construction could lead to downstream erosion, or
where necessary to meet local agency stormwater discharge requirements (e.g., discharge to
combined sewer systems).
3.1.4 Element #4 – Install Sediment Controls
All stormwater runoff from disturbed areas shall pass through an appropriate sediment removal
BMP before leaving the construction site or prior to being discharged to the downstream
drainage course. The specific BMPs to be used for controlling sediment on this project include:
Silt Fence (BMP C233)
Baker Tanks
Sediment Traps (See section D.2.1.5.1 of RSWDM, 2017).
A silt fence shall be installed along the downstream perimeter of the proposed site. Alternate
sediment control BMPs are included in Appendix C as a quick reference tool for the onsite
inspector in the event the BMP(s) listed above are deemed ineffective or inappropriate during
construction to satisfy the requirements set forth in the General NPDES Permit (Appendix D).
To avoid potential erosion and sediment control issues that may cause a violation(s) of the
NPDES Construction Stormwater permit (as provided in Appendix D), the Certified Erosion and
Sediment Control Lead will promptly initiate the implementation of one or more of the alternative
BMPs listed in Appendix C after the first sign that existing BMPs are ineffective or failing.
In addition, sediment will be removed from paved areas in and adjacent to construction work
areas manually or using mechanical sweepers, as needed, to minimize tracking of sediments on
vehicle tires away from the site and to minimize washoff of sediments from adjacent streets in
runoff.
Stormwater Pollution Prevention Plan
Whenever possible, sediment-laden water shall be discharged into onsite, relatively level,
vegetated areas (BMP C240 paragraph 5, page 4-102).
In some cases, sediment discharge in concentrated runoff can be controlled using permanent
stormwater BMPs (e.g., infiltration swales, ponds, trenches). Sediment loads can limit the
effectiveness of some permanent stormwater BMPs, such as those used for infiltration or
biofiltration; however, those BMPs designed to remove solids by settling (wet ponds or sediment
ponds) can be used during the construction phase. When permanent stormwater BMPs will be
used to control sediment discharge during construction, the structure will be protected from
excessive sedimentation with adequate erosion and sediment control BMPs. Any accumulated
sediment shall be removed after construction is complete and the remainder of the site has
been stabilized.
The following BMPs will be implemented as end-of-pipe sediment controls as required to meet
permitted turbidity limits in the site discharge(s). Prior to the implementation of these
technologies, sediment sources and erosion control and soil stabilization BMP efforts will be
maximized to reduce the need for end-of-pipe sedimentation controls.
Baker Tanks with Sand Filtration
Construction Stormwater Filtration (BMP C251)
Construction Stormwater Chemical Treatment (BMP C 250) (implemented
only with prior written approval from Ecology).
3.1.5 Element #5 – Stabilize Soils
Exposed and unworked soils shall be stabilized with the application of effective BMPs to prevent
erosion throughout the life of the project. The specific BMPs for soil stabilization that shall be
used on this project include:
Temporary and Permanent Seeding (BMP C120)
Mulching (BMP C121)
Dust Control (BMP C 140)
Seeding shall occur on all areas to remain unworked pursuant to below. Dust shall be controlled
if construction occurs during the summer. Alternate soil stabilization BMPs are included in
Appendix C as a quick reference tool for the onsite inspector in the event the BMP(s) listed
above are deemed ineffective or inappropriate during construction to satisfy the requirements
set forth in the General NPDES Permit (Appendix D). To avoid potential erosion and sediment
control issues that may cause a violation(s) of the NPDES Construction Stormwater permit (as
provided in Appendix D), the Certified Erosion and Sediment Control Lead will promptly initiate
the implementation of one or more of the alternative BMPs listed in Appendix C after the first
sign that existing BMPs are ineffective or failing.
The project site is located west of the Cascade Mountain Crest. As such, no soils shall remain
exposed and unworked for more than 7 days during the dry season (May 1 to September 30)
Stormwater Pollution Prevention Plan
and 2 days during the wet season (October 1 to April 30). Regardless of the time of year, all
soils shall be stabilized at the end of the shift before a holiday or weekend if needed based on
weather forecasts.
In general, cut and fill slopes will be stabilized as soon as possible and soil stockpiles will be
temporarily covered with plastic sheeting. All stockpiled soils shall be stabilized from erosion,
protected with sediment trapping measures, and where possible, be located away from storm
drain inlets, waterways, and drainage channels.
3.1.6 Element #6 – Protect Slopes
All cut and fill slopes will be designed, constructed, and protected in a manner that minimizes
erosion. The following specific BMPs will be used to protect slopes for this project:
Temporary and Permanent Seeding (BMP C 120)
Temporary and permanent seeding shall be used at all exposed areas pursuant to the prior
mentioned schedule (seasonal restrictions).
Alternate slope protection BMPs are included in Appendix C as a quick reference tool for the
onsite inspector in the event the BMP(s) listed above are deemed ineffective or inappropriate
during construction to satisfy the requirements set forth in the General NPDES Permit
(Appendix D). To avoid potential erosion and sediment control issues that may cause a
violation(s) of the NPDES Construction Stormwater permit (as provided in Appendix D), the
Certified Erosion and Sediment Control Lead will promptly initiate the implementation of one or
more of the alternative BMPs listed in Appendix C after the first sign that existing BMPs are
ineffective or failing.
3.1.7 Element #7 – Protect Drain Inlets
All storm drain inlets and culverts made operable during construction shall be protected to
prevent unfiltered or untreated water from entering the drainage conveyance system. However,
the first priority is to keep all access roads clean of sediment and keep street wash water
separate from entering storm drains until treatment can be provided. Storm Drain Inlet
Protection (BMP C220) will be implemented for all drainage inlets and culverts that could
potentially be impacted by sediment-laden runoff on and near the project site. The following inlet
protection measures will be applied on this project:
Excavated Drop Inlet Protection
Block and Gravel Drop Inlet Protection
Gravel and Wire Drop Inlet Protection
Catch Basin Filters
Culvert Inlet Sediment Trap
Stormwater Pollution Prevention Plan
If the BMP options listed above are deemed ineffective or inappropriate during construction to
satisfy the requirements set forth in the General NPDES Permit (Appendix D), or if no BMPs are
listed above but deemed necessary during construction, the Certified Erosion and Sediment
Control Lead shall implement one or more of the alternative BMP inlet protection options listed
in Appendix C.
3.1.8 Element #8 – Stabilize Channels and Outlets
Where site runoff is to be conveyed in channels, or discharged to a stream or some other
natural drainage point, efforts will be taken to prevent downstream erosion. The specific BMPs
for channel and outlet stabilization that shall be used on this project include:
Site runoff shall be discharged to Baker Tanks
Alternate channel and outlet stabilization BMPs are included in Appendix C as a quick reference
tool for the onsite inspector in the event the BMP(s) listed above are deemed ineffective or
inappropriate during construction to satisfy the requirements set forth in the General NPDES
Permit (Appendix D). To avoid potential erosion and sediment control issues that may cause a
violation(s) of the NPDES Construction Stormwater permit (as provided in Appendix D), the
Certified Erosion and Sediment Control Lead will promptly initiate the implementation of one or
more of the alternative BMPs listed in Appendix C after the first sign that existing BMPs are
ineffective or failing.
The project site is located west of the Cascade Mountain Crest. As such, all temporary on-site
conveyance channels shall be designed, constructed, and stabilized to prevent erosion from the
expected peak 10 minute velocity of flow from a Type 1A, 10-year, 24-hour recurrence interval
storm for the developed condition. Alternatively, the 10-year, 1-hour peak flow rate indicated by
an approved continuous runoff simulation model, increased by a factor of 1.6, shall be used.
Stabilization, including armoring material, adequate to prevent erosion of outlets, adjacent
streambanks, slopes, and downstream reaches shall be provided at the outlets of all
conveyance systems.
3.1.9 Element #9 – Control Pollutants
All pollutants, including waste materials and demolition debris, that occur onsite shall be
handled and disposed of in a manner that does not cause contamination of stormwater. Good
housekeeping and preventative measures will be taken to ensure that the site will be kept clean,
well organized, and free of debris. If required, BMPs to be implemented to control specific
sources of pollutants are discussed below. Vehicles, construction equipment, and/or petroleum
product storage/dispensing:
All vehicles, equipment, and petroleum product storage/dispensing areas
will be inspected regularly to detect any leaks or spills, and to identify
maintenance needs to prevent leaks or spills.
On-site fueling tanks and petroleum product storage containers shall
include secondary containment.
Stormwater Pollution Prevention Plan
Spill prevention measures, such as drip pans, will be used when
conducting maintenance and repair of vehicles or equipment.
In order to perform emergency repairs on site, temporary plastic will be
placed beneath and, if raining, over the vehicle.
Contaminated surfaces shall be cleaned immediately following any
discharge or spill incident.
Demolition:
Dust released from demolished sidewalks, buildings, or structures will be
controlled using Dust Control measures (BMP C140).
Storm drain inlets vulnerable to stormwater discharge carrying dust, soil,
or debris will be protected using Storm Drain Inlet Protection (BMP C220
as described above for Element 7).
Process water and slurry resulting from sawcutting and surfacing
operations will be prevented from entering the waters of the State by
implementing Sawcutting and Surfacing Pollution Prevention measures
(BMP C152).
Concrete and grout:
Process water and slurry resulting from concrete work will be prevented
from entering the waters of the State by implementing Concrete Handling
measures (BMP C151).
3.1.10 Element #10 – Control Dewatering
All dewatering water from open cut excavation, tunneling, foundation work, trench, or
underground vaults shall be discharged into a controlled conveyance system prior to discharge
to the downstream drainage course. Channels will be stabilized, per Element #8. Clean, non-
turbid dewatering water will not be routed through stormwater sediment ponds, and will be
discharged to systems tributary to the receiving waters of the State in a manner that does not
cause erosion, flooding, or a violation of State water quality standards in the receiving water.
Highly turbid dewatering water from soils known or suspected to be contaminated, or from use
of construction equipment, will require additional monitoring and treatment as required for the
specific pollutants based on the receiving waters into which the discharge is occurring. Such
monitoring is the responsibility of the contractor.
However, the dewatering of soils known to be free of contamination will trigger BMPs to trap
sediment and reduce turbidity. At a minimum, geotextile fabric socks/bags/cells will be used to
filter this material. Other BMPs to be used for sediment trapping and turbidity reduction include
the following:
Concrete Handling (BMP C151)
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Concrete shall be handled pursuant to BMP C151 wherever and whenever concrete is mixed
and poured at the project site.
Alternate dewatering control BMPs are included in Appendix C as a quick reference tool for the
onsite inspector in the event the BMP(s) listed above are deemed ineffective or inappropriate
during construction to satisfy the requirements set forth in the General NPDES Permit
(Appendix D). To avoid potential erosion and sediment control issues that may cause a
violation(s) of the NPDES Construction Stormwater permit (as provided in Appendix D), the
Certified Erosion and Sediment Control Lead will promptly initiate the implementation of one or
more of the alternative BMPs listed in Appendix C after the first sign that existing BMPs are
ineffective or failing.
3.1.11 Element #11 – Maintain BMPs
All temporary and permanent erosion and sediment control BMPs shall be maintained and
repaired as needed to assure continued performance of their intended function. Maintenance
and repair shall be conducted in accordance with each particular BMP's specifications. Visual
monitoring of the BMPs will be conducted at least once every calendar week and within 24
hours of any rainfall event that causes a discharge from the site. If the site becomes inactive,
and is temporarily stabilized, the inspection frequency will be reduced to once every month.
All temporary erosion and sediment control BMPs shall be removed within 30 days after the final
site stabilization is achieved or after the temporary BMPs are no longer needed. Trapped
sediment shall be removed or stabilized on site. Disturbed soil resulting from removal of BMPs
or vegetation shall be permanently stabilized.
3.1.12 Element #12 – Manage the Project
Erosion and sediment control BMPs for this project have been designed based on the following
principles:
Design the project to fit the existing topography, soils, and drainage
patterns.
Emphasize erosion control rather than sediment control.
Minimize the extent and duration of the area exposed.
Keep runoff velocities low.
Retain sediment on site.
Thoroughly monitor site and maintain all ESC measures.
Schedule major earthwork during the dry season.
In addition, project management will incorporate the key components listed below:
As this project site is located west of the Cascade Mountain Crest, the project will be managed
according to the following key project components:
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Phasing of Construction
The construction project is being phased to the extent practicable in order
to prevent soil erosion, and, to the maximum extent possible, the
transport of sediment from the site during construction.
Revegetation of exposed areas and maintenance of that vegetation shall
be an integral part of the clearing activities during each phase of
construction, per the Scheduling BMP (C 162).
Seasonal Work Limitations
From October 1 through April 30, clearing, grading, and other soil
disturbing activities shall only be permitted if shown to the satisfaction of
the local permitting authority that silt-laden runoff will be prevented from
leaving the site through a combination of the following:
Site conditions including existing vegetative coverage, slope, soil type,
and proximity to receiving waters; and
Limitations on activities and the extent of disturbed areas; and
Proposed erosion and sediment control measures.
Based on the information provided and/or local weather conditions, the
local permitting authority may expand or restrict the seasonal limitation on
site disturbance.
The following activities are exempt from the seasonal clearing and
grading limitations:
Routine maintenance and necessary repair of erosion and sediment
control BMPs;
Routine maintenance of public facilities or existing utility structures that do
not expose the soil or result in the removal of the vegetative cover to soil;
and
Activities where there is 100 percent infiltration of surface water runoff
within the site in approved and installed erosion and sediment control
facilities.
Coordination with Utilities and Other Jurisdictions
Care has been taken to coordinate with utilities, other construction
projects, and the local jurisdiction in preparing this SWPPP and
scheduling the construction work.
Inspection and Monitoring
All BMPs shall be inspected, maintained, and repaired as needed to
assure continued performance of their intended function. Site inspections
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shall be conducted by a person who is knowledgeable in the principles
and practices of erosion and sediment control. This person has the
necessary skills to:
Assess the site conditions and construction activities that could impact
the quality of stormwater, and
Assess the effectiveness of erosion and sediment control measures used
to control the quality of stormwater discharges.
A Certified Erosion and Sediment Control Lead shall be on-site or on-call
at all times.
Whenever inspection and/or monitoring reveals that the BMPs identified
in this SWPPP are inadequate, due to the actual discharge of or potential
to discharge a significant amount of any pollutant, appropriate BMPs or
design changes shall be implemented as soon as possible.
Maintaining an Updated Construction SWPPP
This SWPPP shall be retained on-site or within reasonable access to the
site.
The SWPPP shall be modified whenever there is a change in the design,
construction, operation, or maintenance at the construction site that has,
or could have, a significant effect on the discharge of pollutants to waters
of the state.
The SWPPP shall be modified if, during inspections or investigations
conducted by the owner/operator, or the applicable local or state
regulatory authority, it is determined that the SWPPP is ineffective in
eliminating or significantly minimizing pollutants in stormwater discharges
from the site. The SWPPP shall be modified as necessary to include
additional or modified BMPs designed to correct problems identified.
Revisions to the SWPPP shall be completed within seven (7) days
following the inspection.
3.1.13 Element #13 – Construction Stormwater Chemical
Treatment
Turbidity is difficult to control once fine particles are suspended in stormwater runoff from a
construction site. Sedimentation ponds are effective at removing larger particulate matter by
gravity settling, but are ineffective at removing smaller particulates such as clay and fine silt.
Sediment ponds are typically designed to remove sediment no smaller than medium silt
(0.02 mm). Chemical treatment may be used to reduce the turbidity of stormwater runoff.
Chemical treatment can reliably provide exceptional reductions of turbidity and associated
pollutants. Very high turbidities can be reduced to levels comparable to what is found in streams
during dry weather. Traditional BMPs used to control soil erosion and sediment loss from sites
under development may not be adequate to ensure compliance with the water quality standard
for turbidity in the receiving water. Chemical treatment may be required to protect streams from
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The proposed maximum dosage shall be at least a factor of five lower
than the no observed effects concentration (NOEC).
The approval of a proposed treatment chemical shall be conditional,
subject to full-scale bioassay monitoring of treated stormwater at the
construction site where the proposed treatment chemical is to be used.
Treatment chemicals that have already passed the above testing protocol
do not need to be reevaluated. Contact the Department of Ecology
Regional Office for a list of treatment chemicals that have been evaluated
and are currently approved for use.
Treatment System Design Considerations
The design and operation of a chemical treatment system should take into consideration the
factors that determine optimum, cost-effective performance. It may not be possible to fully
incorporate all of the classic concepts into the design because of practical limitations at
construction sites. Nonetheless, it is important to recognize the following:
The right chemical must be used at the right dosage. A dosage that is
either too low or too high will not produce the lowest turbidity. There is an
optimum dosage rate. This is a situation where the adage "adding more is
always better" is not the case.
The coagulant must be mixed rapidly into the water to insure proper
dispersion.
A flocculation step is important to increase the rate of settling, to produce
the lowest turbidity, and to keep the dosage rate as low as possible.
Too little energy input into the water during the flocculation phase results
in flocs that are too small and/or insufficiently dense. Too much energy
can rapidly destroy floc as it is formed.
Since the volume of the basin is a determinant in the amount of energy
per unit volume, the size of the energy input system can be too small
relative to the volume of the basin.
Care must be taken in the design of the withdrawal system to minimize
outflow velocities and to prevent floc discharge. The discharge should be
directed through a physical filter such as a vegetated swale that would
catch any unintended floc discharge.
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the impact of turbid stormwater discharges, especially when construction is to proceed through
the wet season.
Formal written approval from Ecology and the Local Permitting Authority is required for
the use of chemical treatment regardless of site size. The intention to use Chemical
Treatment shall be indicated on the Notice of Intent for coverage under the General
Construction Permit. Chemical treatment systems should be designed as part of the
Construction SWPPP, not after the fact. Chemical treatment may be used to correct
problem sites in limited circumstances with formal written approval from Ecology and
the Local Permitting Authority.
The SEPA review authority must be notified at the application phase of the project review (or the
time that the SEPA determination on the project is performed) that chemical treatment is
proposed. If it is added after this stage, an addendum will be necessary and may result in
project approval delay.
See Appendix II-B for background information on chemical treatment.
