HomeMy WebLinkAboutLUA16-000314_Report 1DEPARTMENT OF COMML rY ---------Ren ton 8 AND ECONOMIC DEVELOPMENT
DATE:
PROJECT NUMBER:
PROJECT NAME:
PROJECT MANAGER:
OWNER:
CONTACT:
LOCATION:
DESCRIPTION:
CRITICAL AREA:
PLANNING DIVISION
CERTIFICATE OF EXEMPTION
FROM CRITICAL AREAS REGULATIONS
EVALUATION FORM & DECISION
June 03, 2016
LUAlG-000314
Children's Institute Tree Removal Critical Areas Exemption
Angelea Weihs, Assistant Planner
Carrie Fannin, Children's Institute for Learning Differences
2640 Benson Rd S
Renton, WA 98055-5192
Ray Robinson, Integrated Site Design, Inc
12743 26th Ave NE
Seattle, WA 98125
2640 BENSON RD S
The applicant, Children's Institute for Learning Differences, is requesting
approval of a Critical Areas Exemption in order to remove 11 hazardous trees
and prune 4 trees on the site located at 2640 Benson Road S. The site is within
the Residential-8 (R-8) Zone and is 175,111 square feet. The site is presently
used as a private school. The site contains sensitive and protected slopes, high
landslide hazards, moderate coalmine hazards, and high coalmine hazards
within 50 feet of the site. The purpose of the tree removal is to prevent damage
by hazardous trees to residents and buildings within and nearby the subject
property. The applicant's original proposal was to remove a total of 62 trees on
site; however, upon inspection, city arborist Terry Flatley observed that several
of the trees identified for removal were not located near any buildings or
streets, but in the middle of the woods. The city determined it is unnecessary to
remove trees, except where they might pose a danger to adjacent property or
street right-of-ways. The applicant revised their proposal to remove 11 trees
and prune 4 trees. Terry Flatley concurs with the assessment of these trees and
recommends removal. The proposed tree removal has been assessed by a
geotechnical engineer, and the report indicates that the tree removal will not
have a significant impacts on the slope/critical area stability, provided the root
mass and stumps remain, and the tree removal plan include new plantings near
trees 1, 2, and 3 (See Exhibit 2).
Sensitive and Protected Slopes, High Landslide Hazards, Moderate
and High Coal Mine Hazards
Page 1 of 3
City of Renton Deportment of Commun it conomic Development Ce . rte of Exemption from Critical Areas Regulations
Children's Institute Tree Removal Critical Areas Exemption WA16·000314
EXEMPTION JUSTIFICATION: Renton Municipal Code, Section 4-3-0SOC.3.c.iii. Dangerous Trees: Removal of
non-native invasive ground cover or weeds listed by King County Noxious Weed
Board or other government agency or dangerous trees, as defined in Chapter
4-11 RMC which have been approved by the City and certified dangerous by a
licensed landscape architect, or certified arborist, selection of whom to be
approved by the City based on the type of information required. Limited to
cutting of dangerous trees; such hazardous trees shall be retained as large
woody debris in critical areas and/or associated buffers, where feasible.
FINDINGS: The proposed development is consistent with the following findings pursuant to
RMC section 4-3-0SOC.2.d:
DECISION:
CONDITIONS:
i. The activity is not prohibited by this or any other provision of the Renton
Municipal Code or State or Federal law or regulation;
ii. The activity will be conducted using best management practices as specified
by industry standards or applicable Federal agencies or scientific principles;
iii. Impacts are minimized and, where applicable, disturbed areas are
immediately restored;
iv. Where water body or buffer disturbance has occurred in accordance with an
exemption during construction or other activities, revegetation with native
vegetation shall be required;
v. If a hazardous material, activity, and/or facility that is exempt pursuant to
this Section has a significant or substantial potential to degrade groundwater
quality, then the Administrator may require compliance with the Wellhead
Protection Area requirements of this Section otherwise relevant to that
hazardous material, activity, and/or facility. Such determinations will be based
An exemption from the Critical Areas Regulations is hereby Approved with
Conditions•.
1. Planting shall be installed per the approved planting plan (Exhibit 2)
immediately following tree removal for trees 2 and 3.
2. No tree stumps shall be removed, and all trees shall be retained as large,
woody debris on site.
