HomeMy WebLinkAbout34_Drainage-ReportKING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 1/9/2009
1
Part 1 PROJECT OWNER AND
PROJECT ENGINEER Part 2 PROJECT LOCATION AND
DESCRIPTION
Project Owner ________________________
Phone ______________________________
Address ____________________________
____________________________________
Project Engineer ______________________
Company ___________________________
Phone ______________________________
Project Name _________________________
DDES Permit # ________________________
Location Township ______________
Range ________________
Section ________________
Site Address __________________________
_____________________________________
Part 3 TYPE OF PERMIT APPLICATION Part 4 OTHER REVIEWS AND PERMITS
Landuse Services
Subdivison / Short Subd. / UPD
Building Services
M/F / Commerical / SFR
Clearing and Grading
Right-of-Way Use
Other _______________________
DFW HPA
COE 404
DOE Dam Safety
FEMA Floodplain
COE Wetlands
Other ________
Shoreline
Management
Structural
Rockery/Vault/_____
ESA Section 7
Part 5 PLAN AND REPORT INFORMATION
Technical Information Report Site Improvement Plan (Engr. Plans)
Type of Drainage Review
(circle):
Date (include revision
dates):
Date of Final:
Full / Targeted /
Large Site
___________________
___________________
___________________
Type (circle one):
Date (include revision
dates):
Date of Final:
Full / Modified /
Small Site
__________________
__________________
__________________
Part 6 ADJUSTMENT APPROVALS
Type (circle one): Standard / Complex / Preapplication / Experimental / Blanket
Description: (include conditions in TIR Section 2)
____________________________________________________________________________________
____________________________________________________________________________________
____________________________________________________________________________________
Date of Approval: ______________________
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 1/9/2009
2
Part 7 MONITORING REQUIREMENTS
Monitoring Required: Yes / No
Start Date: _______________________
Completion Date: _______________________
Describe: _________________________________
_________________________________________
_________________________________________
_________________________________________
_________________________________________
Part 8 SITE COMMUNITY AND DRAINAGE BASIN
Community Plan : _________________________________
Special District Overlays: __________________________________________________________
Drainage Basin: ___________________________________
Stormwater Requirements: ________________________________________________________
Part 9 ONSITE AND ADJACENT SENSITIVE AREAS
River/Stream _______________________
Lake _____________________________
Wetlands ___________________________
Closed Depression ___________________
Floodplain __________________________
Other ______________________________
___________________________________
Steep Slope ______________________
Erosion Hazard ___________________
Landslide Hazard __________________
Coal Mine Hazard __________________
Seismic Hazard ___________________
Habitat Protection __________________
_________________________________
Part 10 SOILS
Soil Type
_________________
_________________
_________________
_________________
Slopes
_________________
_________________
_________________
_________________
Erosion Potential
_________________
_________________
_________________
_________________
High Groundwater Table (within 5 feet)
Other ________________________
Sole Source Aquifer
Seeps/Springs
Additional Sheets Attached
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 1/9/2009
3
Part 11 DRAINAGE DESIGN LIMITATIONS
REFERENCE
Core 2 – Offsite Analysis_________________
Sensitive/Critical Areas___________________
SEPA________________________________
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
(incl. facility summary sheet)
Level: 1 / 2 / 3 or Exemption Number ____________
Small Site BMPs ___________________________________
Conveyance System
Spill containment located at: _________________________
Erosion and Sediment Control
ESC Site Supervisor:
Contact Phone:
After Hours Phone:
Maintenance and Operation
Responsibility: Private / Public
If Private, Maintenance Log Required: Yes / No
Financial Guarantees and
Liability
Provided: Yes / No
Water Quality
(include facility summary sheet)
Type: Basic / Sens. Lake / Enhanced Basicm / Bog
or Exemption No. ______________________
Landscape Management Plan: Yes / No
Special Requirements (as applicable)
Area Specific Drainage
Requirements
Type: CDA / SDO / MDP / BP / LMP / Shared Fac. / None
Name: ________________________
Floodplain/Floodway Delineation Type: Major / Minor / Exemption / None
100-year Base Flood Elevation (or range): ______________
Datum:
Flood Protection Facilities
Describe:
Source Control
(comm./industrial landuse)
Describe landuse:
Describe any structural controls:
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 1/9/2009
4
Oil Control
High-use Site: Yes / No
Treatment BMP: ________________________________
Maintenance Agreement: Yes / No
with whom? ____________________________________
Other Drainage Structures
Describe:
Part 13 EROSION AND SEDIMENT CONTROL REQUIREMENTS
MINIMUM ESC REQUIREMENTS
DURING CONSTRUCTION
Clearing Limits
Cover Measures
Perimeter Protection
Traffic Area Stabilization
Sediment Retention
Surface Water Collection
Dewatering Control
Dust Control
Flow Control
MINIMUM ESC REQUIREMENTS
AFTER CONSTRUCTION
Stabilize Exposed Surfaces
Remove and Restore Temporary ESC Facilities
Clean and Remove All Silt and Debris, Ensure
Operation of Permanent Facilities
Flag Limits of SAO and open space
preservation areas
Other ______________________
Part 14 STORMWATER FACILITY DESCRIPTIONS (Note: Include Facility Summary and Sketch)
Flow Control Type/Description Water Quality Type/Description
Detention
Infiltration
Regional Facility
Shared Facility
Flow Control
BMPs
Other
________________
________________
________________
________________
________________
________________
Biofiltration
Wetpool
Media Filtration
Oil Control
Spill Control
Flow Control BMPs
Other
________________
________________
________________
________________
________________
________________
________________
KING COUNTY, WASHINGTON, SURFACE WATER DESIGN MANUAL
TECHNICAL INFORMATION REPORT (TIR) WORKSHEET
2009 Surface Water Design Manual 1/9/2009
5
Part 15 EASEMENTS/TRACTS Part 16 STRUCTURAL ANALYSIS
Drainage Easement
Covenant
Native Growth Protection Covenant
Tract
Other
Cast in Place Vault
Retaining Wall
Rockery > 4’ High
Structural on Steep Slope
Other
Part 17 SIGNATURE OF PROFESSIONAL ENGINEER
I, or a civil engineer under my supervision, have visited the site. Actual site conditions as observed were
incorporated into this worksheet and the attached Technical Information Report. To the best of my
knowledge the information provided here is accurate.
Signed/Date
i
Contents
SECTION 1: Project Overview .......................................................................................................... 1
SECTION 2: Core and Special Requirements Summary .................................................................. 3
SECTION 3: Offsite Analysis ............................................................................................................. 4
SECTION 4: Flow Control and water quality Facility Analysis and Design ...................................... 6
SECTION 5: Conveyance System Analysis and Design .................................................................. 10
SECTION 6: Special Reports and Studies ....................................................................................... 12
SECTION 7: Other Permits ............................................................................................................. 12
SECTION 8: CSWPP Analysis and Design ....................................................................................... 12
SECTION 9: Bond Quantities, Facility Summaries, and Declaration of Covenant ......................... 12
SECTION 10: Operations and Maintenance Manual ..................................................................... 12
FIGURES
Figure 1 – Vicinity Map
Figure 2 – Soils Map
Figure 3A & 3B – Downstream Mapping
APPENDICIES
Appendix A – KCRTS Analysis
Appendix B – Operations & Maintenance Manual
Appendix C – Geotechnical Report
Appendix D – Arborist Report
Appendix E – Wetland & Stream Reconnaissance
1
SECTION 1: Project Overview
This Technical Information Report is submitted in support of the Renton Subdivision Preliminary
Plat. The project site consists of 2 parcels; KC Parcel #’s 0087000265 and 0087000270. The
properties are rectangular in shape and are located on the east side of 106th Avenue SE (See
Figure 1 - Vicinity Map below). The property is bordered along the north, south, and east by
single family residences. The project area is approximately 1.94 acres and is presently
developed with 2 single-family residences. The existing buildings and driveways will be
removed. Project site improvements will consist of on & off-site infrastructure improvements
to support the future construction of 11 single family residential building lots and new public
road. Frontage improvements will include the installation of an 8’ wide planter strip and a 5’
wide sidewalk along 106th Avenue SE.