Criteria for Chemical Treatment Product Use
Chemically treated stormwater discharged from construction sites must be nontoxic to aquatic
organisms. The following protocol shall be used to evaluate chemicals proposed for stormwater
treatment at construction sites. Authorization to use a chemical in the field based on this
protocol does not relieve the applicant from responsibility for meeting all discharge and
receiving water criteria applicable to a site.
Treatment chemicals must be approved by EPA for potable water use.
Petroleum-based polymers are prohibited.
Prior to authorization for field use, jar tests shall be conducted to
demonstrate that turbidity reduction necessary to meet the receiving
water criteria can be achieved. Test conditions, including but not limited to
raw water quality and jar test procedures, should be indicative of field
conditions. Although these small-scale tests cannot be expected to
reproduce performance under field conditions, they are indicative of
treatment capability.
Prior to authorization for field use, the chemically treated stormwater shall
be tested for aquatic toxicity. Applicable procedures defined in
Chapter 173-205 WAC, Whole Effluent Toxicity Testing and Limits, shall
be used. Testing shall use stormwater from the construction site at which
the treatment chemical is proposed for use or a water solution using soil
from the proposed site.
Stormwater Pollution Prevention Plan
Treatment System Design
Chemical treatment systems shall be designed as batch treatment systems using either ponds
or portable trailer-mounted tanks. Flow-through continuous treatment systems are not allowed
at this time.
A chemical treatment system consists of the stormwater collection system (either temporary
diversion or the permanent site drainage system), a storage pond, pumps, a chemical feed
system, treatment cells, and interconnecting piping.
The treatment system shall use a minimum of two lined treatment cells. Multiple treatment cells
allow for clarification of treated water while other cells are being filled or emptied. Treatment
cells may be ponds or tanks. Ponds with constructed earthen embankments greater than six
feet high require special engineering analyses. Portable tanks may also be suitable for some
sites.
The following equipment should be located in an operations shed:
the chemical injector;
secondary containment for acid, caustic, buffering compound, and
treatment chemical;
emergency shower and eyewash, and
monitoring equipment which consists of a pH meter and a turbidimeter.
Sizing Criteria
The combination of the storage pond or other holding area and treatment capacity should be
large enough to treat stormwater during multiple day storm events. It is recommended that at a
minimum the storage pond or other holding area should be sized to hold 1.5 times the runoff
volume of the 10-year, 24-hour storm event. Bypass should be provided around the chemical
treatment system to accommodate extreme storm events. Runoff volume shall be calculated
using the methods presented in Volume 3, Chapter 2. If no hydrologic analysis is required for
the site, the Rational Method may be used.
Primary settling should be encouraged in the storage pond. A forebay with access for
maintenance may be beneficial.
There are two opposing considerations in sizing the treatment cells. A larger cell is able to treat
a larger volume of water each time a batch is processed. However, the larger the cell the longer
the time required to empty the cell. A larger cell may also be less effective at flocculation and
therefore require a longer settling time. The simplest approach to sizing the treatment cell is to
multiply the allowable discharge flow rate times the desired drawdown time. A 4-hour drawdown
time allows one batch per cell per 8-hour work period, given 1 hour of flocculation followed by
two hours of settling.
Stormwater Pollution Prevention Plan
The permissible discharge rate governed by potential downstream effect can be used to
calculate the recommended size of the treatment cells. The following discharge flow rate limits
shall apply:
If the discharge is directly or indirectly to a stream, the discharge flow rate
shall not exceed 50 percent of the peak flow rate of the 2-year, 24-hour
event for all storm events up to the 10-year, 24-hour event.
If discharge is occurring during a storm event equal to or greater than the
10-year, 24-hour event, the allowable discharge rate is the peak flow rate
of the 10-year, 24-hour event.
Discharge to a stream should not increase the stream flow rate by more
than 10 percent.
If the discharge is directly to a lake, a major receiving water listed in
Appendix C of Volume I, or to an infiltration system, there is no discharge
flow limit.
If the discharge is to a municipal storm drainage system, the allowable
discharge rate may be limited by the capacity of the public system. It may
be necessary to clean the municipal storm drainage system prior to the
start of the discharge to prevent scouring solids from the drainage
system.
Runoff rates shall be calculated using the methods presented in Volume
3, Chapter 2 for the pre-developed condition. If no hydrologic analysis is
required for the site, the Rational Method may be used.
Monitoring
The following monitoring shall be conducted. Test results shall be recorded on a daily log kept
on site:
Operational Monitoring
pH, conductivity (as a surrogate for alkalinity), turbidity and temperature
of the untreated stormwater
Total volume treated and discharged
Discharge time and flow rate
Type and amount of chemical used for pH adjustment
Amount of polymer used for treatment
Settling time
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Compliance Monitoring
pH and turbidity of the treated stormwater
pH and turbidity of the receiving water
Biomonitoring: Treated stormwater shall be tested for acute (lethal) toxicity. Bioassays shall be
conducted by a laboratory accredited by Ecology, unless otherwise approved by Ecology. The
performance standard for acute toxicity is no statistically significant difference in
survival between the control and 100 percent chemically treated stormwater.
Acute toxicity tests shall be conducted with the following species and protocols:
Fathead minnow, Pimephales promelas (96 hour static-renewal test,
method: EPA/600/4-90/027F). Rainbow trout, Oncorhynchus mykiss
(96 hour static-renewal test, method: EPA/600/4-90/027F) may be used
as a substitute for fathead minnow.
Daphnid, Ceriodaphnia dubia, Daphnia pulex, or Daphnia magna (48 hour
static test, method: EPA/600/4-90/027F).
All toxicity tests shall meet quality assurance criteria and test conditions in the most recent
versions of the EPA test method and Ecology Publication # WO-R-95-80, Laboratory Guidance
and Whole Effluent Toxicity Test Review Criteria.
Bioassays shall be performed on the first five batches and on every tenth batch thereafter, or as
otherwise approved by Ecology. Failure to meet the performance standard shall be immediately
reported to Ecology.
Discharge Compliance: Prior to discharge, each batch of treated stormwater must be
sampled and tested for compliance with pH and turbidity limits. These limits may be
established by the water quality standards or a site-specific discharge permit. Sampling and
testing for other pollutants may also be necessary at some sites. Turbidity must be within
5 NTUs of the background turbidity. Background is measured in the receiving water, upstream
from the treatment process discharge point. pH must be within the range of 6.5 to 8.5 standard
units and not cause a change in the pH of the receiving water of more than 0.2 standard units. It
is often possible to discharge treated stormwater that has a lower turbidity than the receiving
water and that matches the pH.
Treated stormwater samples and measurements shall be taken from the discharge pipe or
another location representative of the nature of the treated stormwater discharge. Samples used
for determining compliance with the water quality standards in the receiving water shall not be
taken from the treatment pond prior to decanting. Compliance with the water quality standards is
determined in the receiving water.
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Operator Training
Each contractor who intends to use chemical treatment shall be trained by an experienced
contractor on an active site for at least 40 hours.
Standard BMPs
Surface stabilization BMPs should be implemented on site to prevent significant erosion. All
sites shall use a truck wheel wash to prevent tracking of sediment off site.
Sediment Removal and Disposal
Sediment shall be removed from the storage or treatment cells as
necessary. Typically, sediment removal is required at least once during a
wet season and at the decommissioning of the cells. Sediment remaining
in the cells between batches may enhance the settling process and
reduce the required chemical dosage.
Sediment may be incorporated into the site away from drainages.
3.1.14 Element #14 – Construction Stormwater Filtration
Filtration removes sediment from runoff originating from disturbed areas of the site.
Traditional BMPs used to control soil erosion and sediment loss from sites under development
may not be adequate to ensure compliance with the water quality standard for turbidity in the
receiving water. Filtration may be used in conjunction with gravity settling to remove sediment
as small as fine silt (0.5 μm). The reduction in turbidity will be dependent on the particle size
distribution of the sediment in the stormwater. In some circumstances, sedimentation and
filtration may achieve compliance with the water quality standard for turbidity.
Unlike chemical treatment, the use of construction stormwater filtration does not require
approval from Ecology.
Filtration may also be used in conjunction with polymer treatment in a portable system to assure
capture of the flocculated solids.
Design and Installation Specifications – Background Information
Filtration with sand media has been used for over a century to treat water and wastewater. The
use of sand filtration for treatment of stormwater has developed recently, generally to treat
runoff from streets, parking lots, and residential areas. The application of filtration to
construction stormwater treatment is currently under development.
Two types of filtration systems may be applied to construction stormwater treatment: rapid and
slow. Rapid sand filters are the typical system used for water and wastewater treatment. They
can achieve relatively high hydraulic flow rates, on the order of 2 to 20 gpm/sf, because they
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have automatic backwash systems to remove accumulated solids. In contrast, slow sand filters
have very low hydraulic rates, on the order of 0.02 gpm/sf, because they do not have backwash
systems. To date, slow sand filtration has generally been used to treat stormwater. Slow sand
filtration is mechanically simple in comparison to rapid sand filtration but requires a much larger
filter area.
Filtration Equipment
Sand media filters are available with automatic backwashing features that can filter to 50 µm
particle size. Screen or bag filters can filter down to 5 µm. Fiber wound filters can remove
particles down to 0.5 µm. Filters should be sequenced from the largest to the smallest pore
opening. Sediment removal efficiency will be related to particle size distribution in the
stormwater.
Treatment Process Description
Stormwater is collected at interception point(s) on the site and is diverted to a sediment pond or
tank for removal of large sediment and storage of the stormwater before it is treated by the
filtration system. The stormwater is pumped from the trap, pond, or tank through the filtration
system in a rapid sand filtration system. Slow sand filtration systems are designed as flow
through systems using gravity.
If large volumes of concrete are being poured, pH adjustment may be necessary.
Maintenance Standards
Rapid sand filters typically have automatic backwash systems that are triggered by a pre-set
pressure drop across the filter. If the backwash water volume is not large or substantially more
turbid than the stormwater stored in the holding pond or tank, backwash return to the pond or
tank may be appropriate. However, land application or another means of treatment and disposal
may be necessary.
Screen, bag, and fiber filters must be cleaned and/or replaced when they
become clogged.
Sediment shall be removed from the storage and/or treatment ponds as
necessary. Typically, sediment removal is required once or twice during a
wet season and at the decommissioning of the ponds.
3.2 Site Specific BMPs
Site specific BMPs are shown on the TESC Plan Sheets and Details in Appendix A. These site
specific plan sheets will be updated annually.
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4.0 Construction Phasing and BMP
Implementation
The BMP implementation schedule will be driven by the construction schedule. The following
provides a sequential list of the proposed construction schedule milestones and the
corresponding BMP implementation schedule. The list contains key milestones such as wet
season construction.
The BMP implementation schedule listed below is keyed to proposed phases of the construction
project, and reflects differences in BMP installations and inspections that relate to wet season
construction. The project site is located west of the Cascade Mountain Crest. As such, the dry
season is considered to be from May 1 to September 30 and the wet season is considered to be
from October 1 to April 30.
Estimate of Construction start date: March 2018
Estimate of Construction finish date: March 2019
Mobilize equipment on site:
Mobilize and store all ESC and soil stabilization products
(store materials on hand BMP C150):
Install ESC measures:
Install stabilized construction entrance:
Begin clearing and grubbing:
Temporary erosion control measures (hydroseeding):
Site inspections reduced to monthly:
Begin concrete pour and implement BMP C151:
Excavate and install new utilities and services (Phase 1):
Complete utility construction:
Begin implementing soil stabilization and sediment
control BMPs throughout the site in preparation for wet
season:
WET SEASON STARTS: October 1, 2017
Stormwater Pollution Prevention Plan
5.0 Pollution Prevention Team
5.1 Roles and Responsibilities
The pollution prevention team consists of personnel responsible for implementation of the
SWPPP, including the following:
Certified Erosion and Sediment Control Lead (CESCL) – primary
contractor contact, responsible for site inspections (BMPs, visual
monitoring, sampling, etc.); to be called upon in case of failure of any
ESC measures.
Resident Engineer – For projects with engineered structures only
(sediment ponds/traps, sand filters, etc.): site representative for the owner
that is the project's supervising engineer responsible for inspections and
issuing instructions and drawings to the contractor's site supervisor or
representative
Emergency Ecology Contact – individual to be contacted at Ecology in
case of emergency. Go to the following website to get the name and
number for the Ecology contact information:
http://www.ecy.wa.gov/org.html.
Emergency Owner Contact – individual that is the site owner or
representative of the site owner to be contacted in the case of an
emergency.
Non-Emergency Ecology Contact – individual that is the site owner or
representative of the site owner than can be contacted if required.
Monitoring Personnel – personnel responsible for conducting water
quality monitoring; for most sites this person is also the Certified Erosion
and Sediment Control Lead.
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5.2 Team Members
Names and contact information for those identified as members of the pollution prevention team
are provided in the following table.
Title Name(s) Phone Number
Certified Erosion and Sediment Control
Lead (CESCL)
T.B.D.
Resident Engineer Ali Sadr (425) 251-6222
Emergency Ecology Contact T.B.D.
Emergency Owner Contact T.B.D.
Non-Emergency Ecology Contact Ali Sadr (425) 251-6222
Monitoring Personnel T.B.D.
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6.0 Site Inspections and Monitoring
Monitoring includes visual inspection, monitoring for water quality parameters of concern, and
documentation of the inspection and monitoring findings in a site log book. A site log book will
be maintained for all on-site construction activities and will include:
A record of the implementation of the SWPPP and other permit
requirements;
Site inspections; and,
Stormwater quality monitoring.
For convenience, the inspection form and water quality monitoring forms included in this
SWPPP include the required information for the site log book. This SWPPP may function as the
site log book if desired, or the forms may be separated and included in a separate site log book.
However, if separated, the site log book but must be maintained on-site or within reasonable
access to the site and be made available upon request to Ecology or the local jurisdiction.
6.1 Site Inspection
All BMPs will be inspected, maintained, and repaired as needed to assure continued
performance of their intended function. The inspector will be a Certified Erosion and Sediment
Control Lead (CESCL) per BMP C160. The name and contact information for the CESCL is
provided in Section 5 of this SWPPP.
Site inspection will occur in all areas disturbed by construction activities and at all stormwater
discharge points. Stormwater will be examined for the presence of suspended sediment,
turbidity, discoloration, and oily sheen. The site inspector will evaluate and document the
effectiveness of the installed BMPs and determine if it is necessary to repair or replace any of
the BMPs to improve the quality of stormwater discharges. All maintenance and repairs will be
documented in the site log book or forms provided in this document. All new BMPs or design
changes will be documented in the SWPPP as soon as possible.
6.1.1 Site Inspection Frequency
Site inspections will be conducted at least once a week and within 24 hours following any
rainfall event which causes a discharge of stormwater from the site. For sites with temporary
stabilization measures, the site inspection frequency can be reduced to once every month.
6.1.2 Site Inspection Documentation
The site inspector will record each site inspection using the site log inspection forms provided in
Appendix E. The site inspection log forms may be separated from this SWPPP document, but
will be maintained on-site or within reasonable access to the site and be made available upon
request to Ecology or the local jurisdiction.
Stormwater Pollution Prevention Plan
6.2 Stormwater Quality Monitoring
6.2.1 Turbidity Sampling
Monitoring requirements for the proposed project will include either turbidity or water
transparency sampling to monitor site discharges for water quality compliance with the 2005
Construction Stormwater General Permit (Appendix D). Sampling will be conducted at all
discharge points at least once per calendar week.
Turbidity or transparency monitoring will follow the analytical methodologies described in
Section S4 of the 2005 Construction Stormwater General Permit (Appendix D). The key
benchmark values that require action are 25 NTU for turbidity (equivalent to 32 cm
transparency) and 250 NTU for turbidity (equivalent to 6 cm transparency). If the 25 NTU
benchmark for turbidity (equivalent to 32 cm transparency) is exceeded, the following steps will
be conducted:
1. Ensure all BMPs specified in this SWPPP are installed and functioning as
intended.
2. Assess whether additional BMPs should be implemented, and document
revisions to the SWPPP as necessary.
3. Sample discharge location daily until the analysis results are less than
25 NTU (turbidity) or greater than 32 cm (transparency).
If the turbidity is greater than 25 NTU (or transparency is less than 32 cm) but less than
250 NTU (transparency greater than 6 cm) for more than 3 days, additional treatment BMPs will
be implemented within 24 hours of the third consecutive sample that exceeded the benchmark.
If the 250 NTU benchmark for turbidity (or less than 6 cm transparency) is exceeded at any
time, the following steps will be conducted:
1. Notify Ecology by phone within 24 hours of analysis (see Section 5.0 of
this SWPPP for contact information).
2. Continue daily sampling until the turbidity is less than 25 NTU (or
transparency is greater than 32 cm).
3. Initiate additional treatment BMPs such as off-site treatment, infiltration,
filtration and chemical treatment within 24 hours of the first 250 NTU
exceedance.
4. Implement additional treatment BMPs as soon as possible, but within
7 days of the first 250 NTU exceedance.
5. Describe inspection results and remedial actions taken in the site log
book and in monthly discharge monitoring reports as described in Section
7.0 of this SWPPP.
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6.2.2 pH Sampling
Stormwater runoff will be monitored for pH starting on the first day of any activity that includes
more than 40 yards of poured or recycled concrete, or after the application of "Engineered Soils"
such as Portland cement treated base, cement kiln dust, or fly ash. This does not include
fertilizers. For concrete work, pH monitoring will start the first day concrete is poured and
continue until 3 weeks after the last pour. For engineered soils, the pH monitoring period begins
when engineered soils are first exposed to precipitation and continue until the area is fully
stabilized.
Stormwater samples will be collected daily from all points of discharge from the site and
measured for pH using a calibrated pH meter, pH test kit, or wide range pH indicator paper. If
the measured pH is 8.5 or greater, the following steps will be conducted:
1. Prevent the high pH water from entering storm drains or surface water.
2. Adjust or neutralize the high pH water if necessary using appropriate
technology such as CO2 sparging (liquid or dry ice).
3. Contact Ecology if chemical treatment other than CO2 sparging is
planned.