Page 2 of 3
City of Renton Department of Communi :conomic Development (
Children's Institute Tree Removal Critical Areas Exemption
SIGNATURE & DATE OF DECISION :
Jenn/Ye;Henning, Planning Director
~ate of Exemption from Critical Areas Regulations
LUA16-000314
June 03, 2016
Date
The above land use decision will become final if the decision is not appealed within the 14-day appeal
period (RCW 43.21.C.075(3); WAC 197-11-680).
APPEALS: An appeal of this administrative land use decision must be filed in writing together with the
required fee to the City of Renton Hearing Examiner, City of Renton, 1055 South Grady Way, Renton, WA
98057, on or before 5:00 p.m., on June 17, 2016. RMC 4-8-110 governs appeals to the Hearing Examiner and
additional information regarding the appeal process may be obtained from the Renton City Clerk's Office,
(425) 430-6510.
RECONSIDERATION: Within 14 days of the decision date, any party may request that the decision be
reopened by the approval body. The approval body may modify his decision if material evidence not readily
discoverable prior to the original decision is found or if he finds there was misrepresentation of fact. After
review of the reconsideration request, if the approval body finds sufficient evidence to amend the original
decision, there will be no further extension of the appeal period. Any person wishing to take further action
must file a formal appeal within the 14-day appeal time frame.
EXPIRATION: Five (5) years from the date of decision (date signed).
Attachments: Site Plan, Hazard Tree Mitigation Plan
Page 3 of 3
[)>
[)>
Hazard Trees 2 and 3
proposed for removal. See
Exhibit 2 for Planting Plan.
TREE INVENTORY LEGEND
:tf;;,,:.~ TREE PREVIOUSLY REMOVED
~ TREE TO BE RETAINED
~ _..
TREE TO BE REMOVED
[)> p-TREE TO BE PRUNED
CRITICAL AREA BOUNDARY ,---i
15' CRITICAL AREA BUFFER SETBACK L __ _J ,a AREA TO BE CLEARED -FUTURE BUILDING SITE
TREE INVENTORY PLAN
SCALE, I" -so'
Trees located off-site
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THE REPORT INCLUDES A TREE Pl.AN AND INVENTORY, WHICH
DOCUMENTED THE HAZARD TREE SIZE, SPECIES, CONDITION, RISK RATING,
AND RECOMMENDED ACTION. THE TREES ARE IDENTIFIED l=ON SITE WITH
METAL TAGS CORRESPONDING TO TREE INVENTORY NUMBERING SYSTEM.
ALL TREES APPROVED FOR REMOVAL HAVE A BLUE DOT PAINTED ON THE
TRUNK AND APPROVED FOR PRUNING HAVE A BLUE LETIER P PAINTED ON
THE TRUNK
I MEGRATEDSITEOESIG
~tj 26TH AYF. ME
SEATT\.E, WA 91!112:,
?I 2D8.3fll.ll04II ~-CHILDRENS INSTITlrrE
2640 Benson Road S.
Rrnton, WA
lREE IN"1::NTORY PLAN
NOTE:
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t----cq, r-. ~ ··--,} I!\ N I
. 1 · 1 , ;o ii -.. -,_,,_~I =, i:i::
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SEE ARBORlSTS REPORT FOR TREE INVENTORY TABLE ON L 1
0 50 100
SCALE IN FEET
150
~
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l iii.-11-11 i.iiii iiia.
"'"'"" ''""""'""'"'"""''°'"'''""
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PLANT LIST
~ Scientific Name Common Name
Deciduous T,eea
Ac 2 Acer c1rc1nauxn Vine Maple
Evergreen Shrubs
Vo 8 Vac:imum ovatum E..ergreen Huckleberry
Deciduous Shrub
Cef 7 Corrus slolonilere "Arciic Fire" Hybnd Redtwig DogMXld
Sa 10 Symptnoc•;ius
Ground Cover
Pm
M,
15
200
Polystichurr-munitixn
Mahoma l"Elf!ns
Saowborry
Swortl Fem
Low Oregon Gra~
Ml"(IQAJION PLANTING
Ground cover
MITIGATION PLANTING
Shrubs
MITIGATION PLANTING
Trees
PL.ANTING BOUNDARY
groundcover under shrubs
Sl:i:e
6-8'ht
2-0>
2-Gal
2-Gal
1-Gal
1-Gal
S.e_acing Note
As shoWn Multi-trunk
3'o.c
3'o.c.