Figure 1 – Vicnity Map
SITE
2
Soils:
The SCS Soils map indicates the site is underlain with AgC (Alderwood) soils.
Figure 2 – Soils Map
SITE
3
SECTION 2: Core and Special Requirements Summary
To obtain preliminary approval with the City of Renton, the relevancy of the 8 core and 6 special
requirements per Section 4-6-030 of the Renton Municipal Code (RMC), KCSWDM are required to
be addressed:
1. Core Req. #1 – Discharge at natural location
A field review of the site-specific topography indicates that the developed drainage will
discharge to the natural location situated downstream to the west of the project site.
2. Core Req. #2 – Offsite Analysis
An off-site analysis has been prepared for approval by the City of Renton, See Section 3.
3. Core Req. #3 – Flow Control
Flow control will be provided for the development via a detention vault. See Section 4.
4. Core Req. #4 – Conveyance System
The proposed on-site conveyance and tightline system will route runoff to the existing
conveyance system within 106th AVE SE.
5. Core Req. #5 – Erosion & Sediment Control.
An erosion and sediment control plan, which will serve to minimize soil
erosion/sedimentation during the proposed site construction, will be prepared for approval
by the City of Renton.
6. Core Req. #6 – Maintenance and Operations
The on-site stormwater system will be maintained by the homeowners. The off-site
conveyance systems will be maintained by the City of Renton. See Appendix B.
7. Core Req. #7 – Financial Guarantees & Liability
Financial Guarantee & Liability commitments between the property developer and the City
of Renton will be established at the time of permit issuance.
8. Core Req. #8 – Water Quality
The proposed pollution generating impervious surfaces are greater than the 5,000 SF
threshold, therefore water quality treatment is required. The project proposes a combined
detention and wetvault system to meet the water quality requirement.
9. Special Req. #1 – Other Adopted Requirements
The Renton SWDM was reviewed and there are no additional requirements.
10. Special Req. #2 – Floodplain/Floodway Delineation
Per City of Renton mapping the site does not lie within a floodplain or floodway
11. Special Req. #3 – Flood Protection Facilities
Not applicable to this project.
12. Special Req. #4 – Source Control
Not applicable to this project
13. Special Req. #5 – Oil Control
This project is not considered high-use therefore oil control is not applicable to this project.
14. Special Req. #6 – Aquifer Protection Area
Not applicable to this project.
4
SECTION 3: Offsite Analysis
A field review of the downstream conditions was performed on January 27, 2015. The weather
was sunny and wet; the temperature was approximately 55 degrees. A visual reconnaissance
was performed utilizing information obtained from the City of Renton GIS Mapping. Please
refer to storm drainage mapping exhibits that follow for a depiction of the downstream
drainage conditions.
Upstream:
A detention vault constructed for the Marvin Garden Townhomes project is located east of the
Skattum properties and presently discharges to a ditch east located near the northeast property
corner. Drainage from this system will be collected and conveyed along the east and south
property lines to bypass the Skattum Plat’s detention vault. Please refer to Figure 3A for the
location of the Marvin Garden Townhomes vault.
Downstream:
The runoff is tributary to the existing ditch to the west of the site. The ditch conveys runoff to
the south for approximately 320 feet before crossing SE 172nd Street via an existing closed pipe
conveyance system for 68 feet. Runoff then appears to sheet flow down the hill to an existing
ditch along the north side of Benson Drive South before entering an existing closed pipe
conveyance system. The conveyance system directs runoff to the west for 80 feet where runoff
then enters a ditch and continues west for approximately 400 feet. Runoff is then directed to
the southwest for approximately 580 feet via a closed pipe system within South 36th Street. The
field reconnaissance was terminated as the investigation exceeded the required ¼ mile point
analysis.
Downstream Concerns & Effects of Proposed Project: Discharge from the developed site will
sheet flow across the property in a similar fashion as it presently exists. The downstream
drainage system consists of a series of catch basins, ditches, and closed pipe systems. No
adverse impacts to the downstream system are anticipated or expected.
5
Figure 3A – Downstream Mapping (City of Renton GIS)
Figure 3B – Downstream Mapping (City of Renton GIS)
Marvin Gardens
Townhomes vault SITE Match Line Match Line
6
SECTION 4: Flow Control and water quality Facility Analysis and Design
A formal flow control facility is required for the project site based on Section 1.2.3 of the City of
Renton Surface Water Design Manual (SWDM). According to the Flow Control Application Map in
the City of Renton SWDM the project site is located within the Flow Control Duration Standard
(Forested Conditions). This flow control standard is equivalent to the Conservation Flow Control
Area in the King County SWDM which utilizes historic site conditions for the predeveloped flow
rates. A combined detention and wetvault is proposed to meet the Flow Control and Water Quality
Requirements. Flow control BMPS will be analyzed and sized in the preparation of the Engineering
Drawings.
A hydrologic analysis of the site was completed in order to size the required on site detention and
water quality treatment necessary to account for the increase in the peak storm water release rate
for the developed site. The site was analyzed for the pre-developed and developed conditions
under the King County Continuous Runoff Time Series (KCRTS) hydrograph model using the KCRTS
software developed and provided by the King County Surface Water Management Division. Below
are the historic and developed KCRTS flow rates output. Please refer to Appendix A for the
complete KCRTS analysis.
Due to topographic constraints a portion of the project area cannot be intercepted therefore an
area swap is proposed.
The area swap is summarized below (see Developed Conditions Map):
Impervious Area Swap Summary (See map below)
Project Swap Area = 1,673 SF
Off-Site Trade Area = 1,600 SF
Historic Site Conditions:
7
Flow Frequency Analysis
Time Series File:skattum2ex.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.132 2 2/09/01 18:00 0.170 1 100.00 0.990
0.036 7 1/06/02 3:00 0.132 2 25.00 0.960
0.098 4 2/28/03 3:00 0.102 3 10.00 0.900
0.004 8 3/24/04 20:00 0.098 4 5.00 0.800
0.058 6 1/05/05 8:00 0.086 5 3.00 0.667
0.102 3 1/18/06 21:00 0.058 6 2.00 0.500
0.086 5 11/24/06 4:00 0.036 7 1.30 0.231
0.170 1 1/09/08 9:00 0.004 8 1.10 0.091
Computed Peaks 0.157 50.00 0.980
Developed Conditions (without flow control):
Flow Frequency Analysis
Time Series File:skattum2de.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.393 6 2/09/01 2:00 0.794 1 100.00 0.990
0.321 8 1/05/02 16:00 0.506 2 25.00 0.960
0.472 3 2/27/03 7:00 0.472 3 10.00 0.900
0.348 7 8/26/04 2:00 0.419 4 5.00 0.800
0.419 4 10/28/04 16:00 0.417 5 3.00 0.667
0.417 5 1/18/06 16:00 0.393 6 2.00 0.500
0.506 2 10/26/06 0:00 0.348 7 1.30 0.231
0.794 1 1/09/08 6:00 0.321 8 1.10 0.091
Computed Peaks 0.698 50.00 0.980
8
Outlet Riser:
The outlet riser for the combined facility was sized per Section 5.3.4.2 of the KCSWDM. A 12-
inch diameter riser, with 0.50 feet of head, can convey 2.67 CFS. The 100-Year developed peak
flows for the drainage basin tributary to the detention vault is 0.740 CFS.
QORIFICE = C x A x (2 x g x H)1/2
where:
D = diameter (ft) – 1.0’
H = head (ft) – 0.50'
Existing Conditions Map
9
Developed Conditions Map
10
Water Quality:
The proposed pollution generating impervious surfaces are greater than the 5,000 SF threshold,
therefore water quality treatment is required for this project. The area-specific water quality
treatment was determined to be Basic. The project proposes a combined detention and
wetvault system to meet the water quality requirement.