Stormwater Pollution Prevention Plan
7.0 Reporting and Recordkeeping
7.1 Recordkeeping
7.1.1 Site Log Book
A site log book will be maintained for all on-site construction activities and will include:
A record of the implementation of the SWPPP and other permit
requirements;
Site inspections; and,
Stormwater quality monitoring.
For convenience, the inspection form and water quality monitoring forms included in this
SWPPP include the required information for the site logbook.
7.1.2 Records Retention
Records of all monitoring information (site log book, inspection reports/checklists, etc.), this
Stormwater Pollution Prevention Plan, and any other documentation of compliance with permit
requirements will be retained during the life of the construction project and for a minimum of
three years following the termination of permit coverage in accordance with permit condition
S5.C.
7.1.3 Access to Plans and Records
The SWPPP, General Permit, Notice of Authorization letter, and Site Log Book will be retained
on site or within reasonable access to the site and will be made immediately available upon
request to Ecology or the local jurisdiction. A copy of this SWPPP will be provided to Ecology
within 14 days of receipt of a written request for the SWPPP from Ecology. Any other
information requested by Ecology will be submitted within a reasonable time. A copy of the
SWPPP or access to the SWPPP will be provided to the public when requested in writing in
accordance with Permit Condition S5.G.
7.1.4 Updating the SWPPP
In accordance with Conditions S3, S4.B, and S9.B.3 of the General Permit, this SWPPP will be
modified if the SWPPP is ineffective in eliminating or significantly minimizing pollutants in
stormwater discharges from the site or there has been a change in design, construction,
operation, or maintenance at the site that has a significant effect on the discharge, or potential
for discharge, of pollutants to the waters of the State. The SWPPP will be modified within seven
days of determination based on inspection(s) that additional or modified BMPs are necessary to
correct problems identified, and an updated timeline for BMP implementation will be prepared.
Stormwater Pollution Prevention Plan
7.2 Reporting
7.2.1 Discharge Monitoring Reports
Discharge Monitoring Report (DMR) forms will be submitted to Ecology because water quality
sampling is being conducted at the site.
7.2.2 Notification of Noncompliance
If any of the terms and conditions of the permit are not met, and it causes a threat to human
health or the environment, the following steps will be taken in accordance with permit
section S5.F:
1. Ecology will be immediately notified of the failure to comply.
2. Immediate action will be taken to control the noncompliance issue and to
correct the problem. If applicable, sampling and analysis of any
noncompliance will be repeated immediately and the results submitted to
Ecology within five (5) days of becoming aware of the violation.
3. A detailed written report describing the noncompliance will be submitted
to Ecology within five (5) days, unless requested earlier by Ecology.
Stormwater Pollution Prevention Plan
Appendix A – Site Plans
W
W
W
W WWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWWUW MEDICINE - VALLEY MEDICAL CENTER
MEDICAL OFFICE BUILDING EXPANSION
Stormwater Pollution Prevention Plan
Appendix B – Construction BMPs
High Visibility Plastic or Metal Fence (BMP C103)
Stabilized Construction Entrance (BMP C105)
Silt Fence (BMP C233)
Temporary and Permanent Seeding (BMP C120)
Mulching (BMP C121)
Dust Control (BMP C140)
Check Dams (BMP C207)
Grass-Lined Channels (BMP C201)
Construction Stormwater Chemical Treatment (BMP C250)
Construction Stormwater Filtration (BMP C251)
Stormwater Pollution Prevention Plan
Appendix C – Alternative BMPs
The following includes a list of possible alternative BMPs for each of the 12 elements not
described in the main SWPPP text. This list can be referenced in the event a BMP for a specific
element is not functioning as designed and an alternative BMP needs to be implemented.
Element #1 - Mark Clearing Limits
Element #2 - Establish Construction Access
Element #3 - Control Flow Rates
Element #4 - Install Sediment Controls
Advanced BMPs:
Element #5 - Stabilize Soils
Element #6 - Protect Slopes
Element #8 - Stabilize Channels and Outlets
Element #10 - Control Dewatering
Additional Advanced BMPs to Control Dewatering:
Stormwater Pollution Prevention Plan
Appendix D – General Permit
Stormwater Pollution Prevention Plan
Appendix E – Site Inspection Forms (and Site Log)
The results of each inspection shall be summarized in an inspection report or checklist that is
entered into or attached to the site log book. It is suggested that the inspection report or
checklist be included in this appendix to keep monitoring and inspection information in one
document, but this is optional; however, it is mandatory that this SWPPP and the site inspection
forms be kept onsite at all times during construction, and that inspections be performed and
documented as outlined below.
At a minimum, each inspection report or checklist shall include:
a. Inspection date/times
b. Weather information: general conditions during inspection, approximate amount
of precipitation since the last inspection, and approximate amount of precipitation
within the last 24 hours.
c. A summary or list of all BMPs that have been implemented, including
observations of all erosion/sediment control structures or practices.
d. The following shall be noted:
i. locations of BMPs inspected,
ii. locations of BMPs that need maintenance,
iii. the reason maintenance is needed,
iv. locations of BMPs that failed to operate as designed or intended, and
v. locations where additional or different BMPs are needed, and the reason(s)
why
e. A description of stormwater discharged from the site. The presence of
suspended sediment, turbid water, discoloration, and/or oil sheen shall be noted,
as applicable.
f. A description of any water quality monitoring performed during inspection, and
the results of that monitoring.
g. General comments and notes, including a brief description of any BMP repairs,
maintenance or installations made as a result of the inspection.
h. A statement that, in the judgment of the person conducting the site inspection,
the site is either in compliance or out of compliance with the terms and conditions
of the SWPPP and the NPDES permit. If the site inspection indicates that the site
is out of compliance, the inspection report shall include a summary of the
remedial actions required to bring the site back into compliance, as well as a
schedule of implementation.
i. Name, title, and signature of person conducting the site inspection; and the
following statement: “I certify under penalty of law that this report is true,
accurate, and complete, to the best of my knowledge and belief”.
When the site inspection indicates that the site is not in compliance with any terms and
conditions of the NPDES permit, the Permittee shall take immediate action(s) to: stop, contain,
and clean up the unauthorized discharges, or otherwise stop the noncompliance; correct the
Stormwater Pollution Prevention Plan
problem(s); implement appropriate Best Management Practices (BMPs), and/or conduct
maintenance of existing BMPs; and achieve compliance with all applicable standards and permit
conditions. In addition, if the noncompliance causes a threat to human health or the
environment, the Permittee shall comply with the Noncompliance Notification requirements in
Special Condition S5.F of the permit.
Stormwater Pollution Prevention Plan
Site Inspection Form
General Information
Project Name: Valley Medical Center Medical Office Building
Inspector Name: T.B.D. Title:
CESCL # :
Date: Time:
Inspection Type: □ After a rain event
□ Weekly
□ Turbidity/transparency benchmark exceedance
□ Other
Weather
Precipitation Since last inspection In last 24 hours
Description of General Site Conditions:
Inspection of BMPs
Element 1: Mark Clearing Limits
BMP:
Location Inspected Functioning Problem/Corrective Action Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Element 2: Establish Construction Access
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Stormwater Pollution Prevention Plan
36
Element 3: Control Flow Rates
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Element 4: Install Sediment Controls
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Stormwater Pollution Prevention Plan
37
Element 5: Stabilize Soils
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Element 6: Protect Slopes
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Stormwater Pollution Prevention Plan
38
Element 7: Protect Drain Inlets
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Element 8: Stabilize Channels and Outlets
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Stormwater Pollution Prevention Plan
39
Element 9: Control Pollutants
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Element 10: Control Dewatering
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
BMP:
Inspected Functioning
Y N Y N NIP
Stormwater Discharges From the Site
Observed?
Y N
Location
Turbidity
Discoloration
Sheen
Location
Turbidity
Discoloration
Sheen
Stormwater Pollution Prevention Plan
40
Water Quality Monitoring
Was any water quality monitoring conducted? □ Yes □ No
If water quality monitoring was conducted, record results here:
If water quality monitoring indicated turbidity 250 NTU or greater; or transparency 6 cm
or less, was Ecology notified by phone within 24 hrs?
□ Yes □ No
If Ecology was notified, indicate the date, time, contact name and phone number below:
Date:
Time:
Contact Name:
Phone #:
General Comments and Notes
Include BMP repairs, maintenance, or installations made as a result of the inspection.
Were Photos Taken? □ Yes □ No
If photos taken, describe photos below:
Stormwater Pollution Prevention Plan
41
Appendix F – Engineering Calculations
Stormwater Storage Pond Calculations
The sediment traps used as storage ponds prior to pumping to the baker tanks
were sized based upon the criteria presented in section D.2.1.5.1 (RSWDM, 2017).
These calculations are conservative since they assume the pond is sized to
remove sediment, whereas the proposed ponds are simply used for storage and
need not provide the additional capacity for the purposes of increased retention
time and subsequent sediment settling.
The peak runoff from the 10-year storm was calculated using WWHM by specifying
the land cover across the 1.96 acre site as completely impervious, to be
conservative. The runoff from the 10-year storm was used, rather than the 2-year
runoff volume, because the construction is expected to extend through several wet
seasons.
From the calculations below, we see that the total surface area of the two separate
sediment traps on-site should total to ~2,200 square feet. Thus, each sediment
trap should have a surface area of ~1,100 square feet.
WWHM2012
PROJECT REPORT
___________________________________________________________________
Project Name: 18092-MOB-2017-09-18-TESC Runoff
Site Name: MOB
Site Address: NWC--Talbot / 180th
City : Renton
Report Date: 12/19/2017
Gage : Seatac
Data Start : 1948/10/01
Data End : 2009/09/30
Precip Scale: 1.00
Version Date: 2017/04/14
Version : 4.2.13
_________________________________________________________________
UNMITIGATED LAND USE
Name : Basin 1
Bypass: No
GroundWater: No
Pervious Land Use acre
Pervious Total 0
Impervious Land Use acre
PARKING FLAT 1.96
Impervious Total 1.96
Basin Total 1.96
________________________________________________________________
______________________________________________________________
Flow Frequency Return Periods for UnMitigated. POC #1
Return Period Flow(cfs)
2 year 0.747279
5 year 0.9439
10 year 1.07749
25 year 1.250777
50 year 1.383405
100 year 1.519255
___________________________________________________________________
Stream Protection Duration
Annual Peaks for Predeveloped and Mitigated. POC #1
Year Predeveloped Mitigated
1949 0.057 0.968
1950 0.071 1.046
1951 0.127 0.605
1952 0.040 0.538
1953 0.032 0.581
1954 0.050 0.608
1955 0.079 0.689
1956 0.063 0.678
1957 0.051 0.769
1958 0.057 0.621
1959 0.049 0.633
1960 0.086 0.621
1961 0.048 0.657
1962 0.030 0.572
1963 0.041 0.636
1964 0.054 0.624
1965 0.039 0.792
1966 0.037 0.530
1967 0.078 0.913
1968 0.049 1.038
1969 0.048 0.722
1970 0.039 0.696
1971 0.042 0.830
1972 0.094 0.857
1973 0.043 0.519
1974 0.047 0.757
1975 0.063 0.873
1976 0.046 0.587
1977 0.005 0.635
1978 0.040 0.777
1979 0.024 1.064
1980 0.090 0.955
1981 0.036 0.781
1982 0.069 1.101
1983 0.062 0.896
1984 0.038 0.565
1985 0.023 0.779
1986 0.100 0.675
1987 0.088 1.042
1988 0.035 0.632
1989 0.023 0.791
1990 0.185 1.332
1991 0.111 1.064
1992 0.043 0.560
1993 0.045 0.485
1994 0.015 0.528
1995 0.064 0.692
1996 0.135 0.737
1997 0.113 0.716
1998 0.026 0.725
1999 0.106 1.484
2000 0.045 0.739
2001 0.008 0.812
2002 0.049 0.947
2003 0.062 0.736
2004 0.081 1.388
2005 0.058 0.634
2006 0.068 0.560
2007 0.137 1.298
2008 0.177 1.045
2009 0.087 0.966
___________________________________________________________________
Stream Protection Duration
Ranked Annual Peaks for Predeveloped and Mitigated. POC #1
Rank Predeveloped Mitigated
1 0.1847 1.4839
2 0.1769 1.3884
3 0.1371 1.3317
4 0.1350 1.2977
5 0.1269 1.1012
6 0.1129 1.0641
7 0.1112 1.0638
8 0.1058 1.0459
9 0.0999 1.0452
10 0.0945 1.0419
11 0.0896 1.0380
12 0.0883 0.9679
13 0.0868 0.9659
14 0.0858 0.9546
15 0.0806 0.9468
16 0.0792 0.9129
17 0.0784 0.8963
18 0.0706 0.8726
19 0.0688 0.8572
20 0.0682 0.8303
21 0.0641 0.8116
22 0.0631 0.7923
23 0.0630 0.7905
24 0.0623 0.7809
25 0.0617 0.7791
26 0.0579 0.7773
27 0.0573 0.7691
28 0.0566 0.7574
29 0.0544 0.7386
30 0.0509 0.7369
31 0.0497 0.7356
32 0.0491 0.7253
33 0.0489 0.7215
34 0.0488 0.7156
35 0.0484 0.6961
36 0.0478 0.6925
37 0.0466 0.6890
38 0.0456 0.6780
39 0.0447 0.6753
40 0.0446 0.6570
41 0.0429 0.6360
42 0.0429 0.6355
43 0.0422 0.6345
44 0.0414 0.6330
45 0.0400 0.6321
46 0.0400 0.6237
47 0.0394 0.6212
48 0.0390 0.6206
49 0.0381 0.6077
50 0.0375 0.6046
51 0.0358 0.5868
52 0.0349 0.5808
53 0.0323 0.5725
54 0.0301 0.5654
55 0.0255 0.5605
56 0.0242 0.5599
57 0.0227 0.5378
58 0.0226 0.5297
59 0.0150 0.5275
60 0.0080 0.5191
61 0.0054 0.4849
___________________________________________________________________
Perlnd and Implnd Changes
No changes have been made.
___________________________________________________________________
This program and accompanying documentation are provided 'as-is' without warranty of any kind. The
entire risk regarding the performance and results of this program is assumed by End User. Clear Creek
Solutions Inc. and the governmental licensee or sublicensees disclaim all warranties, either expressed
or implied, including but not limited to implied warranties of program and accompanying documentation.
In no event shall Clear Creek Solutions Inc. be liable for any damages whatsoever (including without
limitation to damages for loss of business profits, loss of business information, business
interruption, and the like) arising out of the use of, or inability to use this program even if Clear
Creek Solutions Inc. or their authorized representatives have been advised of the possibility of such
damages. Software Copyright © by : Clear Creek Solutions, Inc. 2005-2017; All Rights Reserved.
Project:
BCE #:
REQUIRED SURFACE AREA Flow cfs
SA = (2,080)(Q10)=2246 SF Q2*0.74
∴ USE SURFACE AREA =2200 SF Q10 1.08
0.05 AC Q100 1.52
PRINCIPAL SPILLWAY SIZING
D = [(Q10 ) / (3.782)(H)0.5]0.5 =6.413 FT KEY
*H MIN (DEFAULT 1)=1 FT INPUT
∴ USE RISER DIAMETER =6 2/4 IN OUTPUT
CHECK
EMERGENCY OVERFLOW SPILLWAY SPECS
L = [Q100 / (3.21)(H)1.5] - 2.4H =0.14 FT
*H MIN (DEFAULT .5)=0.5 FT
∴ USE SPILLWAY LENGTH =6 FT
DEWATERING ORIFICE
A0 = (S.A.)(2H)0.5/(0.6)(3,600)(T)(g)0.5 =0.011 SF
DIAM. = 13.54 (A0)0.5 =1.39 IN
*H MIN (DEFAULT 3.5')=1 FT
∴ USE ORIFICE DIAMETER =1 1/2 IN
*IF CONSTRUCTION TAKES PLACE OUTSIDE THE WET SEASON IN SUMMER MONTHS, Q2 IS ALLOWED TO SIZE POND S.A.
MOB
18092
TESC Calculations
Developed Site Runoff
P:\18000s\18092\excel\18092 - TESC CALCS
BAKER TANK SIZING CALCULATIONS
CESF System Calculations For
“UW Medicine-Valley Medical Center”
Site size:
The site is 1.96 acres in size. All CESF calculations will be based on this site size and assume
there will be no run on or significant ground water. Areas beyond this open area where storm wa-
ter will be collected must be added to the totals in this report to be accurate. These calculations
assume the whole site will be open at one time.
Soil types on site:
The USDA WSS tool was able to give data on the area to be disturbed. Soil on this site consists
of “Alderwood Gravelly Sandy Loam,” with 88.7% of the site having slopes between 15-30%.
Alderwood Gravelly Sandy Loam in the area has a low infiltration capacity of .06% as it falls
into hydrologic group D. The King County soil survey map and USDA WSS confirm this. The
rational method will be used in these calculations which will assign a runoff coefficient of .75%
to this site.
Rainfall information:
The site gets an average total of 36.15” of precipitation per year. That average over the job site is
an annual total of 1,717,829 gallons. The following is a breakdown of average total precipitation
per month for Bothell, the nearest measured location.
Following is daily extreme and average information.
System sizing:
The proposed system is a batch Chitosan enhanced sand filtration system (CESF). The system is
capable of treating water in a range from 100 GPM to 300 GPM. This system will be sized to
treat water at no less than 250 GPM at which rate it is possible to treat up to 84,000 gallons in an
8-hour shift, accounting for startup and settling times. Systems storage must be sized so there is
storage for a 24hr 10-year storm minus what the system can treat in 8 hours. A 10 year 24-hour
storm in Bellevue is about 4.5” according to NOAA atlas. After the application of the runoff co-
efficient we can find the minimum storage for the filtration system is 160,378 gallons minus the
82,500 gallons for the batch system we are left needing 77,878 gallons of storage. Four tanks
will be used to this storage volume with an additional two tanks for the batch treatment. All cal-
culations in this report will assume that storage volume. With the proposed system it would take
about one 8 hour shift to drain the system completely.
Chemical Consumption:
Chemical consumptions assume influent turbidity of less than 600 NTU so a limit of 1 ppm is
used. The chemical assumed is 1% chitosan acetate solution.