3'o.c
2'o.c
18" o.c.
\
Full and symetrical
~---
-----
LANDSCAPE NOTES
THIS Pl.AN IS~EDOli THE Bl.l1LDIOO PEA:MITTFIEE RETEITTION ?L,\N DATED JUNE 18,
?('114 W1TH TREE NOTATION PER THE AABOflEAL REPORT
DATED DECEMBER 2, 2011iTHE MITIGATION Pl.ANTING IS F!£QUIFlEO RAS!;OON TI-IE
GEOTECHNICAl ~ENT ANO AS DELINEATED IN THE GEOT'EC,._IC,t,I.
EVALUATION OF fiAZAAll TREE REMOVAL ,iEPQRT DATED MARCM 25TH, 21l11
2. THE P-.:lSEO Pl.l<>ITINGS ME iNT'EtlOED 4S MITIGATION OF TREE REl,UNAI. NID
GROUND DIST1JRIIANCE !!£SUL Tl'-IG FROM THE Tll£E REl,IOIIAI.
3. Tl1E PI..ANTIOOS SHOWN ARE REQUIRED MIIED SOLEY ON THE TREE REMOVAL
~. LOCATIONSNIIDQUANTJTIES MAY INCREASE BASED ON THE N;T\.l,\l GROUND
OlsnJ-CE.
--------
-----~
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CHILDREN'S INSTITUTE I HAZARD TREE" MITIGATION PLANTING PLAN
May 25, 2016 Scale: Y,6 " = 1'-0"
----
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16 ~
DEPARTMENT OF COMMUN IT
AND ECONOMIC DEVELOPMENT -------Renton®
DATE:
PROJECT NUMBER:
PROJECT NAME:
PROJECT MANAGER:
OWNER:
CONTACT:
LOCATION:
DESCRIPTION:
CRITICAL AREA:
PLANNING DIVISION
CERTIFICATE OF EXEMPTION
FROM CRITICAL AREAS REGULATIONS
EVALUATION FORM & DECISION
June 03, 2016
LUA16-000314
Children's Institute Tree Removal Critical Areas Exemption
Angelea Weihs, Assistant Planner
CARRIE FANNIN, CHILDREN'S INSTITUTE FOR LEARNING DIFFERENCES
2640 Benson Rd S
Renton, WA 98055-5192
Ray Robinson, Integrated Site Design, Inc
12743 26th Ave NE
Seattle, WA 98125
2640 BENSON RD S
DATE
NAME
Jennifer T. Henning
Vanessa Dolbee
Sabrina Mirante
Jennifer Cisneros
Angelea Weihs
The applicant, Children's Institute for Learning Differences, is requesting
approval of a Critical Areas Exemption in order to remove 11 hazardous trees
and prune 4 trees on the site located at 2640 Benson Road S. The site is within
the Residential-8 (R-8) Zone and is 175,111 square feet. The site is presently
used as a private school. The site contains sensitive and protected slopes, high
landslide hazards, moderate coalmine hazards, and high coalmine hazards
within SO feet of the site. The purpose of the tree removal is to prevent damage
by hazardous trees to residents and buildings within and nearby the subject
property. The applicant's original proposal was to remove a total of 62 trees on
site; however, upon inspection, city arborist Terry Flatley observed that several
ofthe trees identified for removal were not located near any buildings or
streets, but in the middle of the woods. The city determined it is unnecessary to
remove trees, except where they might pose a danger to adjacent property or
street right-of-ways. The applicant revised their proposal to remove 11 trees
and prune 4 trees. Terry Flatley concurs with the assessment of these trees and
recommends removal. The proposed tree removal has been assessed by a
geotechnical engineer, and the report indicates that the tree removal will not
have a significant impacts on the slope/critical area stability, provided the root
mass and stumps remain, and the tree removal plan include new plantings near
trees 1, 2, and 3 (See Exhibit 2).
Sensitive and Protected Slopes, High Landslide Hazards, Moderate and High Coal Mine Hazards
Page 1 of 3
April 28, 2016
Ray Robinson
Integrated Site Design, Inc.