The storm water facility incorporates and provides a two-cell basic wet vault (i.e. VB/VR = 3.0)
into the design of the storm water control and treatment facility by providing additional storage
volume below the detention vault volume.
The wet vault was designed as detailed in the 2009 KCSWDM utilizing the following equation:
Vb = fVr = f (0.90Ai + 0.25At) x (R/12)}
where; Vb = wetpool volume (cu. ft.)
f = volume factor = 3.0
Vr = volume of runoff from the mean annual storm (cu. ft.)
Ai = area of impervious surface (sf)
At = area of till soil covered with grass or forest (sf)
R/12 = rainfall from mean annual storm (feet) = 0.47/12
Impervious Areas (Ai) = 58,370 sf
Pervious Areas (Ao) = 33,106 sf
Vb = 3.0Vr = 3.0(0.90 x Ai + 0.25 x At ) x (0.47/12)
= 7,145 c.f. (required volume)
The proposed vault provides 28,000 CF of live storage and 7,200 CF of dead storage.
SECTION 5: Conveyance System Analysis and Design
The on-site drainage conveyance system is planned to be constructed of a series of catch basins
interconnected with 12” PVC pipe.
The conveyance calculations were performed using Manning’s Equation. The conveyance
system was checked to ensure that during the 100-year storm event, the system would function
adequately. The 100-year peak flow using KCRTS 15-minute time steps from the developed site
was compared to the maximum capacity of the pipe. Using the Manning’s Equation, the
maximum capacity of a 12” pipe sloped at 0.50% is 2.98 cfs, which is greater than the actual
100-year flow of 1.83 cfs (see output below). Since all pipes within the proposed conveyance
system are sloped at grades equal to or steeper than 0.50%, the system will have adequate
capacity to convey the generated runoff.
11
Flow Frequency Analysis
Time Series File:skatt2conv.tsf
Project Location:Sea-Tac
---Annual Peak Flow Rates--- -----Flow Frequency Analysis-------
Flow Rate Rank Time of Peak - - Peaks - - Rank Return Prob
(CFS) (CFS) Period
0.601 6 8/27/01 18:00 1.83 1 100.00 0.990
0.425 8 1/05/02 15:00 1.29 2 25.00 0.960
1.29 2 12/08/02 17:15 0.837 3 10.00 0.900
0.484 7 8/23/04 14:30 0.727 4 5.00 0.800
0.727 4 11/17/04 5:00 0.716 5 3.00 0.667
0.716 5 10/27/05 10:45 0.601 6 2.00 0.500
0.837 3 10/25/06 22:45 0.484 7 1.30 0.231
1.83 1 1/09/08 6:30 0.425 8 1.10 0.091
Computed Peaks 1.65 50.00 0.980
12
SECTION 6: Special Reports and Studies
Geotechnical Engineering Study; Earth Solutions NW; December 20, 2016
Arborist Report; American Forest Management; December 13, 2016
Wetland & Stream Reconnaissance; Altmann Oliver Associates; May 21, 2016
SECTION 7: Other Permits
Single-Family Residential Building Permits and a Right-of-Way Use Permit from the City of
Renton will be required. Utility permits to construct the water and sewer system will be
required from Soos Creek Water and Sewer Distict.
SECTION 8: CSWPP Analysis and Design
Several standard Best Management Practices (BMPs) will be utilized by the contractor to
minimize the amount of erosion and sedimentation that may be perpetuated by the
construction site. Some of the measures might include filter fence, catch basin protection, and
standard ground cover practices. A general stormwater permit will be required from the
Washington Department of Ecology and will be obtained prior to construction.
SECTION 9: Bond Quantities, Facility Summaries, and Declaration of Covenant
These documents will be provided at the time of Single-Family Building Permit application.
SECTION 10: Operations and Maintenance Manual
A draft Operations & Maintenance Manual is provided in Appendix B.
APPENDIX A
KCRTS HYDROLOGIC ANALYSES
Retention/Detention Facility
Type of Facility: Detention Vault
Facility Length: 80.00 ft
Facility Width: 50.00 ft
Facility Area: 4000. sq. ft
Effective Storage Depth: 7.00 ft
Stage 0 Elevation: 0.00 ft
Storage Volume: 28000. cu. ft
Riser Head: 7.00 ft
Riser Diameter: 12.00 inches
Number of orifices: 3
Full Head Pipe
Orifice # Height Diameter Discharge Diameter
(ft) (in) (CFS) (in)
1 0.00 0.69 0.034
2 4.70 1.25 0.064 4.0
3 6.00 1.00 0.027 4.0
Top Notch Weir: None
Outflow Rating Curve: None
Stage Elevation Storage Discharge Percolation
(ft) (ft) (cu. ft) (ac-ft) (cfs) (cfs)
0.00 0.00 0. 0.000 0.000 0.00
0.01 0.01 40. 0.001 0.002 0.00
0.02 0.02 80. 0.002 0.002 0.00
0.03 0.03 120. 0.003 0.002 0.00
0.04 0.04 160. 0.004 0.003 0.00
0.05 0.05 200. 0.005 0.003 0.00
0.06 0.06 240. 0.006 0.003 0.00
0.20 0.20 800. 0.018 0.006 0.00
0.34 0.34 1360. 0.031 0.007 0.00
0.48 0.48 1920. 0.044 0.009 0.00
0.61 0.61 2440. 0.056 0.010 0.00
0.75 0.75 3000. 0.069 0.011 0.00
0.89 0.89 3560. 0.082 0.012 0.00
1.03 1.03 4120. 0.095 0.013 0.00
1.16 1.16 4640. 0.107 0.014 0.00
1.30 1.30 5200. 0.119 0.015 0.00
1.44 1.44 5760. 0.132 0.015 0.00
1.57 1.57 6280. 0.144 0.016 0.00
1.71 1.71 6840. 0.157 0.017 0.00
1.85 1.85 7400. 0.170 0.017 0.00
1.99 1.99 7960. 0.183 0.018 0.00
2.12 2.12 8480. 0.195 0.019 0.00
2.26 2.26 9040. 0.208 0.019 0.00
2.40 2.40 9600. 0.220 0.020 0.00
2.54 2.54 10160. 0.233 0.020 0.00
2.67 2.67 10680. 0.245 0.021 0.00
2.81 2.81 11240. 0.258 0.021 0.00
2.95 2.95 11800. 0.271 0.022 0.00
3.08 3.08 12320. 0.283 0.023 0.00
3.22 3.22 12880. 0.296 0.023 0.00
3.36 3.36 13440. 0.309 0.023 0.00
3.50 3.50 14000. 0.321 0.024 0.00
3.63 3.63 14520. 0.333 0.024 0.00
3.77 3.77 15080. 0.346 0.025 0.00
3.91 3.91 15640. 0.359 0.025 0.00
4.04 4.04 16160. 0.371 0.026 0.00
4.18 4.18 16720. 0.384 0.026 0.00
4.32 4.32 17280. 0.397 0.027 0.00
4.46 4.46 17840. 0.410 0.027 0.00
4.59 4.59 18360. 0.421 0.027 0.00
4.70 4.70 18800. 0.432 0.028 0.00
4.71 4.71 18840. 0.433 0.028 0.00
4.73 4.73 18920. 0.434 0.029 0.00
4.74 4.74 18960. 0.435 0.031 0.00
4.75 4.75 19000. 0.436 0.033 0.00