Calculations:
Based on the average daily rain totals the storage volume discussed prior and chemical consump-
tion discussed earlier.
Variables:
Some of the largest variables not factored into this report are:
-Site run on or ground water which would result in much higher totals
-Project staging which would result in less for the totals
-Excessively dirty influent water which will slow the treatment rate and increase chemi-
cal consumption.
-Abnormal rain totals or large scale rain events (ie storms beyond averages)
-Possible request of customer to keep storage tanks drawn down instead of waiting to fill
Month Rain Total
in gallons
Runoff Potential
in gallons
Probable Hours
for Treatment
Probable chemical con-
sumption in gallons under
600 NTU
January 267,060 200,295 20 20
February 194,829 146,121 20 15
March 184,851 136,638 20 14
April 109,295 81,971 10 8
May 108,819 81,614 10 8
June 103,592 77,694 10 7
July 38,490 28,868 0 3
August 49,420 37,065 0 4
September 88,386 66,289 10 7
October 179,148 134,361 20 13
November 246,151 184,613 20 18
December 276,563 207,422 24 21
Total 1,846,132 1,307,951 164 138
-Suspended solids that take longer to settle, pH adjustment need, or conductivity issues
-Sediment build up in the system that is allowed to become excessive
Tab 9.0
9.0 BOND QUANTITIES, FACILITY SUMMARIES, AND DECLARATION OF COVENANT
A Bond Quantities Worksheet, and a Declaration of Covenant have been provided with this final
Technical Information Report. A Flow Control and Water Quality Facility Summary Sheet was not
provided since it was not requested, nor was it available in the 2017 RSWDM.
SITE IMPROVEMENT BOND QUANTITY WORKSHEET
FOR
VALLEY MEDICAL CENTER
MEDICAL OFFICE BUILDING
Planning Division |1055 South Grady Way – 6th Floor | Renton, WA 98057 (425) 430-7200Date Prepared: Name:PE Registration No:Firm Name:Firm Address:Phone No.Email Address:Project Name: Project Owner:CED Plan # (LUA):Phone:CED Permit # (U):Address: Site Address:Street Intersection:Addt'l Project Owner:Parcel #(s):Phone:Address: Clearing and grading greater than or equal to 5,000 board feet of timber? Yes/No:NoWater Service Provided by:If Yes, Provide Forest Practice Permit #:Sewer Service Provided by: SITE IMPROVEMENT BOND QUANTITY WORKSHEETPROJECT INFORMATIONCITY OF RENTONCITY OF RENTON1 Select the current project status/phase from the following options: For Approval - Preliminary Data Enclosed, pending approval from the City; For Construction - Estimated Data Enclosed, Plans have been approved for contruction by the City; Project Closeout - Final Costs and Quantities Enclosed for Project Close-out SubmittalPhoneEngineer Stamp Required (all cost estimates must have original wet stamp and signature)Clearing and GradingUtility ProvidersN/AProject Location and DescriptionProject Owner InformationValley Medical Center Medical Office BuildingRenton, WA. 98055Parcel NumberValley Medical Center##-######425-228-3440x59326/6/2017 --> Revised 01/19/2017Prepared by:FOR CONSTRUCTIONProject Phase 1asadr@bargausen.comAli Sadr24661Barghausen18215 72nd AVE South425-251-6222400 South 43rd Street400 South 43rd Street,Additional Project OwnerCarr Road / Talbot########AddressAbbreviated Legal Description:Abbreviated LegalCity, State, ZipPage 2 of 14Ref 8-H Bond Quantity WorksheetSECTION I PROJECT INFORMATIONUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/201801/19/18
CED Permit #:########UnitReference #PriceUnitQuantity CostBackfill & compaction-embankmentESC-16.50$ CYCheck dams, 4" minus rockESC-2SWDM 5.4.6.380.00$ Each10800.00Catch Basin ProtectionESC-335.50$ Each20710.00Crushed surfacing 1 1/4" minusESC-4WSDOT 9-03.9(3)95.00$ CY DitchingESC-59.00$ CY2001,800.00Excavation-bulkESC-62.00$ CY2300046,000.00Fence, siltESC-7SWDM 5.4.3.11.50$ LF9261,389.00Fence, Temporary (NGPE)ESC-81.50$ LF Geotextile FabricESC-92.50$ SY Hay Bale Silt TrapESC-100.50$ Each HydroseedingESC-11SWDM 5.4.2.40.80$ SY25002,000.00Interceptor Swale / DikeESC-121.00$ LF Jute MeshESC-13SWDM 5.4.2.23.50$ SY Level SpreaderESC-141.75$ LF Mulch, by hand, straw, 3" deepESC-15SWDM 5.4.2.12.50$ SY Mulch, by machine, straw, 2" deepESC-16SWDM 5.4.2.12.00$ SY Piping, temporary, CPP, 6"ESC-1712.00$ LF Piping, temporary, CPP, 8"ESC-1814.00$ LF2303,220.00Piping, temporary, CPP, 12"ESC-1918.00$ LF Plastic covering, 6mm thick, sandbaggedESC-20SWDM 5.4.2.34.00$ SY Rip Rap, machine placed; slopesESC-21WSDOT 9-13.1(2)45.00$ CY Rock Construction Entrance, 50'x15'x1'ESC-22SWDM 5.4.4.11,800.00$ Each11,800.00Rock Construction Entrance, 100'x15'x1'ESC-23SWDM 5.4.4.13,200.00$ EachSediment pond riser assemblyESC-24SWDM 5.4.5.22,200.00$ Each12,200.00Sediment trap, 5' high berm ESC-25SWDM 5.4.5.119.00$ LF30570.00Sed. trap, 5' high, riprapped spillway berm section ESC-26SWDM 5.4.5.170.00$ LF Seeding, by handESC-27SWDM 5.4.2.41.00$ SY Sodding, 1" deep, level groundESC-28SWDM 5.4.2.58.00$ SY Sodding, 1" deep, sloped groundESC-29SWDM 5.4.2.510.00$ SY TESC SupervisorESC-30110.00$ HR20022,000.00Water truck, dust controlESC-31SWDM 5.4.7140.00$ HR24033,600.00UnitReference #PriceUnitQuantity Cost180,000.00$ LS1180,000.00 EROSION/SEDIMENT SUBTOTAL:296,089.00SALES TAX @ 10%29,608.90EROSION/SEDIMENT TOTAL:325,697.90(A)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR EROSION & SEDIMENT CONTROLDescription No.(A)Baker Tanks and filtration systemWRITE-IN-ITEMS Page 3 of 14Ref 8-H Bond Quantity WorksheetSECTION II.a EROSION_CONTROLUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostGENERAL ITEMS Backfill & Compaction- embankmentGI-16.00$ CY15009,000.00Backfill & Compaction- trenchGI-29.00$ CYClear/Remove Brush, by hand (SY)GI-31.00$ SYBollards - fixedGI-4240.74$ EachBollards - removableGI-5452.34$ EachClearing/Grubbing/Tree RemovalGI-610,000.00$ Acre2.222,000.00Excavation - bulkGI-72.00$ CYExcavation - TrenchGI-85.00$ CY4002,000.00Fencing, cedar, 6' highGI-920.00$ LFFencing, chain link, 4'GI-1038.31$ LFFencing, chain link, vinyl coated, 6' highGI-1120.00$ LFFencing, chain link, gate, vinyl coated, 20' GI-121,400.00$ EachFill & compact - common barrowGI-1325.00$ CYFill & compact - gravel baseGI-1427.00$ CY95025,650.00Fill & compact - screened topsoilGI-1539.00$ CYGabion, 12" deep, stone filled mesh GI-1665.00$ SYGabion, 18" deep, stone filled mesh GI-1790.00$ SYGabion, 36" deep, stone filled meshGI-18150.00$ SYGrading, fine, by handGI-192.50$ SYGrading, fine, with graderGI-202.00$ SYMonuments, 3' LongGI-21250.00$ EachSensitive Areas SignGI-227.00$ EachSodding, 1" deep, sloped groundGI-238.00$ SYSurveying, line & gradeGI-24850.00$ DaySurveying, lot location/linesGI-251,800.00$ Acre2.23,960.00Topsoil Type A (imported)GI-2628.50$ CYTraffic control crew ( 2 flaggers )GI-27120.00$ HR20024,000.00Trail, 4" chipped woodGI-288.00$ SYTrail, 4" crushed cinderGI-299.00$ SYTrail, 4" top courseGI-3012.00$ SYConduit, 2"GI-315.00$ LFWall, retaining, concreteGI-3255.00$ SFWall, rockeryGI-3315.00$ SFSUBTOTAL THIS PAGE:86,610.00(B)(C)(D)(E)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR STREET AND SITE IMPROVEMENTSQuantity Remaining (Bond Reduction) (B)(C)Page 4 of 14Ref 8-H Bond Quantity WorksheetSECTION II.b TRANSPORTATIONUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostSITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR STREET AND SITE IMPROVEMENTSQuantity Remaining (Bond Reduction) (B)(C)ROAD IMPROVEMENT/PAVEMENT/SURFACINGAC Grinding, 4' wide machine < 1000syRI-130.00$ SYAC Grinding, 4' wide machine 1000-2000syRI-216.00$ SYAC Grinding, 4' wide machine > 2000syRI-310.00$ SYAC Removal/DisposalRI-435.00$ SY7250253,750.00Barricade, Type III ( Permanent )RI-556.00$ LFGuard RailRI-630.00$ LFCurb & Gutter, rolledRI-717.00$ LFCurb & Gutter, verticalRI-812.50$ LF4505,625.00Curb and Gutter, demolition and disposalRI-918.00$ LF200036,000.00Curb, extruded asphaltRI-105.50$ LFCurb, extruded concreteRI-117.00$ LF10007,000.00Sawcut, asphalt, 3" depthRI-121.85$ LF200370.00Sawcut, concrete, per 1" depthRI-133.00$ LFSealant, asphaltRI-142.00$ LFShoulder, gravel, 4" thickRI-1515.00$ SYSidewalk, 4" thickRI-1638.00$ SY180068,400.00Sidewalk, 4" thick, demolition and disposalRI-1732.00$ SY3009,600.00Sidewalk, 5" thickRI-1841.00$ SYSidewalk, 5" thick, demolition and disposalRI-1940.00$ SYSign, Handicap RI-2085.00$ Each10850.00Striping, per stallRI-217.00$ Each43301.00Striping, thermoplastic, ( for crosswalk )RI-223.00$ SFStriping, 4" reflectorized lineRI-230.50$ LFAdditional 2.5" Crushed SurfacingRI-243.60$ SYHMA 1/2" Overlay 1.5" RI-2514.00$ SYHMA 1/2" Overlay 2"RI-2618.00$ SYHMA Road, 2", 4" rock, First 2500 SYRI-2728.00$ SYHMA Road, 2", 4" rock, Qty. over 2500SYRI-2821.00$ SYHMA Road, 4", 6" rock, First 2500 SYRI-2945.00$ SYHMA Road, 4", 6" rock, Qty. over 2500 SYRI-3037.00$ SYHMA Road, 4", 4.5" ATBRI-3138.00$ SYGravel Road, 4" rock, First 2500 SYRI-3215.00$ SYGravel Road, 4" rock, Qty. over 2500 SYRI-3310.00$ SYThickened EdgeRI-348.60$ LFSUBTOTAL THIS PAGE:381,896.00(B)(C)(D)(E)Page 5 of 14Ref 8-H Bond Quantity WorksheetSECTION II.b TRANSPORTATIONUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostSITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR STREET AND SITE IMPROVEMENTSQuantity Remaining (Bond Reduction) (B)(C)PARKING LOT SURFACINGNo.2" AC, 2" top course rock & 4" borrowPL-121.00$ SY2" AC, 1.5" top course & 2.5" base coursePL-228.00$ SY310086,800.004" select borrowPL-35.00$ SY1.5" top course rock & 2.5" base coursePL-414.00$ SYSUBTOTAL PARKING LOT SURFACING:86,800.00(B)(C)(D)(E)LANDSCAPING & VEGETATIONNo.Street TreesLA-1Median LandscapingLA-2Right-of-Way LandscapingLA-3Wetland LandscapingLA-4SUBTOTAL LANDSCAPING & VEGETATION:(B)(C)(D)(E)TRAFFIC & LIGHTINGNo.SignsTR-1Street Light System ( # of Poles)TR-2Traffic SignalTR-3Traffic Signal ModificationTR-4SUBTOTAL TRAFFIC & LIGHTING:(B)(C)(D)(E)WRITE-IN-ITEMSSUBTOTAL WRITE-IN ITEMS:STREET AND SITE IMPROVEMENTS SUBTOTAL:468,506.00SALES TAX @ 10%46,850.60STREET AND SITE IMPROVEMENTS TOTAL:515,356.60(B)(C)(D)(E)Page 6 of 14Ref 8-H Bond Quantity WorksheetSECTION II.b TRANSPORTATIONUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostDRAINAGE (CPE = Corrugated Polyethylene Pipe, N12 or Equivalent) For Culvert prices, Average of 4' cover was assumed. Assume perforated PVC is same price as solid pipe.) Access Road, R/DD-126.00$ SY* (CBs include frame and lid)BeehiveD-290.00$ EachThrough-curb Inlet FrameworkD-3400.00$ EachCB Type ID-41,500.00$ Each812,000.00CB Type ILD-51,750.00$ EachCB Type II, 48" diameterD-62,300.00$ Each49,200.00 for additional depth over 4' D-7480.00$ FT5124,480.00CB Type II, 54" diameterD-82,500.00$ Each410,000.00 for additional depth over 4'D-9495.00$ FT2512,375.00CB Type II, 60" diameterD-102,800.00$ Each12,800.00 for additional depth over 4'D-11600.00$ FT1600.00CB Type II, 72" diameterD-126,000.00$ Each for additional depth over 4'D-13850.00$ FTCB Type II, 96" diameterD-1414,000.00$ Each for additional depth over 4'D-15925.00$ FTTrash Rack, 12"D-16350.00$ EachTrash Rack, 15"D-17410.00$ EachTrash Rack, 18"D-18480.00$ EachTrash Rack, 21"D-19550.00$ EachCleanout, PVC, 4"D-20150.00$ Each5750.00Cleanout, PVC, 6"D-21170.00$ EachCleanout, PVC, 8"D-22200.00$ Each102,000.00Culvert, PVC, 4" D-2310.00$ LF8368,360.00Culvert, PVC, 6" D-2413.00$ LFCulvert, PVC, 8" D-2515.00$ LFCulvert, PVC, 12" D-2623.00$ LFCulvert, PVC, 15" D-2735.00$ LFCulvert, PVC, 18" D-2841.00$ LFCulvert, PVC, 24"D-2956.00$ LFCulvert, PVC, 30" D-3078.00$ LFCulvert, PVC, 36" D-31130.00$ LFCulvert, CMP, 8"D-3219.00$ LFCulvert, CMP, 12"D-3329.00$ LFSUBTOTAL THIS PAGE:82,565.00(B)(C)(D)(E)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESQuantity Remaining (Bond Reduction) (B)(C)Page 7 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostSITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESQuantity Remaining (Bond Reduction) (B)(C)DRAINAGE (Continued)Culvert, CMP, 15"D-3435.00$ LFCulvert, CMP, 18"D-3541.00$ LFCulvert, CMP, 24"D-3656.00$ LFCulvert, CMP, 30"D-3778.00$ LFCulvert, CMP, 36"D-38130.00$ LFCulvert, CMP, 48"D-39190.00$ LFCulvert, CMP, 60"D-40270.00$ LFCulvert, CMP, 72"D-41350.00$ LFCulvert, Concrete, 8"D-4242.00$ LFCulvert, Concrete, 12"D-4348.00$ LFCulvert, Concrete, 15"D-4478.00$ LFCulvert, Concrete, 18"D-4548.00$ LFCulvert, Concrete, 24"D-4678.00$ LFCulvert, Concrete, 30"D-47125.00$ LFCulvert, Concrete, 36"D-48150.00$ LFCulvert, Concrete, 42"D-49175.00$ LFCulvert, Concrete, 48"D-50205.00$ LFCulvert, CPE Triple Wall, 6" D-5114.00$ LFCulvert, CPE Triple Wall, 8" D-5216.00$ LF67110,736.00Culvert, CPE Triple Wall, 12" D-5324.00$ LF49511,880.00Culvert, CPE Triple Wall, 15" D-5435.00$ LFCulvert, CPE Triple Wall, 18" D-5541.00$ LFCulvert, CPE Triple Wall, 24" D-5656.00$ LFCulvert, CPE Triple Wall, 30" D-5778.00$ LF31024,180.00Culvert, CPE Triple Wall, 36" D-58130.00$ LFCulvert, LCPE, 6"D-5960.00$ LFCulvert, LCPE, 8"D-6072.00$ LFCulvert, LCPE, 12"D-6184.00$ LFCulvert, LCPE, 15"D-6296.00$ LFCulvert, LCPE, 18"D-63108.00$ LFCulvert, LCPE, 24"D-64120.00$ LFCulvert, LCPE, 30"D-65132.00$ LFCulvert, LCPE, 36"D-66144.00$ LFCulvert, LCPE, 48"D-67156.00$ LFCulvert, LCPE, 54"D-68168.00$ LFSUBTOTAL THIS PAGE:46,796.00(B)(C)(D)(E)Page 8 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostSITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESQuantity Remaining (Bond Reduction) (B)(C)DRAINAGE (Continued)Culvert, LCPE, 60"D-69180.00$ LFCulvert, LCPE, 72"D-70192.00$ LFCulvert, HDPE, 6"D-7142.00$ LFCulvert, HDPE, 8"D-7242.00$ LFCulvert, HDPE, 12"D-7374.00$ LFCulvert, HDPE, 15"D-74106.00$ LFCulvert, HDPE, 18"D-75138.00$ LFCulvert, HDPE, 24"D-76221.00$ LFCulvert, HDPE, 30"D-77276.00$ LFCulvert, HDPE, 36"D-78331.00$ LFCulvert, HDPE, 48"D-79386.00$ LFCulvert, HDPE, 54"D-80441.00$ LFCulvert, HDPE, 60"D-81496.00$ LFCulvert, HDPE, 72"D-82551.00$ LFPipe, Polypropylene, 6"D-8384.00$ LFPipe, Polypropylene, 8"D-8489.00$ LFPipe, Polypropylene, 12"D-8595.00$ LFPipe, Polypropylene, 15"D-86100.00$ LFPipe, Polypropylene, 18"D-87106.00$ LFPipe, Polypropylene, 24"D-88111.00$ LFPipe, Polypropylene, 30"D-89119.00$ LFPipe, Polypropylene, 36"D-90154.00$ LFPipe, Polypropylene, 48"D-91226.00$ LFPipe, Polypropylene, 54"D-92332.00$ LFPipe, Polypropylene, 60"D-93439.00$ LFPipe, Polypropylene, 72"D-94545.00$ LFCulvert, DI, 6"D-9561.00$ LFCulvert, DI, 8"D-9684.00$ LFCulvert, DI, 12"D-97106.00$ LF19720,882.00Culvert, DI, 15"D-98129.00$ LFCulvert, DI, 18"D-99152.00$ LF203,040.00Culvert, DI, 24"D-100175.00$ LF8114,175.00Culvert, DI, 30"D-101198.00$ LFCulvert, DI, 36"D-102220.00$ LFCulvert, DI, 48"D-103243.00$ LFCulvert, DI, 54"D-104266.00$ LFCulvert, DI, 60"D-105289.00$ LFCulvert, DI, 72"D-106311.00$ LFSUBTOTAL THIS PAGE:38,097.00(B)(C)(D)(E)Page 9 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostSITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESQuantity Remaining (Bond Reduction) (B)(C)Specialty Drainage ItemsDitching SD-19.50$ CYFlow Dispersal Trench (1,436 base+)SD-328.00$ LF French Drain (3' depth)SD-426.00$ LFGeotextile, laid in trench, polypropyleneSD-53.00$ SY6501,950.00Mid-tank Access Riser, 48" dia, 6' deepSD-62,000.00$ EachPond Overflow SpillwaySD-716.00$ SYRestrictor/Oil Separator, 12"SD-81,150.00$ Each55,750.00Restrictor/Oil Separator, 15"SD-91,350.00$ EachRestrictor/Oil Separator, 18"SD-101,700.00$ EachRiprap, placedSD-1142.00$ CYTank End Reducer (36" diameter)SD-121,200.00$ EachInfiltration pond testingSD-13125.00$ HRPermeable PavementSD-14Permeable Concrete SidewalkSD-15Culvert, Box __ ft x __ ftSD-16SUBTOTAL SPECIALTY DRAINAGE ITEMS:7,700.00(B)(C)(D)(E)STORMWATER FACILITIES (Include Flow Control and Water Quality Facility Summary Sheet and Sketch)Detention PondSF-1Each Detention TankSF-2Each Detention VaultSF-3$166,667Each 3500,000.00Infiltration PondSF-4Each Infiltration TankSF-5Each Infiltration VaultSF-6Each Infiltration TrenchesSF-7Each Basic Biofiltration SwaleSF-8Each Wet Biofiltration SwaleSF-9Each WetpondSF-10Each WetvaultSF-11Each Sand FilterSF-12Each Sand Filter VaultSF-13Each Linear Sand FilterSF-14Each Proprietary FacilitySF-1535,000.00$ Each 270,000.00Bioretention FacilitySF-16Each SUBTOTAL STORMWATER FACILITIES:570,000.00(B)(C)(D)(E)Page 10 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostSITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESQuantity Remaining (Bond Reduction) (B)(C)WRITE-IN-ITEMS (INCLUDE ON-SITE BMPs)Trench DrainWI-150.00$ LF21510,750.00Green RoofWI-210.00$ SF250025,000.00Area DrainWI-3500.00$ Each1500.00WI-4WI-5WI-6WI-7WI-8WI-9WI-10WI-11WI-12WI-13WI-14WI-15SUBTOTAL WRITE-IN ITEMS:36,250.00DRAINAGE AND STORMWATER FACILITIES SUBTOTAL:781,408.00SALES TAX @ 10%78,140.80DRAINAGE AND STORMWATER FACILITIES TOTAL:859,548.80(B) (C) (D) (E)Page 11 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostConnection to Existing WatermainW-12,000.00$ Each24,000.00Ductile Iron Watermain, CL 52, 4 Inch DiameterW-250.00$ LF13650.007350.00Ductile Iron Watermain, CL 52, 6 Inch DiameterW-356.00$ LF201,120.00Ductile Iron Watermain, CL 52, 8 Inch DiameterW-460.00$ LF291,740.00Ductile Iron Watermain, CL 52, 10 Inch DiameterW-570.00$ LF503,500.00Ductile Iron Watermain, CL 52, 12 Inch DiameterW-680.00$ LFGate Valve, 4 inch DiameterW-7500.00$ Each1500.00Gate Valve, 6 inch DiameterW-8700.00$ Each21,400.00Gate Valve, 8 Inch DiameterW-9800.00$ Each1800.00Gate Valve, 10 Inch DiameterW-101,000.00$ EachGate Valve, 12 Inch DiameterW-111,200.00$ Each22,400.00Fire Hydrant AssemblyW-124,000.00$ EachPermanent Blow-Off AssemblyW-131,800.00$ EachAir-Vac Assembly, 2-Inch DiameterW-142,000.00$ EachAir-Vac Assembly, 1-Inch DiameterW-151,500.00$ EachCompound Meter Assembly 3-inch DiameterW-168,000.00$ Each18,000.00Compound Meter Assembly 4-inch DiameterW-179,000.00$ EachCompound Meter Assembly 6-inch DiameterW-1810,000.00$ EachPressure Reducing Valve Station 8-inch to 10-inchW-1920,000.00$ EachWATER SUBTOTAL:22,370.002,090.00SALES TAX @ 10%2,237.00209.00WATER TOTAL:24,607.002,299.00(B) (C) (D) (E)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR WATERQuantity Remaining (Bond Reduction) (B)(C)Page 12 of 14Ref 8-H Bond Quantity WorksheetSECTION II.d WATERUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostClean OutsSS-11,000.00$ Each11,000.00Grease Interceptor, 500 gallonSS-28,000.00$ EachGrease Interceptor, 1000 gallonSS-310,000.00$ EachGrease Interceptor, 1500 gallonSS-415,000.00$ EachSide Sewer Pipe, PVC. 4 Inch DiameterSS-580.00$ LFSide Sewer Pipe, PVC. 6 Inch DiameterSS-695.00$ LF353,325.00Sewer Pipe, PVC, 8 inch DiameterSS-7105.00$ LF13714,385.00Sewer Pipe, PVC, 12 Inch DiameterSS-8120.00$ LFSewer Pipe, DI, 8 inch DiameterSS-9115.00$ LFSewer Pipe, DI, 12 Inch DiameterSS-10130.00$ LFManhole, 48 Inch DiameterSS-116,000.00$ Each212,000.00Manhole, 54 Inch DiameterSS-136,500.00$ EachManhole, 60 Inch DiameterSS-157,500.00$ EachManhole, 72 Inch DiameterSS-178,500.00$ EachManhole, 96 Inch DiameterSS-1914,000.00$ EachPipe, C-900, 12 Inch DiameterSS-21180.00$ LFOutside DropSS-241,500.00$ LSInside DropSS-251,000.00$ LSArea DrainSS-26$500Each1500.00Lift Station (Entire System)SS-27LSSANITARY SEWER SUBTOTAL:31,210.00SALES TAX @ 10%3,121.00SANITARY SEWER TOTAL:34,331.00(B) (C) (D) (E)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR SANITARY SEWERQuantity Remaining (Bond Reduction) (B)(C)Page 13 of 14Ref 8-H Bond Quantity WorksheetSECTION II.e SANITARY SEWERUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
Planning Division |1055 South Grady Way – 6th Floor | Renton, WA 98057 (425) 430-7200Date:Name:Project Name: PE Registration No:CED Plan # (LUA):Firm Name:CED Permit # (U):Firm Address:Site Address:Phone No.Parcel #(s):Email Address:Project Phase: Site Restoration/Erosion Sediment Control Subtotal (a)Existing Right-of-Way Improvements Subtotal (b)(b)-$ Future Public Improvements Subtotal(c)24,607.00$ Stormwater & Drainage Facilities (Public & Private) Subtotal(d)(d)859,548.80$ (e)(f)Site RestorationCivil Construction PermitMaintenance Bond176,831.16$ Bond Reduction2Construction Permit Bond Amount 3Minimum Bond Amount is $10,000.001 Estimate Only - May involve multiple and variable components, which will be established on an individual basis by Development Engineering.2 The City of Renton allows one request only for bond reduction prior to the maintenance period. Reduction of not more than 70% of the original bond amount, provided that the remaining 30% willcover all remaining items to be constructed. 3 Required Bond Amounts are subject to review and modification by Development Engineering.* Note: The word BOND as used in this document means any financial guarantee acceptable to the City of Renton.** Note: All prices include labor, equipment, materials, overhead and profit. 425-251-6222asadr@bargausen.comValley Medical Center Medical Office Building##-######400 South 43rd StreetParcel NumberFOR CONSTRUCTION########18215 72nd AVE South1,185,246.70$ P (a) x 100%SITE IMPROVEMENT BOND QUANTITY WORKSHEET BOND CALCULATIONS6/6/2017 --> Revised 01/19/2017Ali Sadr24661BarghausenR((b x 150%) + (d x 100%))S(e) x 150% + (f) x 100%Bond Reduction: Existing Right-of-Way Improvements (Quantity Remaining)2Bond Reduction: Stormwater & Drainage Facilities (Quantity Remaining)2T(P +R - S)Prepared by:Project InformationCONSTRUCTION BOND AMOUNT */**(prior to permit issuance)EST1((b) + (c) + (d)) x 20%-$ MAINTENANCE BOND */**(after final acceptance of construction)325,697.90$ -$ 859,548.80$ 325,697.90$ -$ 859,548.80$ -$ Page 14 of 14Ref 8-H Bond Quantity WorksheetSECTION III. BOND WORKSHEETUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 1/19/2018
SITE IMPROVEMENT BOND QUANTITY WORKSHEET
FOR
VALLEY MEDICAL CENTER
ROAD IMPROVEMENTS
Planning Division |1055 South Grady Way – 6th Floor | Renton, WA 98057 (425) 430-7200Date:Name:Project Name: PE Registration No:CED Plan # (LUA):Firm Name:CED Permit # (U):Firm Address:Site Address:Phone No.Parcel #(s):Email Address:Project Phase: Site Restoration/Erosion Sediment Control Subtotal (a)Existing Right-of-Way Improvements Subtotal (b)(b)-$ Future Public Improvements Subtotal(c)5,720.00$ Stormwater & Drainage Facilities (Public & Private) Subtotal(d)(d)673,043.80$ (e)(f)Site RestorationCivil Construction PermitMaintenance Bond135,752.76$ Bond Reduction2Construction Permit Bond Amount 3Minimum Bond Amount is $10,000.001 Estimate Only - May involve multiple and variable components, which will be established on an individual basis by Development Engineering.2 The City of Renton allows one request only for bond reduction prior to the maintenance period. Reduction of not more than 70% of the original bond amount, provided that the remaining 30% willcover all remaining items to be constructed. 3 Required Bond Amounts are subject to review and modification by Development Engineering.* Note: The word BOND as used in this document means any financial guarantee acceptable to the City of Renton.** Note: All prices include labor, equipment, materials, overhead and profit. 425-251-6222asadr@bargausen.comValley Medical Center Medical Office Building##-######400 South 43rd StreetParcel NumberFOR CONSTRUCTION########18215 72nd AVE South998,038.80$ P (a) x 100%SITE IMPROVEMENT BOND QUANTITY WORKSHEET BOND CALCULATIONS6/6/2017 --> Revised 9/20/2017Ali Sadr24661BarghausenR((b x 150%) + (d x 100%))S(e) x 150% + (f) x 100%Bond Reduction: Existing Right-of-Way Improvements (Quantity Remaining)2Bond Reduction: Stormwater & Drainage Facilities (Quantity Remaining)2T(P +R - S)Prepared by:Project InformationCONSTRUCTION BOND AMOUNT */**(prior to permit issuance)EST1((b) + (c) + (d)) x 20%-$ MAINTENANCE BOND */**(after final acceptance of construction)324,995.00$ -$ 673,043.80$ 324,995.00$ -$ 673,043.80$ -$ Page 14 of 14Ref 8-H Bond Quantity WorksheetSECTION III. BOND WORKSHEETUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 9/20/2017
Planning Division |1055 South Grady Way – 6th Floor | Renton, WA 98057 (425) 430-7200Date Prepared: Name:PE Registration No:Firm Name:Firm Address:Phone No.Email Address:Project Name: Project Owner:CED Plan # (LUA):Phone:CED Permit # (U):Address: Site Address:Street Intersection:Addt'l Project Owner:Parcel #(s):Phone:Address: Clearing and grading greater than or equal to 5,000 board feet of timber? Yes/No:NoWater Service Provided by:If Yes, Provide Forest Practice Permit #:Sewer Service Provided by: AddressAbbreviated Legal Description:Abbreviated LegalCity, State, Zip400 South 43rd Street400 South 43rd Street,Additional Project OwnerCarr Road / Talbot########425-228-3440x593210/9/2017Prepared by:FOR CONSTRUCTIONProject Phase 1asadr@bargausen.comAli Sadr24661Barghausen18215 72nd AVE South425-251-6222SITE IMPROVEMENT BOND QUANTITY WORKSHEETPROJECT INFORMATIONCITY OF RENTONCITY OF RENTON1 Select the current project status/phase from the following options: For Approval - Preliminary Data Enclosed, pending approval from the City; For Construction - Estimated Data Enclosed, Plans have been approved for contruction by the City; Project Closeout - Final Costs and Quantities Enclosed for Project Close-out SubmittalPhoneEngineer Stamp Required (all cost estimates must have original wet stamp and signature)Clearing and GradingUtility ProvidersN/AProject Location and DescriptionProject Owner InformationVMC MOB Road ImprovementsRenton, WA. 98055Parcel NumberValley Medical Center##-######Page 1 of 1Ref 8-H Bond Quantity WorksheetSECTION I PROJECT INFORMATIONUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 12/27/2017
CED Permit #:########UnitReference #PriceUnitQuantity CostBackfill & compaction-embankmentESC-16.50$ CYCheck dams, 4" minus rockESC-2SWDM 5.4.6.380.00$ EachCatch Basin ProtectionESC-335.50$ Each20710.00Crushed surfacing 1 1/4" minusESC-4WSDOT 9-03.9(3)95.00$ CY DitchingESC-59.00$ CYExcavation-bulkESC-62.00$ CYFence, siltESC-7SWDM 5.4.3.11.50$ LF Fence, Temporary (NGPE)ESC-81.50$ LF Geotextile FabricESC-92.50$ SY Hay Bale Silt TrapESC-100.50$ Each HydroseedingESC-11SWDM 5.4.2.40.80$ SY200160.00Interceptor Swale / DikeESC-121.00$ LF Jute MeshESC-13SWDM 5.4.2.23.50$ SY Level SpreaderESC-141.75$ LF Mulch, by hand, straw, 3" deepESC-15SWDM 5.4.2.12.50$ SY Mulch, by machine, straw, 2" deepESC-16SWDM 5.4.2.12.00$ SY Piping, temporary, CPP, 6"ESC-1712.00$ LF Piping, temporary, CPP, 8"ESC-1814.00$ LFPiping, temporary, CPP, 12"ESC-1918.00$ LF Plastic covering, 6mm thick, sandbaggedESC-20SWDM 5.4.2.34.00$ SY Rip Rap, machine placed; slopesESC-21WSDOT 9-13.1(2)45.00$ CY Rock Construction Entrance, 50'x15'x1'ESC-22SWDM 5.4.4.11,800.00$ Each11,800.00Rock Construction Entrance, 100'x15'x1'ESC-23SWDM 5.4.4.13,200.00$ EachSediment pond riser assemblyESC-24SWDM 5.4.5.22,200.00$ EachSediment trap, 5' high berm ESC-25SWDM 5.4.5.119.00$ LFSed. trap, 5' high, riprapped spillway berm section ESC-26SWDM 5.4.5.170.00$ LF Seeding, by handESC-27SWDM 5.4.2.41.00$ SY Sodding, 1" deep, level groundESC-28SWDM 5.4.2.58.00$ SY Sodding, 1" deep, sloped groundESC-29SWDM 5.4.2.510.00$ SY TESC SupervisorESC-30110.00$ HR20022,000.00Water truck, dust controlESC-31SWDM 5.4.7140.00$ HR24033,600.00UnitReference #PriceUnitQuantity Cost EROSION/SEDIMENT SUBTOTAL:58,270.00SALES TAX @ 10%5,827.00EROSION/SEDIMENT TOTAL:64,097.00(A)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR EROSION & SEDIMENT CONTROLDescription No.(A)WRITE-IN-ITEMS Page 3 of 14Ref 8-H Bond Quantity WorksheetSECTION II.a EROSION_CONTROLUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostGENERAL ITEMS Backfill & Compaction- embankmentGI-16.00$ CY15009,000.00Backfill & Compaction- trenchGI-29.00$ CYClear/Remove Brush, by hand (SY)GI-31.00$ SYBollards - fixedGI-4240.74$ EachBollards - removableGI-5452.34$ EachClearing/Grubbing/Tree RemovalGI-610,000.00$ AcreExcavation - bulkGI-72.00$ CYExcavation - TrenchGI-85.00$ CYFencing, cedar, 6' highGI-920.00$ LFFencing, chain link, 4'GI-1038.31$ LFFencing, chain link, vinyl coated, 6' highGI-1120.00$ LFFencing, chain link, gate, vinyl coated, 20' GI-121,400.00$ EachFill & compact - common barrowGI-1325.00$ CYFill & compact - gravel baseGI-1427.00$ CYFill & compact - screened topsoilGI-1539.00$ CYGabion, 12" deep, stone filled mesh GI-1665.00$ SYGabion, 18" deep, stone filled mesh GI-1790.00$ SYGabion, 36" deep, stone filled meshGI-18150.00$ SYGrading, fine, by handGI-192.50$ SYGrading, fine, with graderGI-202.00$ SYMonuments, 3' LongGI-21250.00$ EachSensitive Areas SignGI-227.00$ EachSodding, 1" deep, sloped groundGI-238.00$ SYSurveying, line & gradeGI-24850.00$ DaySurveying, lot location/linesGI-251,800.00$ Acre0.5900.00Topsoil Type A (imported)GI-2628.50$ CYTraffic control crew ( 2 flaggers )GI-27120.00$ HR20024,000.00Trail, 4" chipped woodGI-288.00$ SYTrail, 4" crushed cinderGI-299.00$ SYTrail, 4" top courseGI-3012.00$ SYConduit, 2"GI-315.00$ LFWall, retaining, concreteGI-3255.00$ SFWall, rockeryGI-3315.00$ SFSUBTOTAL THIS PAGE:33,900.00(B)(C)(D)(E)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR STREET AND SITE IMPROVEMENTSQuantity Remaining (Bond Reduction) (B)(C)Page 4 of 14Ref 8-H Bond Quantity WorksheetSECTION II.b TRANSPORTATIONUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostSITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR STREET AND SITE IMPROVEMENTSQuantity Remaining (Bond Reduction) (B)(C)ROAD IMPROVEMENT/PAVEMENT/SURFACINGAC Grinding, 4' wide machine < 1000syRI-130.00$ SY20600.0010300.00AC Grinding, 4' wide machine 1000-2000syRI-216.00$ SYAC Grinding, 4' wide machine > 2000syRI-310.00$ SYAC Removal/DisposalRI-435.00$ SY1414,935.00135547,425.00Barricade, Type III ( Permanent )RI-556.00$ LFGuard RailRI-630.00$ LFCurb & Gutter, rolledRI-717.00$ LFCurb & Gutter, verticalRI-812.50$ LF7519,387.504775,962.50Curb and Gutter, demolition and disposalRI-918.00$ LF66011,880.00108719,566.00Curb, extruded asphaltRI-105.50$ LFCurb, extruded concreteRI-117.00$ LFSawcut, asphalt, 3" depthRI-121.85$ LF6601,221.00207382.95Sawcut, concrete, per 1" depthRI-133.00$ LFSealant, asphaltRI-142.00$ LFShoulder, gravel, 4" thickRI-1515.00$ SYSidewalk, 4" thickRI-1638.00$ SY62423,712.001736,574.00Sidewalk, 4" thick, demolition and disposalRI-1732.00$ SY2598,288.00541,728.00Sidewalk, 5" thickRI-1841.00$ SYSidewalk, 5" thick, demolition and disposalRI-1940.00$ SYSign, Handicap RI-2085.00$ EachStriping, per stallRI-217.00$ Each535.00Striping, thermoplastic, ( for crosswalk )RI-223.00$ SF7292,187.00323969.00Striping, 4" reflectorized lineRI-230.50$ LF31501,575.00250125.00Additional 2.5" Crushed SurfacingRI-243.60$ SY608.82,191.687562,721.60HMA 1/2" Overlay 1.5" RI-2514.00$ SYHMA 1/2" Overlay 2"RI-2618.00$ SYHMA Road, 2", 4" rock, First 2500 SYRI-2728.00$ SYHMA Road, 2", 4" rock, Qty. over 2500SYRI-2821.00$ SYHMA Road, 4", 6" rock, First 2500 SYRI-2945.00$ SY76134,245.0045020,250.00HMA Road, 4", 6" rock, Qty. over 2500 SYRI-3037.00$ SYHMA Road, 4", 4.5" ATBRI-3138.00$ SYGravel Road, 4" rock, First 2500 SYRI-3215.00$ SYGravel Road, 4" rock, Qty. over 2500 SYRI-3310.00$ SYThickened EdgeRI-348.60$ LFSUBTOTAL THIS PAGE:100,222.18106,039.05(B)(C)(D)(E)Page 5 of 14Ref 8-H Bond Quantity WorksheetSECTION II.b TRANSPORTATIONUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostSITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR STREET AND SITE IMPROVEMENTSQuantity Remaining (Bond Reduction) (B)(C)PARKING LOT SURFACINGNo.2" AC, 2" top course rock & 4" borrowPL-121.00$ SY2" AC, 1.5" top course & 2.5" base coursePL-228.00$ SY50014,000.004" select borrowPL-35.00$ SY1.5" top course rock & 2.5" base coursePL-414.00$ SYSUBTOTAL PARKING LOT SURFACING:14,000.00(B)(C)(D)(E)LANDSCAPING & VEGETATIONNo.Street TreesLA-1Median LandscapingLA-2Right-of-Way LandscapingLA-3Wetland LandscapingLA-4SUBTOTAL LANDSCAPING & VEGETATION:(B)(C)(D)(E)TRAFFIC & LIGHTINGNo.SignsTR-1Street Light System ( # of Poles)TR-2Traffic SignalTR-3Traffic Signal ModificationTR-4SUBTOTAL TRAFFIC & LIGHTING:(B)(C)(D)(E)WRITE-IN-ITEMSSUBTOTAL WRITE-IN ITEMS:STREET AND SITE IMPROVEMENTS SUBTOTAL:100,222.18139,939.05SALES TAX @ 10%10,022.2213,993.91STREET AND SITE IMPROVEMENTS TOTAL:110,244.40153,932.96(B)(C)(D)(E)Page 6 of 14Ref 8-H Bond Quantity WorksheetSECTION II.b TRANSPORTATIONUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostDRAINAGE (CPE = Corrugated Polyethylene Pipe, N12 or Equivalent) For Culvert prices, Average of 4' cover was assumed. Assume perforated PVC is same price as solid pipe.) Access Road, R/DD-126.00$ SY* (CBs include frame and lid)BeehiveD-290.00$ EachThrough-curb Inlet FrameworkD-3400.00$ EachCB Type ID-41,500.00$ Each11,500.00710,500.00CB Type ILD-51,750.00$ EachCB Type II, 48" diameterD-62,300.00$ Each for additional depth over 4' D-7480.00$ FTCB Type II, 54" diameterD-82,500.00$ Each for additional depth over 4'D-9495.00$ FTCB Type II, 60" diameterD-102,800.00$ Each for additional depth over 4'D-11600.00$ FTCB Type II, 72" diameterD-126,000.00$ Each for additional depth over 4'D-13850.00$ FTCB Type II, 96" diameterD-1414,000.00$ Each for additional depth over 4'D-15925.00$ FTTrash Rack, 12"D-16350.00$ EachTrash Rack, 15"D-17410.00$ EachTrash Rack, 18"D-18480.00$ EachTrash Rack, 21"D-19550.00$ EachCleanout, PVC, 4"D-20150.00$ EachCleanout, PVC, 6"D-21170.00$ EachCleanout, PVC, 8"D-22200.00$ EachCulvert, PVC, 4" D-2310.00$ LFCulvert, PVC, 6" D-2413.00$ LFCulvert, PVC, 8" D-2515.00$ LFCulvert, PVC, 12" D-2623.00$ LFCulvert, PVC, 15" D-2735.00$ LFCulvert, PVC, 18" D-2841.00$ LFCulvert, PVC, 24"D-2956.00$ LFCulvert, PVC, 30" D-3078.00$ LFCulvert, PVC, 36" D-31130.00$ LFCulvert, CMP, 8"D-3219.00$ LFCulvert, CMP, 12"D-3329.00$ LFSUBTOTAL THIS PAGE:1,500.0010,500.00(B)(C)(D)(E)Quantity Remaining (Bond Reduction) (B)(C)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESPage 7 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostQuantity Remaining (Bond Reduction) (B)(C)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESDRAINAGE (Continued)Culvert, CMP, 15"D-3435.00$ LFCulvert, CMP, 18"D-3541.00$ LFCulvert, CMP, 24"D-3656.00$ LFCulvert, CMP, 30"D-3778.00$ LFCulvert, CMP, 36"D-38130.00$ LFCulvert, CMP, 48"D-39190.00$ LFCulvert, CMP, 60"D-40270.00$ LFCulvert, CMP, 72"D-41350.00$ LFCulvert, Concrete, 8"D-4242.00$ LFCulvert, Concrete, 12"D-4348.00$ LFCulvert, Concrete, 15"D-4478.00$ LFCulvert, Concrete, 18"D-4548.00$ LFCulvert, Concrete, 24"D-4678.00$ LFCulvert, Concrete, 30"D-47125.00$ LFCulvert, Concrete, 36"D-48150.00$ LFCulvert, Concrete, 42"D-49175.00$ LFCulvert, Concrete, 48"D-50205.00$ LFCulvert, CPE Triple Wall, 6" D-5114.00$ LFCulvert, CPE Triple Wall, 8" D-5216.00$ LFCulvert, CPE Triple Wall, 12" D-5324.00$ LFCulvert, CPE Triple Wall, 15" D-5435.00$ LFCulvert, CPE Triple Wall, 18" D-5541.00$ LFCulvert, CPE Triple Wall, 24" D-5656.00$ LFCulvert, CPE Triple Wall, 30" D-5778.00$ LFCulvert, CPE Triple Wall, 36" D-58130.00$ LFCulvert, LCPE, 6"D-5960.00$ LFCulvert, LCPE, 8"D-6072.00$ LFCulvert, LCPE, 12"D-6184.00$ LFCulvert, LCPE, 15"D-6296.00$ LFCulvert, LCPE, 18"D-63108.00$ LFCulvert, LCPE, 24"D-64120.00$ LFCulvert, LCPE, 30"D-65132.00$ LFCulvert, LCPE, 36"D-66144.00$ LFCulvert, LCPE, 48"D-67156.00$ LFCulvert, LCPE, 54"D-68168.00$ LFSUBTOTAL THIS PAGE:(B)(C)(D)(E)Page 8 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostQuantity Remaining (Bond Reduction) (B)(C)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESDRAINAGE (Continued)Culvert, LCPE, 60"D-69180.00$ LFCulvert, LCPE, 72"D-70192.00$ LFCulvert, HDPE, 6"D-7142.00$ LFCulvert, HDPE, 8"D-7242.00$ LFCulvert, HDPE, 12"D-7374.00$ LFCulvert, HDPE, 15"D-74106.00$ LFCulvert, HDPE, 18"D-75138.00$ LFCulvert, HDPE, 24"D-76221.00$ LFCulvert, HDPE, 30"D-77276.00$ LFCulvert, HDPE, 36"D-78331.00$ LFCulvert, HDPE, 48"D-79386.00$ LFCulvert, HDPE, 54"D-80441.00$ LFCulvert, HDPE, 60"D-81496.00$ LFCulvert, HDPE, 72"D-82551.00$ LFPipe, Polypropylene, 6"D-8384.00$ LFPipe, Polypropylene, 8"D-8489.00$ LF10890.00Pipe, Polypropylene, 12"D-8595.00$ LF121,140.0022821,660.00Pipe, Polypropylene, 15"D-86100.00$ LFPipe, Polypropylene, 18"D-87106.00$ LFPipe, Polypropylene, 24"D-88111.00$ LFPipe, Polypropylene, 30"D-89119.00$ LFPipe, Polypropylene, 36"D-90154.00$ LFPipe, Polypropylene, 48"D-91226.00$ LFPipe, Polypropylene, 54"D-92332.00$ LFPipe, Polypropylene, 60"D-93439.00$ LFPipe, Polypropylene, 72"D-94545.00$ LFCulvert, DI, 6"D-9561.00$ LFCulvert, DI, 8"D-9684.00$ LFCulvert, DI, 12"D-97106.00$ LFCulvert, DI, 15"D-98129.00$ LFCulvert, DI, 18"D-99152.00$ LFCulvert, DI, 24"D-100175.00$ LFCulvert, DI, 30"D-101198.00$ LFCulvert, DI, 36"D-102220.00$ LFCulvert, DI, 48"D-103243.00$ LFCulvert, DI, 54"D-104266.00$ LFCulvert, DI, 60"D-105289.00$ LFCulvert, DI, 72"D-106311.00$ LFSUBTOTAL THIS PAGE:1,140.0022,550.00(B)(C)(D)(E)Page 9 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostQuantity Remaining (Bond Reduction) (B)(C)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESSpecialty Drainage ItemsDitching SD-19.50$ CYFlow Dispersal Trench (1,436 base+)SD-328.00$ LF French Drain (3' depth)SD-426.00$ LFGeotextile, laid in trench, polypropyleneSD-53.00$ SYMid-tank Access Riser, 48" dia, 6' deepSD-62,000.00$ EachPond Overflow SpillwaySD-716.00$ SYRestrictor/Oil Separator, 12"SD-81,150.00$ EachRestrictor/Oil Separator, 15"SD-91,350.00$ EachRestrictor/Oil Separator, 18"SD-101,700.00$ EachRiprap, placedSD-1142.00$ CYTank End Reducer (36" diameter)SD-121,200.00$ EachInfiltration pond testingSD-13125.00$ HRPermeable PavementSD-14Permeable Concrete SidewalkSD-15Culvert, Box __ ft x __ ftSD-16SUBTOTAL SPECIALTY DRAINAGE ITEMS:(B)(C)(D)(E)STORMWATER FACILITIES (Include Flow Control and Water Quality Facility Summary Sheet and Sketch)Detention PondSF-1Each Detention TankSF-2Each Detention VaultSF-3$250,000Each 1250,000.00Infiltration PondSF-4Each Infiltration TankSF-5Each Infiltration VaultSF-6Each Infiltration TrenchesSF-7Each Basic Biofiltration SwaleSF-8Each Wet Biofiltration SwaleSF-9Each WetpondSF-10Each WetvaultSF-11Each Sand FilterSF-12Each Sand Filter VaultSF-13Each Linear Sand FilterSF-14Each Proprietary FacilitySF-1540,000.00$ Each 140,000.00Bioretention FacilitySF-16Each SUBTOTAL STORMWATER FACILITIES:290,000.00(B)(C)(D)(E)Page 10 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostQuantity Remaining (Bond Reduction) (B)(C)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR DRAINAGE AND STORMWATER FACILITIESWRITE-IN-ITEMS (INCLUDE ON-SITE BMPs)WI-1WI-2WI-3WI-4WI-5WI-6WI-7WI-8WI-9WI-10WI-11WI-12WI-13WI-14WI-15SUBTOTAL WRITE-IN ITEMS:DRAINAGE AND STORMWATER FACILITIES SUBTOTAL:1,500.00300,500.00SALES TAX @ 10%150.0030,050.00DRAINAGE AND STORMWATER FACILITIES TOTAL:1,650.00330,550.00(B) (C) (D) (E)Page 11 of 14Ref 8-H Bond Quantity WorksheetSECTION II.c DRAINAGEUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostConnection to Existing WatermainW-12,000.00$ EachDuctile Iron Watermain, CL 52, 4 Inch DiameterW-250.00$ LFDuctile Iron Watermain, CL 52, 6 Inch DiameterW-356.00$ LFDuctile Iron Watermain, CL 52, 8 Inch DiameterW-460.00$ LFDuctile Iron Watermain, CL 52, 10 Inch DiameterW-570.00$ LFDuctile Iron Watermain, CL 52, 12 Inch DiameterW-680.00$ LFGate Valve, 4 inch DiameterW-7500.00$ EachGate Valve, 6 inch DiameterW-8700.00$ EachGate Valve, 8 Inch DiameterW-9800.00$ EachGate Valve, 10 Inch DiameterW-101,000.00$ EachGate Valve, 12 Inch DiameterW-111,200.00$ EachFire Hydrant AssemblyW-124,000.00$ EachPermanent Blow-Off AssemblyW-131,800.00$ EachAir-Vac Assembly, 2-Inch DiameterW-142,000.00$ EachAir-Vac Assembly, 1-Inch DiameterW-151,500.00$ EachCompound Meter Assembly 3-inch DiameterW-168,000.00$ EachCompound Meter Assembly 4-inch DiameterW-179,000.00$ EachCompound Meter Assembly 6-inch DiameterW-1810,000.00$ EachPressure Reducing Valve Station 8-inch to 10-inchW-1920,000.00$ EachWATER SUBTOTAL:SALES TAX @ 10%WATER TOTAL:(B) (C) (D) (E)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR WATERQuantity Remaining (Bond Reduction) (B)(C)Page 12 of 14Ref 8-H Bond Quantity WorksheetSECTION II.d WATERUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
CED Permit #:########ExistingFuture PublicPrivateRight-of-WayImprovementsImprovements(D) (E)DescriptionNo. Unit PriceUnitQuant.CostQuant.CostQuant.CostQuant.CostClean OutsSS-11,000.00$ EachGrease Interceptor, 500 gallonSS-28,000.00$ EachGrease Interceptor, 1000 gallonSS-310,000.00$ EachGrease Interceptor, 1500 gallonSS-415,000.00$ EachSide Sewer Pipe, PVC. 4 Inch DiameterSS-580.00$ LFSide Sewer Pipe, PVC. 6 Inch DiameterSS-695.00$ LFSewer Pipe, PVC, 8 inch DiameterSS-7105.00$ LFSewer Pipe, PVC, 12 Inch DiameterSS-8120.00$ LFSewer Pipe, DI, 8 inch DiameterSS-9115.00$ LFSewer Pipe, DI, 12 Inch DiameterSS-10130.00$ LFManhole, 48 Inch DiameterSS-116,000.00$ EachManhole, 54 Inch DiameterSS-136,500.00$ EachManhole, 60 Inch DiameterSS-157,500.00$ EachManhole, 72 Inch DiameterSS-178,500.00$ EachManhole, 96 Inch DiameterSS-1914,000.00$ EachPipe, C-900, 12 Inch DiameterSS-21180.00$ LFOutside DropSS-241,500.00$ LSInside DropSS-251,000.00$ LSSewer Pipe, PVC, ____ Inch DiameterSS-26Lift Station (Entire System)SS-27LSSANITARY SEWER SUBTOTAL:SALES TAX @ 10%SANITARY SEWER TOTAL:(B) (C) (D) (E)SITE IMPROVEMENT BOND QUANTITY WORKSHEETFOR SANITARY SEWERQuantity Remaining (Bond Reduction) (B)(C)Page 13 of 14Ref 8-H Bond Quantity WorksheetSECTION II.e SANITARY SEWERUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
Planning Division |1055 South Grady Way – 6th Floor | Renton, WA 98057 (425) 430-7200Date:Name:Project Name: PE Registration No:CED Plan # (LUA):Firm Name:CED Permit # (U):Firm Address:Site Address:Phone No.Parcel #(s):Email Address:Project Phase: Site Restoration/Erosion Sediment Control Subtotal (a)Existing Right-of-Way Improvements Subtotal (b)(b)110,244.40$ Future Public Improvements Subtotal(c)-$ Stormwater & Drainage Facilities (Public & Private) Subtotal(d)(d)332,200.00$ (e)(f)Site RestorationCivil Construction PermitMaintenance Bond88,488.88$ Bond Reduction2Construction Permit Bond Amount 3Minimum Bond Amount is $10,000.001 Estimate Only - May involve multiple and variable components, which will be established on an individual basis by Development Engineering.2 The City of Renton allows one request only for bond reduction prior to the maintenance period. Reduction of not more than 70% of the original bond amount, provided that the remaining 30% willcover all remaining items to be constructed. 3 Required Bond Amounts are subject to review and modification by Development Engineering.* Note: The word BOND as used in this document means any financial guarantee acceptable to the City of Renton.** Note: All prices include labor, equipment, materials, overhead and profit. EST1((b) + (c) + (d)) x 20%-$ MAINTENANCE BOND */**(after final acceptance of construction)64,097.00$ 110,244.40$ 497,566.60$ 64,097.00$ -$ 332,200.00$ -$ 561,663.60$ P (a) x 100%SITE IMPROVEMENT BOND QUANTITY WORKSHEET BOND CALCULATIONS10/9/2017Ali Sadr24661BarghausenR((b x 150%) + (d x 100%))S(e) x 150% + (f) x 100%Bond Reduction: Existing Right-of-Way Improvements (Quantity Remaining)2Bond Reduction: Stormwater & Drainage Facilities (Quantity Remaining)2T(P +R - S)Prepared by:Project InformationCONSTRUCTION BOND AMOUNT */**(prior to permit issuance)425-251-6222asadr@bargausen.comValley Medical Center Medical Office Building##-######400 South 43rd StreetParcel NumberFOR CONSTRUCTION########18215 72nd AVE SouthPage 14 of 14Ref 8-H Bond Quantity WorksheetSECTION III. BOND WORKSHEETUnit Prices Updated: 06/14/2016Version: 04/26/2017Printed 10/31/2017
Return Address:
City Clerk’s Office City of Renton
1055 S Grady Way
Renton, WA 98057
DECLARATION OF COVENANT FOR INSPECTION AND
MAINTENANCE OF STORMWATER FACILITIES AND BMPS
Grantor:
Grantee: City of Renton Legal Description:
Assessor's Tax Parcel ID#:
IN CONSIDERATION of the approved City of Renton ___________________________ permit
for application file No. LUA/SWP_______________________ relating to the real property ("Property") described above, the Grantor(s), the owner(s) in fee of that Property, hereby covenants(covenant) with the
City of Renton, a political subdivision of the state of Washington, that he/she(they) will observe, consent to, and abide by the conditions and obligations set forth and described in Paragraphs 1 through 10 below with regard to the Property, and hereby grants(grant) an easement as described in Paragraphs 2 and 3.