12743 26th Avenue NE
Seattle, WA 98125
SUBJECT: "On Hold" Notice
Community & Economic Development Department
C.E. "Chip"Vi ncent, Administrator
Children's Institute Tree Removal Critical Areas Exemption
LUA16·000314
Dear Mr. Robinson:
The Planning Division of the City of Renton accepted the above master application for
review on April 11, 2016. During our review, staff has determined that additional
information is necessary in order to proceed further. The city arborist, Terry Flatley, has
visited the site and reviewed the conditions of the site in relation to the arborist report.
Terry Flatley observed that this is a wooded site. Several of the trees identified for
removal are not located near any buildings or streets etc., but in the middle of the
woods. It is unnecessary to remove trees, except where they might pose a danger to
adjacent property or street right of ways.
You and your client have expressed concerns for the safety of the children who are
using this wooded area as a trail/recreational space. A Critical Areas Exemption is
required for trails within geologic hazardous areas. We do not have record of Critical
Areas Exemption issued for this purpose. Therefore, the referenced trails are not legally
permitted.
In order to move forward with this proposal you will need to submit a revised arborist
report that identifies targets for trees proposed for removal. Trees that do not pose a
danger to adjacent structures or street right of ways shall be retained, and your tree
removal plan will need to be revised accordingly. The submitted geotechnical report
recommended new plantings around trees 1 through 3. If these trees do pose a danger
Renton City Hall • 1055 South Grady Way , Renton, Washington 98057 • rentonwa.gov
•
to adjacent structures or street ROWs, a planting plan will be required. If these trees do
not pose a danger to nearby property/ROWs, the trees will need to be retained and,
therefore, no planting plan will be required.
In addition, your site plan indicates that you are proposing to remove trees that are not
located on your site, but appear to be located on Fred Nelsen Middle School property.
The city cannot authorize you to remove these trees without approval from the
property owner. Please either remove these trees from the scope of your project, or
provide a revised master application form that includes the address, parcel number,
contact information, and the notarized signature of the owner (or authorized
representative) of the Fred Nelsen school.
At this time, your project has been placed "on hold" pending receipt of the requested
information. The requested information will need to be submitted before September 1,
2016, so that we may continue the review of the above subject application. Please
contact me at (425) 430-7312 lfyou have any questions.
Sincerely,
Angelea Weihs
Assistant Planner
cc: Chlldren 1s Institute for Learning Differences/ Owner(s)
Ray Robinson/ Applicant
City of Renton File LUA16-000314
2 il integrated site design
~
ti ro 12743 26th Av& NE
§. Seattle, WA 98125
g P: 206.36::3.9049 I www.J-s-d.com
Ms. Weihs,
Attn: Angelea Weihs
Assistant Planner
City of Renton
1055 S. Grady Way
Renton, WA 98057
Re: CHILD
Letter of Understanding Geologic Risk
2640 Benson Road South Renton, Wa 98055
Date: 04.09.2016
As the applicant and owners representative, I am providing all the documents requested by the City of Renton
Planning Department for the proposed removal of trees within the subject property as shown in the Arborists
Report.
Additionally, and as requested, a Geotechnical Engineer was engaged to assess the site and make
recommendations regarding the tree removal as a portion of the site is identified as being within an Environmental
Critical Area. Steep slope, Landslide, and Coal Mine Hazards were the specific conditions which the Geotechnical
Engineers assessed. The report stated that there would be no measurable adverse impact to the site provided the
recommendations were followed during tree removal.
Our client and owner of the property, the CHILD institute, has been made aware of the requirements for tree
removal and understands and accepts the risk of developing in an unstable area and that they will advise, in
writing, any prospective purchasers of the site, or any prospective purchasers of structures or portions of
structures on the site, of the unstable potential of the area.
Please let me know if this letter is sufficient for compliance with the required letter of understanding.