4.77 4.77 19080. 0.438 0.036 0.00
4.78 4.78 19120. 0.439 0.040 0.00
4.79 4.79 19160. 0.440 0.041 0.00
4.80 4.80 19200. 0.441 0.042 0.00
4.94 4.94 19760. 0.454 0.049 0.00
5.08 5.08 20320. 0.466 0.055 0.00
5.22 5.22 20880. 0.479 0.060 0.00
5.35 5.35 21400. 0.491 0.064 0.00
5.49 5.49 21960. 0.504 0.068 0.00
5.63 5.63 22520. 0.517 0.071 0.00
5.76 5.76 23040. 0.529 0.075 0.00
5.90 5.90 23600. 0.542 0.078 0.00
6.00 6.00 24000. 0.551 0.080 0.00
6.01 6.01 24040. 0.552 0.080 0.00
6.02 6.02 24080. 0.553 0.081 0.00
6.03 6.03 24120. 0.554 0.082 0.00
6.04 6.04 24160. 0.555 0.084 0.00
6.05 6.05 24200. 0.556 0.086 0.00
6.06 6.06 24240. 0.556 0.088 0.00
6.07 6.07 24280. 0.557 0.089 0.00
6.08 6.08 24320. 0.558 0.089 0.00
6.09 6.09 24360. 0.559 0.090 0.00
6.23 6.23 24920. 0.572 0.097 0.00
6.37 6.37 25480. 0.585 0.104 0.00
6.51 6.51 26040. 0.598 0.109 0.00
6.64 6.64 26560. 0.610 0.114 0.00
6.78 6.78 27120. 0.623 0.118 0.00
6.92 6.92 27680. 0.635 0.123 0.00
7.00 7.00 28000. 0.643 0.125 0.00
7.10 7.10 28400. 0.652 0.436 0.00
7.20 7.20 28800. 0.661 1.000 0.00
7.30 7.30 29200. 0.670 1.730 0.00
7.40 7.40 29600. 0.680 2.530 0.00
7.50 7.50 30000. 0.689 2.810 0.00
7.60 7.60 30400. 0.698 3.070 0.00
7.70 7.70 30800. 0.707 3.310 0.00
7.80 7.80 31200. 0.716 3.530 0.00
7.90 7.90 31600. 0.725 3.740 0.00
8.00 8.00 32000. 0.735 3.930 0.00
8.10 8.10 32400. 0.744 4.120 0.00
8.20 8.20 32800. 0.753 4.300 0.00
8.30 8.30 33200. 0.762 4.470 0.00
8.40 8.40 33600. 0.771 4.640 0.00
8.50 8.50 34000. 0.781 4.790 0.00
8.60 8.60 34400. 0.790 4.950 0.00
8.70 8.70 34800. 0.799 5.100 0.00
8.80 8.80 35200. 0.808 5.240 0.00
Hyd Inflow Outflow Peak Storage
Target Calc Stage Elev (Cu-Ft) (Ac-Ft)
1 0.79 0.17 0.42 7.09 7.09 28378. 0.651
2 0.39 ******* 0.12 6.73 6.73 26936. 0.618
3 0.47 ******* 0.10 6.29 6.29 25159. 0.578
4 0.40 ******* 0.08 5.91 5.91 23636. 0.543
5 0.42 ******* 0.04 4.80 4.80 19184. 0.440
6 0.25 ******* 0.03 4.32 4.32 17275. 0.397
7 0.32 ******* 0.03 4.16 4.16 16645. 0.382
8 0.35 ******* 0.02 2.64 2.64 10548. 0.242
----------------------------------
Route Time Series through Facility
Inflow Time Series File:skattum2de.tsf
Outflow Time Series File:rdout
Inflow/Outflow Analysis
Peak Inflow Discharge: 0.794 CFS at 6:00 on Jan 9 in Year 8
Peak Outflow Discharge: 0.419 CFS at 10:00 on Jan 9 in Year 8
Peak Reservoir Stage: 7.09 Ft
Peak Reservoir Elev: 7.09 Ft
Peak Reservoir Storage: 28378. Cu-Ft
: 0.651 Ac-Ft
Flow Duration from Time Series File:rdout.tsf
Cutoff Count Frequency CDF Exceedence_Probability
CFS % % %
0.002 27075 44.154 44.154 55.846 0.558E+00
0.005 8578 13.989 58.143 41.857 0.419E+00
0.009 6853 11.176 69.318 30.682 0.307E+00
0.012 6421 10.471 79.790 20.210 0.202E+00
0.016 4863 7.931 87.720 12.280 0.123E+00
0.019 3217 5.246 92.966 7.034 0.703E-01
0.023 1722 2.808 95.775 4.225 0.423E-01
0.026 1789 2.917 98.692 1.308 0.131E-01
0.030 462 0.753 99.446 0.554 0.554E-02
0.033 13 0.021 99.467 0.533 0.533E-02
0.037 20 0.033 99.499 0.501 0.501E-02
0.040 5 0.008 99.507 0.492 0.492E-02
0.044 37 0.060 99.568 0.432 0.432E-02
0.047 35 0.057 99.625 0.375 0.375E-02
0.050 34 0.055 99.680 0.320 0.320E-02
0.054 28 0.046 99.726 0.274 0.274E-02
0.057 26 0.042 99.768 0.232 0.232E-02
0.061 16 0.026 99.795 0.205 0.205E-02
0.064 11 0.018 99.812 0.188 0.188E-02
0.068 12 0.020 99.832 0.168 0.168E-02
0.071 15 0.024 99.856 0.144 0.144E-02
0.075 18 0.029 99.886 0.114 0.114E-02
0.078 18 0.029 99.915 0.085 0.848E-03
0.082 6 0.010 99.925 0.075 0.750E-03
0.085 1 0.002 99.927 0.073 0.734E-03
0.089 2 0.003 99.930 0.070 0.701E-03
0.092 7 0.011 99.941 0.059 0.587E-03
0.096 5 0.008 99.949 0.051 0.506E-03
0.099 7 0.011 99.961 0.039 0.391E-03
0.103 6 0.010 99.971 0.029 0.294E-03
0.106 2 0.003 99.974 0.026 0.261E-03
0.109 2 0.003 99.977 0.023 0.228E-03
0.113 3 0.005 99.982 0.018 0.179E-03
0.116 3 0.005 99.987 0.013 0.130E-03
0.120 3 0.005 99.992 0.008 0.815E-04
0.123 3 0.005 99.997 0.003 0.326E-04
Duration Comparison Anaylsis
Base File: skattum2ex.tsf
New File: rdout.tsf
Cutoff Units: Discharge in CFS
-----Fraction of Time----- ---------Check of Tolerance-------
Cutoff Base New %Change Probability Base New %Change
0.029 | 0.95E-02 0.57E-02 -40.5 | 0.95E-02 0.029 0.027 -6.5
0.037 | 0.63E-02 0.50E-02 -20.5 | 0.63E-02 0.037 0.028 -24.3
0.045 | 0.50E-02 0.41E-02 -18.0 | 0.50E-02 0.045 0.039 -13.9
0.053 | 0.37E-02 0.29E-02 -21.8 | 0.37E-02 0.053 0.047 -10.7
0.061 | 0.29E-02 0.21E-02 -28.4 | 0.29E-02 0.061 0.053 -12.5
0.069 | 0.22E-02 0.16E-02 -26.5 | 0.22E-02 0.069 0.059 -14.6
0.077 | 0.15E-02 0.10E-02 -30.4 | 0.15E-02 0.077 0.070 -8.6
0.085 | 0.10E-02 0.73E-03 -27.4 | 0.10E-02 0.085 0.077 -9.2
0.093 | 0.62E-03 0.57E-03 -7.9 | 0.62E-03 0.093 0.092 -0.8
0.100 | 0.34E-03 0.31E-03 -9.5 | 0.34E-03 0.100 0.099 -1.0
0.108 | 0.21E-03 0.23E-03 7.7 | 0.21E-03 0.108 0.112 3.2
0.116 | 0.16E-03 0.13E-03 -20.0 | 0.16E-03 0.116 0.115 -0.9
0.124 | 0.98E-04 0.00E+00 -100.0 | 0.98E-04 0.124 0.120 -3.8
0.132 | 0.16E-04 0.00E+00 -100.0 | 0.16E-04 0.132 0.124 -6.2
Maximum positive excursion = 0.004 cfs ( 3.4%)
occurring at 0.108 cfs on the Base Data:skattum2ex.tsf
and at 0.112 cfs on the New Data:rdout.tsf
Maximum negative excursion = 0.012 cfs (-29.1%)
occurring at 0.040 cfs on the Base Data:skattum2ex.tsf
and at 0.029 cfs on the New Data:rdout.tsf
APPENDIX B
MAINTENANCE and OPERATIONS MANUAL
APPENDIX C
GEOTECHNICAL REPORT
EarthSolutionsNWLLC
EarthSolutionsNWLLC
Geotechnical Engineering
Geology
Environmental Scientists
Construction Monitoring
1805 -136th Place N.E.,Suite 201 Bellevue,WA 98005
(425)449-4704 Fax (425)449-4711
www.earthsolutionsnw.com
GEOTECHNICAL ENGINEERING STUDY
PROPOSED
RESIDENTIAL SHORT PLAT
17018 &17022 -106th AVENUE
SOUTHEAST
RENTON,WASHINGTON
ES-4948
Drwn.