Grantor(s) hereby grants(grant), covenants(covenant), and agrees(agree) as follows:
1. The Grantor(s) or his/her(their) successors in interest and assigns ("Owners of the described
property") shall at their own cost, operate, maintain, and keep in good repair, the Property's stormwater
facilities and/or best management practices ("BMPs") constructed as required in the approved construction plans and specifications __________ on file with the City of Renton and submitted to the
City of Renton for the review and approval of permit(s) _____________________________. The
property's stormwater facilities and/or best management practices ("BMPs") are shown and/or listed on Exhibit A. The property’s stormwater facilities and/or BMPs shall be maintained in compliance with the
operation and maintenance schedule included and attached herein as Exhibit B. Stormwater facilities include pipes, swales, tanks, vaults, ponds, and other engineered structures designed to manage and/or treat stormwater on the Property. Stormwater BMPs include dispersion and infiltration devices, native
vegetated areas, permeable pavements, vegetated roofs, rainwater harvesting systems, reduced impervious
surface coverage, and other measures designed to reduce the amount of stormwater runoff on the Property.
2. City of Renton shall have the right to ingress and egress over those portions of the Property necessary to perform inspections of the stormwater facilities and BMPs and conduct maintenance activities specified in this Declaration of Covenant and in accordance with RMC 4-6-030.
3. If City of Renton determines that maintenance or repair work is required to be done to any of the stormwater facilities or BMPs, City of Renton shall give notice of the specific maintenance and/or
repair work required pursuant to RMC 4-6-030. The City shall also set a reasonable time in which such
Page 1 of 3 Form Approved by City Attorney 10/2013
Valley Medical Center
Northeast quarter of Section 31, Township 23 North, Range 5 East,
Willamette Meridian, City of Renton, King County, Washington.
Portions of 8857670010 and 8857670100
Civil Construction
work is to be completed by the Owners. If the above required maintenance or repair is not completed
within the time set by the City, the City may perform the required maintenance or repair, and hereby is
given access to the Property, subject to the exclusion in Paragraph 2 above, for such purposes. Written notice will be sent to the Owners stating the City’s intention to perform such work. This work will not
commence until at least seven (7) days after such notice is mailed. If, within the sole discretion of the
City, there exists an imminent or present danger, the seven (7) day notice period will be waived and maintenance and/or repair work will begin immediately.
4. If at any time the City of Renton reasonably determines that a stormwater facility or BMP on the Property creates any of the hazardous conditions listed in RMC 4-4-060 G or relevant municipal successor's codes as applicable and herein incorporated by reference, the City may take measures
specified therein.
5. The Owners shall assume all responsibility for the cost of any maintenance or repair work completed by the City as described in Paragraph 3 or any measures taken by the City to address hazardous
conditions as described in Paragraph 4. Such responsibility shall include reimbursement to the City within thirty (30) days of the receipt of the invoice for any such work performed. Overdue payments will require payment of interest at the current legal rate as liquidated damages. If legal action ensues, the
prevailing party is entitled to recover reasonable litigation costs and attorney’s fees.
6. The Owners are hereby required to obtain written approval from City of Renton prior to
filling, piping, cutting, or removing vegetation (except in routine landscape maintenance) in open
vegetated stormwater facilities (such as swales, channels, ditches, ponds, etc.), or performing any alterations or modifications to the stormwater facilities and BMPs referenced in this Declaration of
Covenant.
7. Any notice or consent required to be given or otherwise provided for by the provisions of this Agreement shall be effective upon personal delivery, or three (3) days after mailing by Certified Mail,
return receipt requested.
8. With regard to the matters addressed herein, this agreement constitutes the entire agreement between the parties, and supersedes all prior discussions, negotiations, and all agreements whatsoever
whether oral or written.
9. This Declaration of Covenant is intended to protect the value and desirability of the real property described above, and shall inure to the benefit of all the citizens of the City of Renton and its
successors and assigns. This Declaration of Covenant shall run with the land and be binding upon Grantor(s), and Grantor's(s') successors in interest, and assigns.
10. This Declaration of Covenant may be terminated by execution of a written agreement by the
Owners and the City that is recorded by King County in its real property records.
IN WITNESS WHEREOF, this Declaration of Covenant for the Inspection and Maintenance of
Stormwater Facilities and BMPs is executed this _____ day of ____________________, 20_____.
GRANTOR, owner of the Property
GRANTOR, owner of the Property
Page 2 of 3 Form Approved by City Attorney 10/2013
STATE OF WASHINGTON ) COUNTY OF KING )ss.
On this day personally appeared before me:
, to me known to be the individual(s) described in and who executed the within and foregoing instrument and acknowledged that they signed the same as
their free and voluntary act and deed, for the uses and purposes therein stated.
Given under my hand and official seal this _____ day of ____________________, 20_____.
Printed name Notary Public in and for the State of Washington,
residing at
My appointment expires
Page 3 of 3 Form Approved by City Attorney 10/2013
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BAR G HAU
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ENCONSUL
TING ENGI NE E R S , INC.
MAINTENANCE INSTRUCTIONS FOR VEGETATED ROOFS
Your property contains an on-site BMP (best management practice) called a “vegetated roof,” which
was installed to minimize the stormwater runoff impacts of the impervious surfaces on your property.
Vegetated roofs (also called green roofs) consist of a pervious growing medium, plants, and a moisture barrier. The benefits of this device are a reduction in runoff peaks and volumes due to the storage
capabilities of the soil and increased rate of evapotranspiration. This on-site BMP shall be maintained
per Appendix A of the City of Renton’s Surface Water Design Manual.
MAINTENANCE RESTRICTIONS
• The composition and area of vegetated roof as depicted by the site plan and design details must be maintained and may not be changed without written approval from the City of Renton or
through a future development permit from the City of Renton.
• Vegetated roofs must not be subject to any use that would significantly compact the soil.
INSPECTION FREQUENCY AND MAINTENANCE GUIDELINES
Vegetated roofs (also called green roofs) consist of a pervious growing medium, plants, and a moisture
barrier:
• Vegetated roofs must be inspected annually for physical defects and to make sure the vegetation is in good condition.
• If erosion channels or bare spots are evident, they should be stabilized with additional soil similar to the original material.
• A supplemental watering program may be needed the first year to ensure the long-term survival of the roof's vegetation.
• Vegetation should be maintained as follows:
(1) Vegetated roofs must not be subject to any use that would significantly compact the soil;
(2) Replace all dead vegetation as soon as possible;
(3) Remove fallen leaves and debris;
(4) Remove all noxious vegetation when discovered;
(5) Manually weed without herbicides or pesticides
RECORDING REQUIREMENT
These vegetated roof on-site BMP maintenance and operation instructions must be recorded as an
attachment to the required declaration of covenant and grant of easement per Requirement 3 of Section C.1.3.4 of the City of Renton Surface Water Design Manual. The intent of these instructions is to explain to future property owners, the purpose of the BMP and how it must be maintained and
operated. These instructions are intended to be a minimum; the City of Renton may require additional instructions based on site-specific conditions. See the City of Renton’s Surface Water Design Manual website for additional information and updates.
TYPICAL VEGETATED ROOF CROSS-SECTION
Page 24 American Hydrotech, Inc. - Contractor Training Manual - © 2012
MAINTENANCE INTRODUCTION
The Importance of Maintenance
A successful vegetative roof is one that receives proper maintenance,
starting with the installation of the plant material. There is no such
thing as a no-maintenance vegetative roof. Keeping a watchful eye on
the roof will maximize plant health, maintain the aesthetics of the roof,
and ensure any issues such as clogged drains, wind erosion, and
irrigation malfunctions are handled before they become problems. A
well thought out and executed maintenance plan will make certain the
vegetative roof is performing as intended and meets the owner’s
expectations.
What You Need to Know
The plan for maintenance of a vegetative roof must be considered in
the design stage and in place before its installation so the roof isn’t
neglected immediately after completion. There may be an extended
period of time between the installation of the plant material and when
the owner takes possession/responsibility. During this time it may not
be clear where the maintenance responsibility lies, especially when the
installing contractor is not responsible for the roof’s initial and/or long
term maintenance. The owner must understand what is required in
order to protect their investment. Each project is unique, and the best
way to handle this transition period will vary.
As the party responsible for the maintenance of a vegetative roof, it is
important to understand what is required in order to keep valid any
warranties associated with that roof. This includes not only performing
the maintenance in a professional manner but also documenting and
reporting the maintenance performed and the condition of the roof:
x Sign and return the Acknowledgment of Receipt page stating you
understand the tasks to be performed and the schedule on which
they will be performed.
x Conduct maintenance visits to the roof and perform the tasks
outlined in the schedule as required.
x Complete a Visitation Checklist at every required time interval
listed on the Checklist and return it with photographs of sufficient
number to document the general condition of the roof and any
areas of concern.
American Hydrotech, Inc. - Contractor Training Manual - © 2012 Page 25
ACKNOWLEDGMENT OF RECEIPT
Visitation Checklist
All pertinent information recorded by the Landscape Maintenance Contractor shall be submitted to both the Property Owner
and Hydrotech at the required intervals listed on the Visitation Checklist and within ten (10) days of the date of the
maintenance visit. Each submission shall include the following:
x A signed and dated Visitation Checklist verifying the tasks performed and thoroughly and completely describing any
items of concern.
x Photographs of sufficient number to document the general condition of the roof and any areas of concern.
American Hydrotech Inc. Extensive Vegetation Warranty
Specific dates of maintenance/warranty visits and site inspections are flexible, but the contractor must perform the required
tasks within the specified time frame. Timing of visits may be delayed, rescheduled, or added depending on factors such as
climatic conditions, growing seasons, client concerns, or acts of nature. Coverage rates should be as follows:
x Sedum Plugs and Cuttings – Thrive and Coverage: 50% minimum coverage after the first year, 80% minimum
coverage after the second year.
x Sedum Carpet and Sedum Tile – Thrive and Coverage: 90% minimum coverage after the first and second years.
x All other vegetation - Thrive only: Plants selected by Hydrotech will do well in the environment in which they were
installed.
At the end of the two year maintenance period Hydrotech’s warranty obligations to the owner will have been fulfilled.
Determining Plant Coverage
Warranty coverage percentage is to be determined for each 1000 square foot grid area of roof surface. Non-covered areas
smaller than one-half of a square foot will not be counted against the overall warranted coverage percentage. Overall
coverage is based on a visual inspection under these terms and is subject to Hydrotech approval prior to shipping any
supplemental plant material. The maintenance contractor and/or owner is responsible for all labor costs during the 2-year
maintenance period.
I, the undersigned, acknowledge that I have thoroughly read and understand the American Hydrotech, Inc.’s
Extensive Garden Roof Maintenance Plan and agree to meet the requirements stated within. I further acknowledge
receipt of the accompanying Visitation Checklist that is to be periodically submitted to both the Property Owner
and American Hydrotech, Inc.
Maintenance Contractor: ____________________________________________
Print Name: ____________________________________________ Title:______________________
Maintenance Contractor Representative
Signature: ____________________________________________ Date:______________________
Please return to: American Hydrotech, Inc. Phone: (312) 337-4998 Email: GardenRoof@hydrotechusa.com
303 E. Ohio Street, Suite 2700 Fax: (312) 661-0731
Chicago, IL 60611
Page 26 American Hydrotech, Inc. - Contractor Training Manual - © 2012
PRIMARY MAINTENANCE TASKS
Watering
x 1”-1½” of water per required visit in order to thoroughly saturate
growing media. In periods of drought (4-6 weeks) additional watering
is required
x Rotate any temporary irrigation systems as necessary
x Watering requirements can vary based on climate and the type of
vegetation. Contact Hydrotech with any questions regarding a specific
project
Permanent Irrigation (drip or overhead spray irrigation, if
present)
x Check that the system is functioning properly
x Check timers
x Make any necessary adjustments to spray patterns to ensure proper
coverages
x Winterize when necessary
x If drip irrigation is present, overhead watering is still necessary through
establishment (1st Quarter)
Drainage/Overall Roof Inspection:
x Make sure drains are functioning properly
x Clear drains of any debris, including plant material, soil and other
foreign objects
x Report any waterproofing issues or unsecured flashings
American Hydrotech, Inc. - Contractor Training Manual - © 2012 Page 27
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PRIMARY MAINTENANCE TASKS
Hand Weeding:
x Be aware of which plants are intended to be growing on the roof and which ones aren’t. Remove any plants not
intended to be growing on the roof.
x Please contact Hydrotech if you do not have a list of the plants originally installed.
x Prompt removal of weeds will prevent them from becoming a much larger future problem. Certain weeds require
specialized handling and treatment to minimize or eliminate future re-growth.
x Remove ALL plants from Vegetation Free Zones at perimeters, drains and other penetrations.
For more serious weed problems, please contact Hydrotech for alternative methods of weed control.
Poplar seedlings
Purslane Lambsquarter
Nut Sedge
Spurge
Page 28 American Hydrotech, Inc. - Contractor Training Manual - © 2012
SECONDARY MAINTENANCE TASKS
General Plant Inspection
x Check plant material for overall health
x Look for signs of pests or disease
x Replant any viable plants, including Sedum Carpet and Sedum Tile as well as GardMat, that have been uprooted by
wind, erosion, or animals
LiteTop® Growing Media Replacement
x Replace LiteTop Growing Media lost or displaced by wind or water erosion
x Report any major erosion issues to Hydrotech immediately
Debris and Trash Removal
x Remove and properly dispose of any foreign objects, debris or garbage
x Make sure any recyclable materials are placed in the proper receptacles
x Remove any loose metal plates from GardMat Disk Anchors. At the end of the two-year maintenance period, all
metal plates should be removed control
Plant Replacement
x See Hydrotech’s extensive vegetation warranty for plant performance standards
x Replace plants as necessary. Any warranty claims must be validated by a Hydrotech representative before
replacement plants can be ordered
OPTIONAL TASKS
LiteTop Growing Media Testing and Monitoring
x Test for pH, nutrient levels, salt content, etc. Contact Hydrotech for approved soil testing facilities.
x After analysis, Hydrotech can assist in determining any needed solutions.
Fertilizer Application
x Do not apply fertilizer without the consent of Hydrotech and the Property Owner.
x Hydrotech can make recommendations for appropriate products.
Pesticide Application
x Do not apply pesticide without the consent of Hydrotech and the Property Owner.
x Hydrotech can make recommendations for appropriate products and procedures.
Herbicide Application
x Do not apply herbicide without the consent of Hydrotech and the Property Owner.
x Be careful not to impact the desirable plant material.
x Hydrotech can make recommendations for appropriate products and procedures.
American Hydrotech, Inc. - Contractor Training Manual - © 2012 Page 29
MAINTENANCE SCHEDULE
Please note the
schedule of tasks
listed may vary based
on the region in which
the project is located
and the time of year
the project was
installed.
If the growing season
ends before the First
Quarter tasks have
been performed in
their entirety, the
contractor must start
at that point after last
frost in the spring.
Some tasks may not
need to be performed
at every scheduled
visit.
Please contact
Hydrotech with any
specific questions.