Respectfully,
Ray Robinson, RLN ASLA
Cc: Carrie Fannin and the Child Board of Directors
Print Form · Res~t Form Sa•e Form
DEPARTMENT OF COMMUNITY
AND ECONOMIC DEVELOPMENT R CITYOF ~ --------enton~
Planning Division
LAND USE PERMIT MASTER APPLICATION
PROPERTY OWNER($) PROJECT INFORMATION
NAME: Children's Institute for Learning Difference
PROJECT OR DEVELOPMENT NAME:
Children's Institute for Learning Differences
PROJECTIADDRESS(S)/LOCATION AND ZIP CODE:
ADDRESS: 2640 Benson Road S. 2640 Benson Road S.
Renton, WA 98055
CITY: Renton ZIP: 98055
TELEPHONE NUMBER: (206) 232-8680 KING COUNTY ASSESSOR'S ACCOUNT NUMBER($):
2923059102
APPLICANT (if other than owner)
NAME: Ray Robinson EXISTING LAND USE(S}:
School {private)
COMPANY (if applicable): Integrated Site Design, Inc
PROPOSED LAND USE(SJ:
School (private)
EXISTING COMPREHENSIVE PLAN MAP DESIGNATION:
ADDRESS: 12743 26th Ave NE
PROPOSED COMPREHENSIVE PLAN MAP DESIGNATION
CITY: Seattle ZIP: 98125 (if applicable)
TELEPHONE NUMBER: (206) 363-9049 EXISTING ZONING:
R-8
CONTACT PERSON PROPOSED ZONING (If applicable):
NAME: Ray Robinson SITE AREA (in square feet):
175,111
SQUARE FOOTAGE OF PUBLIC ROADWAYS TO BE
COMPANY (If applicable): Integrated Site Design, Inc DEDICATED:
ADDRESS: 12743 26th Ave NE SQUARE FOOTAGE OF PRIVATE ACCESS EASEMENTS:
PROPOSED RESIDENTIAL DENSITY IN UNITS PER NET
CITY: Seattle ZIP: 98125 ACRE (If applicable)
TELEPHONE NUMBER AND EMAIL ADDRESS: NUMBER OF PROPOSED LOTS (if applicable}
(206) 363-9049
r.robinson@i-s-d.com NUMBER OF NEW DWELLING UNITS (If applicable):
1
H :\CED\Data \Forms-Templates\Self-H elp Handouts\Planning\Master App Ilea tion.doc Rev:08/2015
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I,
PROJECT INFOR)IAAT.-IO_N_~(,c_o_n_ti_nu_e_d~I) _______ -,
,-. PROJECT VALUE: NUMBER OF EXISTING DWELLING UNITS (if applicable):
!
\.,
I
SQUARE FOOTAGE OF PROPOSED RESIDENTIAL IS THE SITE LOCATED IN ANY TYPE OF
BUILDINGS (if applicable}:
\_.
(
f
ENVIRONMENTALLY CRITICAL AREA, PLEASE INCLUDE
SQUARE FOOTAGE (if applicable):
SQUARE FOOTAGE OF EXISTING RESIDENTIAL
BUILDINGS TO REMAIN (if applicable): CJ AQUIFlER PROTECTION AREA ONE
SQUARE FOOTAGE OF PROPOSED NON-RESIDENTIAL CJ AQUIFIER PROTECTION AREA TWO
>-·
• \· ~
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~-
~-
t
BUILDINGS (if applicable): o
SQUARE FOOTAGE OF EXISTING NON-RESIDENTIAL
BUILDINGS TO REMAIN (if applicable): 10,899
NET FLOOR AREA ON NON-RESIDENTIAL BUILDINGS (if
applicable}:
NUMBER OF EMPLOYEES TO BE EMPLOYED BY THE NEW
PROJECT (if applicable}:
-·--------·· ····-·---····--·--
CJ FLOOD HAZARD AREA sq. ft
CJ GEOLOGIC HAZARD sq. ft.
CJ HABITAT CONSERVATION sq. ft.
CJ SHORELINE STREAMS & LAKES sq. ft.
CJ WETLANDS sq. ft.
LEGAL DESCRIPTION OF PROPERTY
(Attach leaal description on separate sheet with the followina Information included)
SITUATE IN THE NW QUARTER OF SECTION~. TOWNSHIP~. RANGE _s_, IN THE CITY
· OF RENTON, KING COUNTY, WASHINGTON
AFFIDAVIT OF OWNERSHIP
I, (Print Name/s) declare under penalty of perjury und~ laws of 1ha S!Ble of
Washington that I am (please check one) the current owner of the property involved in U,is application or L.l!S,I the authorized
representative to act for a corporation (please attach proof of autholization) and that the foregoing statements and answe1'$ herein
·ned and th · tion herewith er In all respects true and correct to tne best of my knowledge and belief.