Checked Date
Date Proj.No.
Plate
Earth Solutions NWLLC
Geotechnical Engineering,Construction Monitoring
EarthSolutionsNWLLC
EarthSolutionsNWLLC and Environmental Sciences
Vicinity Map
Skattum Short Plat
Renton,Washington
MRS
BJP
12/19/2016
Dec.2016
4948
1
NOTE:This plate may contain areas of color.ESNW cannot be
responsible for any subsequent misinterpretation of the information
resulting from black &white reproductions of this plate.
Reference:
King County,Washington
Map 656
By The Thomas Guide
Rand McNally
32nd Edition
SITE
Drwn.
Checked Date
Date Proj.No.
Plate
Earth Solutions NWLLC
Geotechnical Engineering,Construction Monitoring
EarthSolutionsNWLLC
EarthSolutionsNWLLC and Environmental Sciences
Test Pit Location Plan
Skattum Short Plat
Renton,Washington
MRS
BJP
12/19/2016
Dec.2016
4948
2
NOTE:This plate may contain areas of color.ESNW cannot be
responsible for any subsequent misinterpretation of the information
resulting from black &white reproductions of this plate.
NOTE:The graphics shown on this plate are not intended for design
purposes or precise scale measurements,but only to illustrate the
approximate test locations relative to the approximate locations of
existing and /or proposed site features.The information illustrated
is largely based on data provided by the client at the time of our
study.ESNW cannot be responsible for subsequent design changes
or interpretation of the data by others.
0 30 60 12 0
Scale in Feet1"=60'
NORTHLEGEND
Approximate Location of
ESNW Test Pit,Proj.No.
ES-4948,Dec.2016
Subject Site
Existing Building
Proposed Building
TP-1
Storm Drainage
TP-1
TP-2
TP-3
TP-4TP-5
106TH AVENUE S.E.390
400
390
400
Drwn.
Checked Date
Date Proj.No.
Plate
Earth Solutions NWLLC
Geotechnical Engineering,Construction MonitoringandEnvironmentalSciences
EarthSolutionsNWLLC
EarthSolutionsNWLLC
RETAINING WALL DRAINAGE DETAIL
Skattum Short Plat
Renton,Washington
MRS
BJP
12/19/2016
Dec.2016
4948
3
NOTES:
Free Draining Backfill should consist
of soil having less than 5 percent fines.
Percent passing #4 should be 25 to
75 percent.
Sheet Drain may be feasible in lieu
of Free Draining Backfill,per ESNW
recommendations.
Drain Pipe should consist of perforated,
rigid PVC Pipe surrounded with 1"
Drain Rock.
LEGEND:
Free Draining Structural Backfill
1 inch Drain Rock
18"Min.
Structural
Fill
Perforated Drain Pipe
(Surround In Drain Rock)
SCHEMATIC ONLY -NOT TO SCALE
NOT A CONSTRUCTION DRAWING
Drwn.
Checked Date
Date Proj.No.
Plate
Earth Solutions NWLLC
Geotechnical Engineering,Construction Monitoring
and Environmental Sciences
EarthSolutionsNWLLC
EarthSolutionsNWLLC
FOOTING DRAIN DETAIL
Slope
Perforated Rigid Drain Pipe
(Surround with 1"Rock)
18"(Min.)
NOTES:
Do NOT tie roof downspouts
to Footing Drain.
Surface Seal to consist of
12"of less permeable,suitable
soil.Slope away from building.
LEGEND:
Surface Seal;native soil or
other low permeability material.
1"Drain Rock
SCHEMATIC ONLY -NOT TO SCALE
NOT A CONSTRUCTION DRAWING
Skattum Short Plat
Renton,Washington
MRS
BJP
12/19/2016
Dec.2016
4948
4
APPENDIX D
ARBORIST REPORT
Arborist Report
Skattum Plat
17018 & 17022 106th Ave SE
Renton, WA
December 13th, 2016
American Forest Management 12/13/2016
Table of Contents
1. Introduction .............................................................................................................. 1
2. Description ............................................................................................................... 1
3. Methodology ............................................................................................................ 1
4. Observations ........................................................................................................... 2
5. Discussion ............................................................................................................... 3
6. Tree Retention ......................................................................................................... 3
7. Tree Replacement .................................................................................................. .3
8. Tree Protection Measures…………………………………………………………………4
Appendix
Site/Tree Photos – pages 7 - 12
Tree Summary Table – attached
Tree Locator Map - attached
Tree Plan Map – attached
City of Renton Tree Protection Measures – page 6
Skattum Plat - Arborist Report
Page 1 American Forest Management 12/13/2016
1. Introduction
American Forest Management, Inc. was contacted by Keith Litchfield of Litchfield Engineering and was asked
to compile an ‘Arborist Report’ for two parcels located within the City of Renton.
The proposed subdivision encompasses the properties at 17018 & 17022 106th Ave SE. Our assignment is to
prepare a written report on present tree conditions, which is to be filed with the preliminary permit application.
This report encompasses all of the criteria set forth under City of Renton code section 4-4-130. The tree
retention requirement is 30% of significant trees.
Date of Field Examination: December 6th, 2016
2. Description
70 significant trees were identified and assessed on the property. According to City of Renton code, a
significant tree is a tree with a caliper (trunk diameter measured 4-1/2’ above the ground) of at least 6” or an
alder or cottonwood tree with a caliper of at least 8”. Trees planted within the most recent 10 years qualify as
significant trees, regardless of the actual caliper.
A numbered aluminum tag was placed on the lower trunks of the subject trees. These numbers were used for
this assessment. Tree tag numbers correspond with the numbers on the Tree Summary Tables and copy of the
attached site survey.
There are eight neighboring trees with a drip lines that extend over the property line.
3. Methodology
Each tree in this report was visited. Tree diameters were measured by tape. The tree heights were measured
using a Spiegel Relaskop. Each tree was visually examined for defects and vigor. The tree assessment
procedure involves the examination of many factors:
The crown of the tree is examined for current vigor. This is comprised of inspecting the crown
(foliage, buds and branches) for color, density, form, and annual shoot growth, limb dieback and
disease. The percentage of live crown is estimated for coniferous species only and scored
appropriately.
The bole or main stem of the tree is inspected for decay, which includes cavities, wounds, fruiting
bodies of decay (conks or mushrooms), seams, insects, bleeding, callus development, broken or dead
tops, structural defects and unnatural leans. Structural defects include crooks, forks with V-shaped
crotches, multiple attachments, and excessive sweep.
The root collar and roots are inspected for the presence of decay, insects and/or damage, as well as if
they have been injured, undermined or exposed, or original grade has been altered.