Page 30 American Hydrotech, Inc. - Contractor Training Manual - © 2012
VISITATION CHECKLIST
PROJECT NAME:
Location: Date of Visit:
Installation Contractor: Date of Installation:
Maintenance Contractor: Maint. Contract in place:
Yes
No
Water Sources at roof: Volume (GPM) Pressure (PSI) Length of Contract:
An in-place and active maintenance contract is required for the warranty to be in effect.
Original Plant Material (check all that apply):
Plugs
Cuttings
Sedum Carpet
Sedum Tile
Garden Tray
Other:_____________
Scheduled Visit (check one):(Note:A visitation checklist is NOT required with every visit but should be submitted at the frequency outlined below. Consult the
maintenance schedule on the previous page for a recommended visit schedule. Dependent on the date of installation and regional
and climatic conditions, the frequency of maintenance may vary. Contact Hydrotech for details.
1st Quarter by Week: 1 2 3 4 5 6 7 8 9 10 11 12
First Year by Month: 1 2 3 4 5 6 7 8 9 10 11 12
see 1st Quarter above
Second Year by Quarter: 1 2 3 4
Photos submitted digitally?
Yes
No (See next page for instructions on submitting photos)
Primary Tasks Comments:Check all that apply
Watering
Irrigation Inspection
Drainage Inspection
Hand Weeding
Secondary Tasks Comments:Check all that apply
General Plant Inspection
LiteTop Replacement
Debris / Trash Removal
Plant Replacement
Optional Tasks Comments:
(list any tasks performed)
Additional comments
Estimated Plant Coverage at time of this visit: _______% Copy submitted to Property Owner?
Yes
No
I hereby certify that the above tasks have been performed in accordance with the
American Hydrotech, Inc. Garden Roof Maintenance Plan.
Print Name: Title:
Maintenance Contractor Representative
Signature: Date:
Please return to: American Hydrotech, Inc. Phone: (312) 337-4998 Email: GardenRoof@hydrotechusa.com
303 E. Ohio Street, Suite 2700 Fax: (312) 661-0731
Chicago, IL 60611
American Hydrotech, Inc. - Contractor Training Manual - © 2012 Page 31
INSTRUCTION FOR SUBMITTING PHOTOS
x Installation and Maintenance Visitation Photos:
o Provide a sufficient number (10-20) of high-resolution digital
photographs during maintenance visits to Hydrotech. When in doubt,
take a picture to help fully document the installation and the condition
of the roof during the maintenance visits.
o Take photos of all parts of the Garden Roof installation including
perimeters, vegetation free zones, inspection chambers, ladder
areas, and other areas of interest.
o This documentation is valuable to the maintenance contractor. It is
proof that they are following the Hydrotech warranty requirements.
x File Preparation:
o High resolution files should be greater that 250Kb in size. Low-
resolution files (e.g. photos taken from cell phones) are often blurry
and do not capture enough fine detail. Photos of cuttings that are
rooting as well as plugs, sedum tile and carpet should be made using
close-up or macro camera settings.
o Please include project name and date in the file name. For example:
Project Name – 12-21-2011- photo 1
Project Name – 12-21-2011- photo 2
Project Name – 12-21-2011- photo 3
x Uploading
o Combining single photos into ZIP files will save time during the
uploading and downloading process. There are a number of ZIP file
utilities available on the Internet.
o To easily transmit your photos, log onto a file sharing website such as
www.yousendit.com. This particular website has a free trial service to
upload large batches of photos and other documents. This eliminates
clogging up your e-mail server and Hydrotech’s server.
o Use this e-mail address:gardenroof@hydrotechusa.com and
reference the project name and Hydrotech contact in the e-mail.
o This website will send an e-mail recipient that the photos are available
for downloading. This website has the ability to notify multiple people
that the photos are available. The e-mails contain a link that directs
Hydrotech staff to a location where the photos can be downloaded.
o If you need assistance, please contact Hydrotech at 312.337.4998.
Clear, close-up photos are important in determining the
growth activity of the Garden Roof, especially for cuttings.
Take as many photos as needed to adequately
document the Garden Roof installation and current
conditions during maintenance visits. Most
projects will require multiple photos to sufficiently
Tab 10.0
MAINTENANCE INSTRUCTIONS FOR VEGETATED ROOFS
Your property contains an on-site BMP (best management practice) called a “vegetated roof,” which
was installed to minimize the stormwater runoff impacts of the impervious surfaces on your property.
Vegetated roofs (also called green roofs) consist of a pervious growing medium, plants, and a moisture barrier. The benefits of this device are a reduction in runoff peaks and volumes due to the storage
capabilities of the soil and increased rate of evapotranspiration. This on-site BMP shall be maintained
per Appendix A of the City of Renton’s Surface Water Design Manual.
MAINTENANCE RESTRICTIONS
• The composition and area of vegetated roof as depicted by the site plan and design details must be maintained and may not be changed without written approval from the City of Renton or
through a future development permit from the City of Renton.
• Vegetated roofs must not be subject to any use that would significantly compact the soil.
INSPECTION FREQUENCY AND MAINTENANCE GUIDELINES
Vegetated roofs (also called green roofs) consist of a pervious growing medium, plants, and a moisture
barrier:
• Vegetated roofs must be inspected annually for physical defects and to make sure the vegetation is in good condition.
• If erosion channels or bare spots are evident, they should be stabilized with additional soil similar to the original material.
• A supplemental watering program may be needed the first year to ensure the long-term survival of the roof's vegetation.
• Vegetation should be maintained as follows:
(1) Vegetated roofs must not be subject to any use that would significantly compact the soil;
(2) Replace all dead vegetation as soon as possible;
(3) Remove fallen leaves and debris;
(4) Remove all noxious vegetation when discovered;
(5) Manually weed without herbicides or pesticides
RECORDING REQUIREMENT
These vegetated roof on-site BMP maintenance and operation instructions must be recorded as an
attachment to the required declaration of covenant and grant of easement per Requirement 3 of Section C.1.3.4 of the City of Renton Surface Water Design Manual. The intent of these instructions is to explain to future property owners, the purpose of the BMP and how it must be maintained and
operated. These instructions are intended to be a minimum; the City of Renton may require additional instructions based on site-specific conditions. See the City of Renton’s Surface Water Design Manual website for additional information and updates.
TYPICAL VEGETATED ROOF CROSS-SECTION
Page 24 American Hydrotech, Inc. - Contractor Training Manual - © 2012
MAINTENANCE INTRODUCTION
The Importance of Maintenance
A successful vegetative roof is one that receives proper maintenance,
starting with the installation of the plant material. There is no such
thing as a no-maintenance vegetative roof. Keeping a watchful eye on
the roof will maximize plant health, maintain the aesthetics of the roof,
and ensure any issues such as clogged drains, wind erosion, and
irrigation malfunctions are handled before they become problems. A
well thought out and executed maintenance plan will make certain the
vegetative roof is performing as intended and meets the owner’s
expectations.
What You Need to Know
The plan for maintenance of a vegetative roof must be considered in
the design stage and in place before its installation so the roof isn’t
neglected immediately after completion. There may be an extended
period of time between the installation of the plant material and when
the owner takes possession/responsibility. During this time it may not
be clear where the maintenance responsibility lies, especially when the
installing contractor is not responsible for the roof’s initial and/or long
term maintenance. The owner must understand what is required in
order to protect their investment. Each project is unique, and the best
way to handle this transition period will vary.
As the party responsible for the maintenance of a vegetative roof, it is
important to understand what is required in order to keep valid any
warranties associated with that roof. This includes not only performing
the maintenance in a professional manner but also documenting and
reporting the maintenance performed and the condition of the roof:
x Sign and return the Acknowledgment of Receipt page stating you
understand the tasks to be performed and the schedule on which
they will be performed.
x Conduct maintenance visits to the roof and perform the tasks
outlined in the schedule as required.
x Complete a Visitation Checklist at every required time interval
listed on the Checklist and return it with photographs of sufficient
number to document the general condition of the roof and any
areas of concern.
American Hydrotech, Inc. - Contractor Training Manual - © 2012 Page 25
ACKNOWLEDGMENT OF RECEIPT
Visitation Checklist
All pertinent information recorded by the Landscape Maintenance Contractor shall be submitted to both the Property Owner
and Hydrotech at the required intervals listed on the Visitation Checklist and within ten (10) days of the date of the
maintenance visit. Each submission shall include the following:
x A signed and dated Visitation Checklist verifying the tasks performed and thoroughly and completely describing any
items of concern.
x Photographs of sufficient number to document the general condition of the roof and any areas of concern.
American Hydrotech Inc. Extensive Vegetation Warranty
Specific dates of maintenance/warranty visits and site inspections are flexible, but the contractor must perform the required
tasks within the specified time frame. Timing of visits may be delayed, rescheduled, or added depending on factors such as
climatic conditions, growing seasons, client concerns, or acts of nature. Coverage rates should be as follows:
x Sedum Plugs and Cuttings – Thrive and Coverage: 50% minimum coverage after the first year, 80% minimum
coverage after the second year.
x Sedum Carpet and Sedum Tile – Thrive and Coverage: 90% minimum coverage after the first and second years.
x All other vegetation - Thrive only: Plants selected by Hydrotech will do well in the environment in which they were
installed.
At the end of the two year maintenance period Hydrotech’s warranty obligations to the owner will have been fulfilled.
Determining Plant Coverage
Warranty coverage percentage is to be determined for each 1000 square foot grid area of roof surface. Non-covered areas
smaller than one-half of a square foot will not be counted against the overall warranted coverage percentage. Overall
coverage is based on a visual inspection under these terms and is subject to Hydrotech approval prior to shipping any
supplemental plant material. The maintenance contractor and/or owner is responsible for all labor costs during the 2-year
maintenance period.
I, the undersigned, acknowledge that I have thoroughly read and understand the American Hydrotech, Inc.’s
Extensive Garden Roof Maintenance Plan and agree to meet the requirements stated within. I further acknowledge
receipt of the accompanying Visitation Checklist that is to be periodically submitted to both the Property Owner
and American Hydrotech, Inc.
Maintenance Contractor: ____________________________________________
Print Name: ____________________________________________ Title:______________________
Maintenance Contractor Representative
Signature: ____________________________________________ Date:______________________
Please return to: American Hydrotech, Inc. Phone: (312) 337-4998 Email: GardenRoof@hydrotechusa.com
303 E. Ohio Street, Suite 2700 Fax: (312) 661-0731
Chicago, IL 60611
Page 26 American Hydrotech, Inc. - Contractor Training Manual - © 2012
PRIMARY MAINTENANCE TASKS
Watering
x 1”-1½” of water per required visit in order to thoroughly saturate
growing media. In periods of drought (4-6 weeks) additional watering
is required
x Rotate any temporary irrigation systems as necessary
x Watering requirements can vary based on climate and the type of
vegetation. Contact Hydrotech with any questions regarding a specific
project
Permanent Irrigation (drip or overhead spray irrigation, if
present)
x Check that the system is functioning properly
x Check timers
x Make any necessary adjustments to spray patterns to ensure proper
coverages
x Winterize when necessary
x If drip irrigation is present, overhead watering is still necessary through
establishment (1st Quarter)
Drainage/Overall Roof Inspection:
x Make sure drains are functioning properly
x Clear drains of any debris, including plant material, soil and other
foreign objects
x Report any waterproofing issues or unsecured flashings
American Hydrotech, Inc. - Contractor Training Manual - © 2012 Page 27
Ox
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Oxalis
PRIMARY MAINTENANCE TASKS
Hand Weeding:
x Be aware of which plants are intended to be growing on the roof and which ones aren’t. Remove any plants not
intended to be growing on the roof.
x Please contact Hydrotech if you do not have a list of the plants originally installed.
x Prompt removal of weeds will prevent them from becoming a much larger future problem. Certain weeds require
specialized handling and treatment to minimize or eliminate future re-growth.
x Remove ALL plants from Vegetation Free Zones at perimeters, drains and other penetrations.
For more serious weed problems, please contact Hydrotech for alternative methods of weed control.
Poplar seedlings
Purslane Lambsquarter
Nut Sedge
Spurge
Page 28 American Hydrotech, Inc. - Contractor Training Manual - © 2012
SECONDARY MAINTENANCE TASKS
General Plant Inspection
x Check plant material for overall health
x Look for signs of pests or disease
x Replant any viable plants, including Sedum Carpet and Sedum Tile as well as GardMat, that have been uprooted by
wind, erosion, or animals
LiteTop® Growing Media Replacement
x Replace LiteTop Growing Media lost or displaced by wind or water erosion
x Report any major erosion issues to Hydrotech immediately
Debris and Trash Removal
x Remove and properly dispose of any foreign objects, debris or garbage
x Make sure any recyclable materials are placed in the proper receptacles
x Remove any loose metal plates from GardMat Disk Anchors. At the end of the two-year maintenance period, all
metal plates should be removed control
Plant Replacement
x See Hydrotech’s extensive vegetation warranty for plant performance standards
x Replace plants as necessary. Any warranty claims must be validated by a Hydrotech representative before
replacement plants can be ordered
OPTIONAL TASKS
LiteTop Growing Media Testing and Monitoring
x Test for pH, nutrient levels, salt content, etc. Contact Hydrotech for approved soil testing facilities.
x After analysis, Hydrotech can assist in determining any needed solutions.
Fertilizer Application
x Do not apply fertilizer without the consent of Hydrotech and the Property Owner.
x Hydrotech can make recommendations for appropriate products.
Pesticide Application
x Do not apply pesticide without the consent of Hydrotech and the Property Owner.
x Hydrotech can make recommendations for appropriate products and procedures.
Herbicide Application
x Do not apply herbicide without the consent of Hydrotech and the Property Owner.
x Be careful not to impact the desirable plant material.
x Hydrotech can make recommendations for appropriate products and procedures.
American Hydrotech, Inc. - Contractor Training Manual - © 2012 Page 29
MAINTENANCE SCHEDULE
Please note the
schedule of tasks
listed may vary based
on the region in which
the project is located
and the time of year
the project was
installed.
If the growing season
ends before the First
Quarter tasks have
been performed in
their entirety, the
contractor must start
at that point after last
frost in the spring.
Some tasks may not
need to be performed
at every scheduled
visit.
Please contact
Hydrotech with any
specific questions.
Page 30 American Hydrotech, Inc. - Contractor Training Manual - © 2012
VISITATION CHECKLIST
PROJECT NAME:
Location: Date of Visit:
Installation Contractor: Date of Installation:
Maintenance Contractor: Maint. Contract in place:
Yes
No
Water Sources at roof: Volume (GPM) Pressure (PSI) Length of Contract:
An in-place and active maintenance contract is required for the warranty to be in effect.
Original Plant Material (check all that apply):
Plugs
Cuttings
Sedum Carpet
Sedum Tile
Garden Tray
Other:_____________
Scheduled Visit (check one):(Note:A visitation checklist is NOT required with every visit but should be submitted at the frequency outlined below. Consult the
maintenance schedule on the previous page for a recommended visit schedule. Dependent on the date of installation and regional
and climatic conditions, the frequency of maintenance may vary. Contact Hydrotech for details.
1st Quarter by Week: 1 2 3 4 5 6 7 8 9 10 11 12
First Year by Month: 1 2 3 4 5 6 7 8 9 10 11 12
see 1st Quarter above
Second Year by Quarter: 1 2 3 4
Photos submitted digitally?
Yes
No (See next page for instructions on submitting photos)
Primary Tasks Comments:Check all that apply
Watering
Irrigation Inspection
Drainage Inspection
Hand Weeding
Secondary Tasks Comments:Check all that apply
General Plant Inspection
LiteTop Replacement
Debris / Trash Removal
Plant Replacement
Optional Tasks Comments:
(list any tasks performed)
Additional comments
Estimated Plant Coverage at time of this visit: _______% Copy submitted to Property Owner?
Yes
No
I hereby certify that the above tasks have been performed in accordance with the
American Hydrotech, Inc. Garden Roof Maintenance Plan.
Print Name: Title:
Maintenance Contractor Representative
Signature: Date:
Please return to: American Hydrotech, Inc. Phone: (312) 337-4998 Email: GardenRoof@hydrotechusa.com
303 E. Ohio Street, Suite 2700 Fax: (312) 661-0731
Chicago, IL 60611
American Hydrotech, Inc. - Contractor Training Manual - © 2012 Page 31
INSTRUCTION FOR SUBMITTING PHOTOS
x Installation and Maintenance Visitation Photos:
o Provide a sufficient number (10-20) of high-resolution digital
photographs during maintenance visits to Hydrotech. When in doubt,
take a picture to help fully document the installation and the condition
of the roof during the maintenance visits.
o Take photos of all parts of the Garden Roof installation including
perimeters, vegetation free zones, inspection chambers, ladder
areas, and other areas of interest.
o This documentation is valuable to the maintenance contractor. It is
proof that they are following the Hydrotech warranty requirements.
x File Preparation:
o High resolution files should be greater that 250Kb in size. Low-
resolution files (e.g. photos taken from cell phones) are often blurry
and do not capture enough fine detail. Photos of cuttings that are
rooting as well as plugs, sedum tile and carpet should be made using
close-up or macro camera settings.
o Please include project name and date in the file name. For example:
Project Name – 12-21-2011- photo 1
Project Name – 12-21-2011- photo 2
Project Name – 12-21-2011- photo 3
x Uploading
o Combining single photos into ZIP files will save time during the
uploading and downloading process. There are a number of ZIP file
utilities available on the Internet.
o To easily transmit your photos, log onto a file sharing website such as
www.yousendit.com. This particular website has a free trial service to
upload large batches of photos and other documents. This eliminates
clogging up your e-mail server and Hydrotech’s server.
o Use this e-mail address:gardenroof@hydrotechusa.com and
reference the project name and Hydrotech contact in the e-mail.
o This website will send an e-mail recipient that the photos are available
for downloading. This website has the ability to notify multiple people
that the photos are available. The e-mails contain a link that directs
Hydrotech staff to a location where the photos can be downloaded.
o If you need assistance, please contact Hydrotech at 312.337.4998.
Clear, close-up photos are important in determining the
growth activity of the Garden Roof, especially for cuttings.
Take as many photos as needed to adequately
document the Garden Roof installation and current
conditions during maintenance visits. Most
projects will require multiple photos to sufficiently