~-/'7-1
Date Signature of OWner/Representative Date
COUNTY OF KING
I cerofy that I know or have oatiofactory evidence that l'.'.?a rr/e Noa, ·a, signed this Instrument and
acknowledge it to be his/her/their free and voluntary act for the uses and purpose mentioned in tna Instrument
Dated
--
Not11y Public
S1111 ot W11hlngton
,fl<ifLI, L ~
Notary Public in and for the tateof Washington
Notary {Print):
. DIANE L HUTTON
Mr At1Paintmtt11 Explm Nov 18, 2017 My appointment expires: -"-/.,_/,_/;.,_..g"'},."''.;:M""..,_J._.7._ ________ _ ~--... _ .. _ ...... _ ............. _ ... _,....(
2
H :\CED\Data \Forms-T emplates\Se If-Help Handouts\P!anning\Ma:ster Appll cation.doc Rev:08/2015
' )
CRITICAL AREAS EXEMPTION
Applicant Name
Ray Robinson
Parcel Number
(FOR SEPA EXEMPT ACTIVITIES)
Planning Division
1055 South Grady Way-Renton, WA 98057
Phone: 425-430-7200 Fax: 425-430-7231
Project Name
Children's Institute
Project Address
Phone Number
206 363 9049
2923059102 2640 Benson Road 5, Renton, WA 98055
Brief Description of Project
Per recommendations in the attached arborist's report, 62 dead and dying hazard trees are required to
be removed and 1 is to remain and pruned to remove dead wood. The City has identified that a portion
of the site contains sensitive and protected slopes, high landslide hazards, moderate coalmine hazards,
and high coalmine hazards within SO feet of the site. The site has been assessed by a geotechnical
engineer and the report indicates the required action of tree removal, provided the root mass and
stumps remain, will not be an impact to slope stability or any coal mine related elements. All work is to
prevent damage to residents and buildings within the subject property and neighboring properties by
hazard trees.
Type of Critical Area
IZI Work Occurs in Buffer Steep Slope Work Occurs in Critical Area
PURPOSE: Exempt activities provided with a letter of exemption from the Development Services
Administrator may intrude into a critical area or required buffer (Subject to any conditions or
requirements provided by the Administrator).
APPLICABILITY OF EXEMPTIONS: The following is a general list of activities that may be exempt from the
critical areas regulations. More specific descriptions of the activities are contained in the Critical Areas
Regulations. Some of the listed activities may not be exempt in certain critical areas. The Planning
Division will evaluate you request according to the City of Renton Critical Areas Regulations in RMC 4-3-
0SOC, J, L, and N.
I AM REQUESTING A CRITICAL AREAS EXEMPTION FOR ONE OR MORE OF THE FOLLOWING ACTIVITIES:
D Conservation, Enhancement, and Related Activities:
• Conservation or preservation of soil, water, vegetation, fish, and other wildlife
• Enhancement activities as defined in chapter 4-11 RMC D;
• Any critical area, buffer restoration, or other mitigation activities that have been approved
by the City
D Research and Site Investigation:
• Nondestructive education and research
• Site investigative work necessary for land use application submittals such as surveys, soil
logs, etc.