Based on these factors a determination of condition is made. The four condition categories are described below
based on the species traits assessed:
Excellent – free of structural defects, no disease or pest problems, no root issues, excellent structure/form with
uniform crown or canopy, foliage of normal color and density, above average vigor, it will be wind firm if
isolated, suitable for its location
Good – free of significant structural defects, no disease concerns, minor pest issues, no significant root issues,
good structure/form with uniform crown or canopy, foliage of normal color and density, average or normal
vigor, will be wind firm if isolated or left as part of a grouping or grove of trees, suitable for its location
Skattum Plat - Arborist Report
Page 2 American Forest Management 12/13/2016
Fair – minor structural defects not expected to contribute to a failure in near future, no disease concerns,
moderate pest issues, no significant root issues, asymmetric or unbalanced crown or canopy, average or normal
vigor, foliage of normal color, moderate foliage density, will be wind firm if left as part of a grouping or grove
of trees, cannot be isolated, suitable for its location
Poor – major structural defects expected to fail in near future, disease or significant pest concerns, decline due
to old age, significant root issues, asymmetric or unbalanced crown or canopy, sparse or abnormally small
foliage, poor vigor, not suitable for its location
A ‘viable’ tree is “A significant tree that a qualified professional has determined to be in good health, with a
low risk of failure due to structural defects, is wind firm if isolated or remains as part of a grove, and is a
species that is suitable for its location.” Trees considered ‘non-viable’ are trees that are in poor condition due to
disease, age related decline, have significant decay issues and/or cumulative structural defects, which
exacerbate failure potential.
The attached tree map indicates the ‘condition’ of the subject trees found at the site.
4. Observations
The subject trees are primarily native, mature conifers. Specific tree information for individual trees can be
found on the attached tree table.
The Douglas-fir trees on the property are generally healthy and mature, estimated at 60 – 70 years of age. Most
were planted in rows or clusters. The row of Douglas-fir trees on the west property line, #150 - #156, are
growing very closely together and should not be isolated. One incident of fungal disease was observed. A
Phaeolus schweinitzii conk was found 1’ from the trunk of tree #132. The vigor of tree #132 is good and the
infection is suspected to be incipient. Foliage color is good. All of the Douglas-fir trees on the site are viable.
The western red cedar trees on the property are generally mature. Most of the western red cedar trees on the
property are in groupings. Decay was observed in multiple trees. The decay is suspected to be brown cubical
rot, but no fungal fruiting bodies were found. Some of the western red cedar trees were topped in the past. Co-
dominant trunks with included bark were commonly observed and are the most concerning defect. The western
red cedar trees on the property range in condition and all but one are viable.
Tree #165 - #167 are black cottonwood trees on the west side of the property. Tree #165 and #166 are mature
black cottonwoods growing closely together. Tree #165 has a DBH of 54” and a height of 167’. Tree #166 has a
DBH of 45” and a height of 154’. Large limbs on both tree have failed but no other concerning defects were
observed. Tree #167 is younger. The top of this tree broke off and there is decay in the trunk. All three trees are
viable.
Tree #149 is an English oak on the west property line. This tree has a forked trunk. The attachment between the
two trunks is good. The crown is full and no other defects were observed. This tree is in good condition and is
viable.
Tree #125, #130 and #131 are European larch trees on the west side of the property. Tree #130 and #131 have
poor trunk taper. All three trees are viable.
Neighboring Trees
Tree #201 - #206 are mature big leaf maple trees north and east of the property lines. Big leaf maple trees often
have large lateral branches. Co-dominant trunks with included bark were the most common defects observed.
All six trees are in fair to good condition and are viable.
Tree #207 is a mature Douglas-fir south of the property line. This tree has no concerning defects, is in good
condition and is viable.
Skattum Plat - Arborist Report
Page 3 American Forest Management 12/13/2016
5. Discussion
The extent of drip-lines (farthest reaching branches) for the subject trees can be found on the tree summary
tables at the back of this report. These have also been delineated on a copy of the site survey for viable/healthy
trees proposed for retention. The information plotted on the attached survey plan may need to be transferred to
a final tree retention/protection plan to meet City submittal requirements. The trees that are to be removed shall
be shown “X’d” out on the final plan.
The Limits of Disturbance (LOD) measurements can also be found on the tree summary table. This is the
recommended distance of the closest impact (soil excavation) to the trunk face. These should be referenced
when determining tree retention feasibility. The LOD measurements are based on species, age, condition, drip-
line, prior improvements, proposed impacts and the anticipated cumulative impacts to the entire root zone.
Tree Protection fencing shall be located beyond the drip-line edge of retained trees, and only moved back to the
LOD when work is authorized.
Trees on the property growing closely together are recommended for retention as groupings. One example is the
row of Douglas-fir trees, #150 - #156 are growing in a row with only a few feet between each trunk. When trees
are growing closely together, they often develop small trunk taper and live crown ratios. As long as the trees are
retained as groupings and not isolated, the risk of failure is lessened.
A Phaeolus schweinitzii conk was found 1’ from the trunk of tree #132. The vigor of tree #132 is good and the
infection is suspected to be incipient. All conifers are susceptible to Phaeolus schweinitzii and it is likely
present in multiple trees on the property. Trees in advanced stages of the disease often have thin crowns and/or
branch dieback, and swollen lower trunks. No trees with advanced or significant internal decay were identified.
The western red cedar trees on the property are mature and some concerning defects were observed. Brown
cubical rot is suspected to be in multiple western red cedar trees on the property. The development of internal
decay columns within mature cedar is common. As long as trees are vigorous and actively growing, the risk of
failure remains low. Western red cedars are good at compartmentalizing decay radially and the presence of rot
is not necessarily an indication that the tree is declining. The largest concern with the western red cedar trees on
the site is co-dominant stems with included bark. Tree #115 is a western red cedar with co-dominant stems that
have split apart. Failure of this tree is extremely likely. Tree #115 is a high risk tree and should be removed
before work commences on the site.
The tree density on the site is currently low and mainly concentrated in the southwest region of the property.
Most of the trees are in the center and west side of the property. Sidewalk improvements, water utilites and the
construction of new homes will prevent retention of the majority of the existing trees. The site will fall 8% short
of meeting the required 30% significant tree retention requirement. New trees will be planted to mitigate for the
tree removal and to enhance the landscape.
There are no concerns with neighboring trees. The tree protection measures below will serve to protect these
trees.
6. Tree Retention
A total of 70 significant trees were identified on the subject property. One of the significant trees is in poor
condition. This tree was not included in the tree calculation.
Landmark trees and tree groves were prioritized when selecting trees for retention, per the City of Renton tree
code 4-4-130.
Tree Calculation based on 69, healthy, viable, significant trees
Viable Trees proposed for removal – 54 (78%)
Viable Trees proposed for retention – 15 (22%)
Skattum Plat - Arborist Report
Page 4 American Forest Management 12/13/2016
7. Tree Replacement
Replacements trees may be required. Consult your city planner for tree replacement requirements. All
replacement trees are to be planted on site. For planting and maintenance specifications, refer to Section 4-4-
130 of the Renton Tree Ordinances.
8. Tree Protection Measures
The following guidelines are recommended to ensure that the designated space set aside for the preserved trees
are protected and construction impacts are kept to a minimum. Refer to the City of Renton Code 4-4-130- 9.
Protection Measures During Construction for more information.
Tree protection barriers shall be initially erected at 5’ outside of the drip-line prior to moving any
heavy equipment on site.
Tree protection fencing shall only be moved where necessary to install improvements, but only as
close as the Limits of Disturbance, as indicated on the attached plan.
Excavation limits should be laid out in paint on the ground to avoid over excavating.
Excavations within the drip-lines shall be monitored by a qualified tree professional so necessary
precautions can be taken to decrease impacts to tree parts. A qualified tree professional shall monitor
excavations when work is required and allowed up to the “Limits of Disturbance”.
To establish sub grade for foundations, curbs and pavement sections near the trees, soil should be
removed parallel to the roots and not at 90 degree angles to avoid breaking and tearing roots that lead
back to the trunk within the drip-line. Any roots damaged during these excavations should be exposed
to sound tissue and cut cleanly with a saw. Cutting tools should be sterilized with alcohol.
Areas excavated within the drip-line of retained trees should be thoroughly irrigated weekly during dry
periods.
Preparations for final landscaping shall be accomplished by hand within the drip-lines of retained trees.
Plantings within the drip lines shall be limited. Large equipment shall be kept outside of the tree
protection zones.