F:\Projects\Commercial\Wangerin Architects\Childrens lnstitute\3 Permit\3 Critical Areas Exemption\PDFs-Completed Forms\2016-03-15\0ld\Critical
Areas Exemption Short Form (2016-03-15),docx
D Agricultural, Harvesting, and Vegetation Management:
• Harvesting wild foods
• Existing/Ongoing agricultural activities 1
• Removal of dead, terminally diseased, damaged, or dangerous ground cover or hazardous
trees which have been certified as such by a forester, registered landscape architect, or
certified arborist
D Surface Water Alteration:
• New surface water discharges provided the discharge meets the requirements of the
Storm and Surface Water Drainage Regulations 1 2 3
• New or modified regional storm water facilities 12 3
• Flood hazard reduction 1 3 4 6
D Roads, Parks, Public and Private Utilities:
• Relocation of Existing Utilities out of Critical Area and Buffer
• Maintenance, operation, and repair of existing parks, trails, roads, facilities, and utilities 12
• Installation, construction, replacement, or operation of utilities, traffic control, and
walkways within existing improved right-if-way or easement 1 2
• Modification of existing utilities and streets by 10% or less 1 2 5
• Management and essential tree removal for public or private utilities, roads and public
parks 1
D Wetland Disturbance, Modification, and Removal:
• Any activity in small Category 3 wetlands 1 2 3 4 5
• Temporary disturbances of a wetland due to construction activities that do not include
permanent filling 1 2 3 5
D Maintenance and Construction for Existing Uses and Facilities:
• Remodeling, replacing, or removing existing structures 1 2
• Normal and routine maintenance and repair of any existing public or private uses and
facilities where no alteration of the critical area and required buffer or additional fill
materials will be placed 1 2
• Construction activity connected with an existing single family residence or garage,
provided that no portion of the new work occurs closer to the critical area or required
buffers than the existing structure and/or the developed area of the site 12
• Existing activities which have not been changed, expanded or altered provided they
comply with the applicable requirements of chapter 4-10 RMC 1
l2S'.J Emergency Activities:
• Removal of trees or ground cover by a City department, agency, public, or private utility in
an emergency situation
• Public interest emergency use, storage, and handling of hazardous materials by
governmental organizations in an Aquifer Protection Area
F:\Projects\Commercial\Wangerin Architects\Childrens lnstitute\3 Permit\3 Critical Areas Exemption\PDFs -completed forms and\2016-03-15\Critical Areas
Exemption Short Form (2016-03-15).docx
ADDITIONAL PERMITS: Additional permits from other agencies may be required. It is the applicant's
responsibility to obtain these other approvals. Information regarding these other requirements may be
found at http://apps.ecy.wa.gov/opas/
F:\Projects\Commercial\Wangerin Architects\Childrens lnstitute\3 Permit\3 Critical Areas Exemption\PDFs -completed forms and\2016-03-15\Critical Areas
Exemption Short Form (2016-03-15).docx
I, the undersigned, declare under penalty of perjury under the laws of the State of Washington, that to
the best of my knowledge the above information 1s true and complete.
Applicant Signature: ~ _., Date: March 15th 2016
D Exemption Granted
C.E. "Chip" Vincent, Planning Director
Planning Division
Conditions of Approval
'Exemption does not apply in Aquifer Protection Areas
'Exemption does not apply in Flood Hazard Areas
'Exemption does not apply in Geologic Hazard Areas
'Exemption does not apply in Habitat Conservation Areas
'Exemption does not apply in Streams and Lakes: Class 2 to 4
6Exemption does not apply in Wetlands
D Exemption Denied
Date
F:\Pl"Ojects\Commercial\Wangerin Arcllitects\Childrens !nstitutt=:\3 PE"nn1t\3 Cr1trcal Areas Exernption\PDFs -completed forms and\2016-03-15\Cntical Areas
Exemption Short Fann (2016-03-15).docx
DEPARTMENT OF COMMUNITY
AND ECONOMIC DEVELOPMENT Renton0
WAIVER OF SUBMITTAL REQUIREMENTS
FOR LAND USE APPLICATIONS
Planning Division
1055 South Grady Way-Renton, WA 98057
Phone: 425-430-7200 I www.rentonwa.gov
LAND USE PERMIT SUBMITIAL REQUIREMENTS: WAIVED MODIFIED
BY: BY:
Arborist Report 4
Biological Assessment, /L5
Calculations,
Colored Maps for Display , -··
Construction Mitigation Description i••••
Deed of Right-of-Way Dedication, I -~----·-
Density Worksheet, .•.
Drainage Control Plan 2 ( b,,.
" . "
Drainage Report 2
Elevations, Architectural,_,
Environmental Checklist,
Existing Covenants (Recorded Copy) 1 ••••
Existing Easements (Recorded Copy) """'
Flood Hazard Data, 1~s
Floor Plans"""'
Geotechnical Report 2 ANDl '
Grading Elevations & Plan, Conceptual, r I'< .. \. JC',.