Tree Type Removal Retained Total
Landmark # 11 0 11
Landmark % 100% 0% 100%
Significant # 43 15 58
Significant % 74% 26% 100%
Total # 54 15 69
Total % 78% 22% 100%
Skattum Plat - Arborist Report
Page 5 American Forest Management 12/13/2016
There is no warranty suggested for any of the trees subject to this report. Weather, latent tree conditions, and
future man-caused activities could cause physiologic changes and deteriorating tree condition. Over time,
deteriorating tree conditions may appear and there may be conditions, which are not now visible which, could
cause tree failure. This report or the verbal comments made at the site in no way warrant the structural stability
or long term condition of any tree, but represent my opinion based on the observations made.
Nearly all trees in any condition standing within reach of improvements or human use areas represent hazards
that could lead to damage or injury.
Please call if you have any questions or I can be of further assistance.
Sincerely,
Kelly Wilkinson
kelly.wilkinson@afmforest.com
ISA Certified Arborist #PN-7673A
ISA Tree Risk Assessment Qualified
Skattum Plat - Arborist Report
Page 6 American Forest Management 12/13/2016
City of Renton Code 4-4-130- 9. Protection Measures During Construction
a. Construction Storage Prohibited: The applicant may not fill, excavate, stack or store any equipment, dispose of any
materials, supplies or fluids, operate any equipment, install impervious surfaces, or compact the earth in any way within
the area defined by the drip line of any tree to be retained.
b. Fenced Protection Area Required: Prior to development activities, the applicant shall erect and maintain six-foot (6') high
chain link temporary construction fencing around the drip lines of all retained trees or at a distance surrounding the tree
equal to one and one-quarter feet (1.25') for every one inch (1") of trunk caliper, whichever is greater, or along the
perimeter of a tree protection tract. Placards shall be placed on fencing every fifty feet (50') indicating the words, “NO
TRESPASSING – Protected Trees,” or on each side of the fencing if less than fifty feet (50'). Site access to individually
protected trees or groups of trees shall be fenced and signed. Individual trees shall be fenced on four (4) sides. In
addition, the applicant shall provide supervision whenever equipment or trucks are moving near trees.
c. Protection from Grade Changes: If the grade level adjoining to a tree to be retained is to be raised, the applicant shall
construct a dry rock wall or rock well around the tree. The diameter of this wall or well must be equal to the tree’s drip line.
d. Impervious Surfaces Prohibited within the Drip Line: The applicant may not install impervious surface material within the
area defined by the drip line of any tree to be retained.
e. Restrictions on Grading within the Drip Lines of Retained Trees: The grade level around any tree to be retained may not
be lowered within the greater of the following areas: (i) the area defined by the drip line of the tree, or (ii) an area around
the tree equal to one and one-half feet (1-1/2') in diameter for each one inch (1") of tree caliper. A larger tree protection
zone based on tree size, species, soil, or other conditions may be required. (Ord. 5676, 12-3-2012)
f. Mulch Layer Required: All areas within the required fencing shall be covered completely and evenly with a minimum of
three inches (3") of bark mulch prior to installation of the protective fencing. Exceptions may be approved if the mulch will
adversely affect protected ground cover plants. (Ord. 5676, 12-3-2012)
g. Monitoring Required during Construction: The applicant shall retain a certified arborist or licensed landscape architect to
ensure trees are protected from development activities and/or to prune branches and roots, fertilize, and water as
appropriate for any trees and ground cover that are to be retained.
h. Alternative Protection: Alternative safeguards may be used if determined to provide equal or greater tree protection. (Ord.
5676, 12-3-2012)
Skattum Plat - Arborist Report
Page 7 American Forest Management 12/13/2016
Photos
Northeast corner of the subject property
Cluster of western red cedar trees (#106 - #108)
Skattum Plat - Arborist Report
Page 8 American Forest Management 12/13/2016
Tree #103 and #102 – big leaf maple and Douglas-fir trees
Tree #114 – western red cedar with a self-corrected lean and column of trunk decay
Skattum Plat - Arborist Report
Page 9 American Forest Management 12/13/2016
Tree #113 – western red cedar with column of decay
Grouping of western red cedar trees (#109 - #114)
Skattum Plat - Arborist Report
Page 10 American Forest Management 12/13/2016
Tree #115 – western red cedar with forked trunk and severe decay
West side of subject property
Skattum Plat - Arborist Report
Page 11 American Forest Management 12/13/2016
Tree #132 – Douglas-fir tree with Phaeolus schweinitzii conk
Tree #133 – European white birch with a large burl
Skattum Plat - Arborist Report
Page 12 American Forest Management 12/13/2016
East side of subject property, tree #169 in the center
Tree #167 – black cottonwood with poor form
Tree Summary Table American Forest Management, Inc.
For:Skattum Plat Date:12/7/2016
City of Renton Inspector:Wilkinson
Tree/DBH Height
Tag #Species (inches)(feet)Condition Viability Comments Proposal
N S E W
101 Douglas-fir 22 96 13 / 10 17 / 10 good viable retain
102 Douglas-fir 28 103 14 / 12 11 / 12 16 / 12 8 / 12 good viable Slight lean E retain
103 big leaf maple 29 85 12 / 12 21 / 12 19 / 12 18 / 12 good viable retain
104 Douglas-fir 12 42 9 / 6 14 / 6 17 / 6 fair viable retain
105 western red cedar 20 81 13 10 17 4 good viable remove
106 western red cedar 28 52 4 17 16 6 fair viable Topped remove
107 western red cedar 24 78 10 8 4 6 good viable remove
108 western red cedar 34 72 18 21 11 23 good viable landmark tree remove
109 western red cedar 37 45 10 17 15 10 good viable landmark tree remove
110 western red cedar 32 103 17 9 12 11 fair viable Top broke off, landmark tree remove
111 western red cedar 20 76 4 13 6 6 good viable remove
112 western red cedar 28, 24 (37)96 17 19 8 9 fair viable Forks at 2', landmark tree remove
113 western red cedar 25 77 18 6 5 17 fair viable Decay remove
114 western red cedar 32 68 2 17 7 14 fair viable
decay, forked top, slight lean S,
landmark tree remove
115 western red cedar 24 46 poor non-viable
Trunk splitting,
hazardous - non-significant remove
116 western red cedar 28 79 16 10 20 fair viable Connected at base to tree 115 remove
117 western red cedar 33 89 17 / 16 17 / 16 14 / 16 16 / 16 good viable
Trunk forks at ~30', some included
bark, landmark tree remove
118 Douglas-fir 27 109 8 / 13 10 / 13 12 / 13 9 / 13 good viable flat trunk on north side retain
119 Douglas-fir 26 120 4 / 12 15 / 12 9 / 12 4 / 12 good viable retain
120 Douglas-fir 21 91 12 / 10 9 / 10 16 / 10 good viable retain
121 Douglas-fir 16 81 5 / 8 9 / 8 12 / 8 6 / 8 fair viable retain
122 Douglas-fir 31 118 9 18 6 16 good viable landmark tree remove
123 Douglas-fir 28 111 13 8 9 11 good viable some old lower trunk bleeding remove
124 Douglas-fir 29 118 7 / 12 11 / 12 11 / 12 good viable retain
125 European larch 10 30 10 9 2 9 fair viable remove
126 Douglas-fir 38 110 20 25 24 18 good viable landmark tree remove
127 western red cedar 35 78 19 18 21 good viable
landmark tree,
in 106th Ave SE right-of-way remove
128 quaking aspen 11 55 9 6 5 11 good viable remove
129 quaking aspen 7 27 0 11 8 2 fair viable remove
130 European larch 14 76 10 6 7 9 fair viable poor trunk taper remove
131 European larch 15 74 6 8 6 11 fair viable poor trunk taper remove
Drip-Line/Limits of Disturbance (feet)
Tree Summary Table American Forest Management, Inc.
For:Skattum Plat Date:12/7/2016
City of Renton Inspector:Wilkinson
Tree/DBH Height
Tag #Species (inches)(feet)Condition Viability Comments Proposal
N S E W
Drip-Line/Limits of Disturbance (feet)
132 Douglas-fir 20 74 10 13 6 15 fair viable
Phaeolus schweinitzii conk
found 1' from trunk on east side remove
133 European white birch 16 64 13 12 7 16 fair viable Burl on trunk remove
134 grand fir 28 77 12 16 14 15 good viable Forked top remove
135 western red cedar 26 84 15 12 19 12 fair viable Forked trunk, minor included bark remove
136 Douglas-fir 13 81 7 10 9 5 good viable remove
137 Douglas-fir 25 115 11 10 8 12 good viable remove
138 Douglas-fir 16 95 10 7 6 12 good viable remove
139 Douglas-fir 24 111 11 17 12 23 good viable remove
140 Douglas-fir 16 100 3 7 6 10 good viable remove
141 Douglas-fir 17 98 11 10 6 12 good viable remove
142 Douglas-fir 22 109 11 14 8 10 good viable remove
143 Douglas-fir 28 110 8 / 13 18 / 13 6 / 13 14 / 13 good viable remove
144 Douglas-fir 33 101 15 / 15 16 / 15 18 / 15 8 / 15 good viable landmark tree remove
145 western red cedar 22 83 6 / 12 12 / 12 16 / 12 5 / 12 good viable in grouping with tree #146 remove
146 western red cedar 27 85 8 / 14 11 / 14 9 / 14 11 / 14 good viable in grouping with tree #145 remove
147 Douglas-fir 29 118 15 8 11 13 good viable remove
148 Douglas-fir 19 100 7 7 9 14 good viable remove
149 English oak 25 91 4 19 11 17 good viable Forked trunk remove
150 Douglas-fir 17 45 13 11 17 good viable remove
151 Douglas-fir 20 95 10 11 good viable Slight lean N remove
152 Douglas-fir 19 91 16 15 good viable remove
153 Douglas-fir 11 63 11 8 good viable remove
154 Douglas-fir 18 85 12 14 good viable remove
155 Douglas-fir 19 83 6 14 good viable remove
156 Douglas-fir 12 52 8 7 7 good viable remove
157 western red cedar 23 38 15 12 11 good viable remove
158 western red cedar 13 23 10 9 9 good viable remove
159 western red cedar 18 39 14 / 15 7 / 15 12 / 15 fair viable Topped retain
160 western red cedar 14 45 13 / 12 9 / 12 7 / 12 fair viable Topped retain
161 western red cedar 19 55 12 / 10 9 / 10 10 / 10 good viable retain
162 western red cedar 23 61 12 / 16 10 / 16 6 / 16 good viable retain
163 Willow 6, 5, 4 (9)39 14 / 6 13 / 6 9 / 6 fair viable retain
164 Douglas-fir 12 51 14 / 6 15 / 6 good viable retain
Tree Summary Table American Forest Management, Inc.
For:Skattum Plat Date:12/7/2016
City of Renton Inspector:Wilkinson
Tree/DBH Height
Tag #Species (inches)(feet)Condition Viability Comments Proposal
N S E W
Drip-Line/Limits of Disturbance (feet)
165 black cottonwood 54 167 18 15 19 fair viable landmark tree remove
166 black cottonwood 45 154 18 17 11 fair viable Large limbs have failed, landmark tree remove
167 black cottonwood 12, 13 (17)55 17 19 16 17 fair viable decay, top broke off remove
168 western red cedar 23 54 16 13 14 14 good viable remove
169 Douglas-fir 23 94 10 17 15 15 good viable remove
170 western red cedar 25 85 8 9 11 11 good viable remove
201 big leaf maple 8, 7 (11)54 6 / 0 good viable Leans W, 10' east of property line protect
202 big leaf maple 16 71 6 / 2 fair viable protect
203 big leaf maple
18, 13,
15 (27)78 9 / 5 fair viable protect
204 big leaf maple
16, 18,
13 (27)70 12 / 14 fair viable 5' from property line protect
205 big leaf maple 29, 32 (43)111 5 / 14 16 / 14 19 / 14 good viable
Trunk forks at base, good
attachment, landmark tree protect
206 big leaf maple 28 73 18 / 12 good viable protect
207 Douglas-fir 28 94 10 / 2 good viable 8' S of property line protect
208 western red cedar 29, 16 (33)49 8 / 5 good viable 10' S of property line, landmark tree protect
Drip-Line and Limits of Disturbance measurements from face of trunk
Trees on neighboring properties - Drip-line and Limits of Disturbance measurements from property lines
Calculated DBH: the DBH is parenthesis is the square root of the sum of the dbh for each individual stem squared (example with 3 stems: dbh = square
root [(stem1)2 +(stem2)2 +(stem3)2].
Neighboring Trees
APPENDIX E
WETLAND and STREAM RECONASSIANCE
May 21, 2016
AOA-5175
Stein Skattum
skattum@comcast.net
SUBJECT: Wetland and Stream Reconnaissance for:
17018 and 17022 - 106th Ave. SE, Renton, WA
Parcels 008700-0265 and -0270
Dear Stein:
On May 19, 2016 I conducted a wetland and stream reconnaissance on the subject
property utilizing the methodology outlined in the May 2010 Regional Supplement to
the Corps of Engineers Wetland Delineation Manual: Western Mountains, Valleys,
and Coast Region (Version 2.0). No wetlands or streams are mapped on the City of
Renton mapping and no wetlands or streams were identified on or adjacent to the
property during the field investigation.
Each of the two parcels are currently developed with a single-family residence and
associated lawn and maintained yard areas. Scattered trees including Douglas fir
(Pseudotsuga menziesii), big-leaf maple (Acer macrophyllum), western red cedar
(Thuja plicata), and black cottonwood (Populus trichocarpa) were observed
throughout both lots. An upland forested area is located off-site to the east. This
off-site area was dominated by big-leaf maple, Indian plum (Oemleria cerasiformis),
vine maple (Acer circinatum), bracken fern (Pteridium aquilinum), trailing blackberry
(Rubus ursinus), and sword fern (Polystichum munitum). No hydrophytic plant
communities were observed on or adjacent to the property.
Borings taken throughout the two parcels revealed high chroma, dry, non-hydric,
soils and there was no evidence of ponding or prolonged soil saturation anywhere
on the property.
Stein Skattum
May 21, 2016
Page 2
Ditch
During the field investigation, a small (~1-foot wide) ditch was observed along the
east and south property lines of the site (Figure 1). Stormwater runoff from an off-
site development to the northeast is collected in a vault and the overflow is
discharged from a pipe at the NE corner of the 17018 residence. Intermittent runoff
within the ditch then drains south and west before entering the roadside ditch
adjacent the east side of 106th Ave. SE.
A slight flow was observed discharging from the off-site vault at the time of the site
visit. This runoff was observed infiltrating within the ditch near the southeast corner
of the 17018 residence and the remainder of the ditch was dry.
Since the ditch: 1) conveys entirely artificially collected stormwater runoff and 2) was
cut through an upland where no stream previously existed, the ditch should not be
considered a stream by the City of Renton or any other regulatory jurisdiction.
Conclusion
No wetlands or streams were identified on or immediately adjacent the site. This
determination is based on a field investigation during which no hydrophytic plant
communities, hydric soils, or evidence of wetland hydrology were observed.
If you have any questions regarding the reconnaissance, please give me a call.
Sincerely,
ALTMANN OLIVER ASSOCIATES, LLC
John Altmann
Ecologist
King County, Pictometry International Corp., King County
Figure 1
Date: 5/21/2016 Notes:
±The information included on this map has been compiled by King County staff from a variety of sources and is subject to changewithout notice. King County makes no representations or warranties, express or implied, as to accuracy, completeness, timeliness,or rights to the use of such information. This document is not intended for use as a survey product. King County shall not be liablefor any general, special, indirect, incidental, or consequential damages including, but not limited to, lost revenues or lost profitsresulting from the use or misuse of the information contained on this map. Any sale of this map or information on this map isprohibited except by written permission of King County.