Grading Elevations & Plan, Detailed 2
I
Habitat Data Report 4
Improvement Deferral ,
Irrigation Plan,
COMMENTS:
PROJECT NAME: Cl-\-! L]) Sc.J,,.= l Un±. frreos fixa,w.p.
DATE: '). /,2.,, I I b
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LAND USE PERMIT SUBMITTAL REQUIREMENTS:
WAIVED MODIFIED COMMENTS: BY: BY:
King County Assessor's Map Indicating Site 4
Landscape Plan, Conceptual•
Landscape Plan, Detailed,
Legal Description,
Letter of Understanding of Geological Risk,
Map of Existing Site Conditions,
Master Application Fonn,
Monument Cards (one per monument),
Neighborhood Detail Map,
Overall Plat Plan ,
Parking, Lot Coverage & Landscaping Analysis 4
Plan Reductions (PMTs),
Post Office Approval ,
Plat Name Reservation , I
Plat Plan 4
Preapplication Meeting Summary, I'.:-~
Public Works Approval Letter,
Rehabilitation Plan ,
Screening Detail,
Shoreline Tracking Worksheet•
Site Plan ""°,
Stream or Lake Study, Standard, f:;::. ~
Stream or Lake Study, Supplemental 4
Stream or Lake Mitigation Plan 4 -
Street Profiles ,
ntle Report or Plat Certificate 1AND4
Topography Map,
Traffic Study 2
Tree Cutting/Land Clearing Plan ,
Urban Design Regulations Analysis,
Utilities Plan, Generalized 2
Wetlands Mitigation Plan, Final ,
Wetlands Mitigation Plan, Preliminary,
H: \C£0\Data \forms-T em plates\Se lf-H elp Handouts \Plannlng\ W a Ive rs ubmittalreq5.doo; Res:08/2015
LAND USE PERMIT SUBMl1TAL REQUIREMENTS:
Wetlands Report/Delineation 4
Wireless:
Applicant Agreement Statement,••••
Inventory of Existing Sites ,..0 ,
Lease Aoreement, Draft'•""'
Mao of Existing Site Conditions 2 "'"'
Map of View Area•••••
Photoslmulations >••••
This Requirement may be waived by:
1. Property Services
2 Development Engineering Plan Review
3 Building
4 Planning
WAIVED MODIFIED
BY: BY:
!CS
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H: \CE D\Data \Fotms• rem plates \Self wHel p H andou ts\Plannlng\ Wa iversubm Itta !req~. dDcx
COMMENTS:
Rev: 08/2015
GEOTECHNICAL EVALUATION OF HAZARD
TREE REMOVAL PLAN
Children's Institute for Learning Differences
2640 Benson Road South
Renton, Washington
Project No. 1601.01
March 25, 2016
Prepared for:
Children's Institute for Learning Differences
Prepared by:
ZGA
Zipper Geo Associates, LLC
Geotechnical and Environmental Consultants
19023 35th Avenue West, Suite D
Lynnwood, WA 98036
Zipper Geo Associa_ s, LLC
Geotechnical and Environmental Consulting
Children's Institute for Learning Differences
2640 Benson Road South
Renton, Washington 98055
Attention: Ms. Carrie Fannin
Project Number 1601.01
March 25, 2016
Subject: Geotechnical Evaluation of Hazard Tree Removal Plan
Children's Institute for Learning Differences
2640 Benson Road South
Renton, Washington 98055
Dear Ms. Fannin,
In accordance with your request and written authorization, Zipper Geo Associates, LLC (ZGA)
has completed the subsurface exploration and geotechnical evaluation of the Hazard Tree
Removal Plan prepared by others for the Children's Institute for Learning Differences (CHILD)
campus located at 2640 Benson Road South in Renton, Washington. This report presents the
findings of our site reconnaissance and subsurface exploration, and our geotechnical
recommendations for the project. Our work was completed in general accordance with our
Proposal for Geotechnical Engineering Se,vices (Proposal No. P16151) dated March 4, 2016.
We appreciate the opportunity to be of service to you on this project. If you have any questions
concerning this report, or if we may be of further service, please contact us.
Sincerely,
Zipper Geo Associates LLC
James P. Georgis, L.E.G.
Principal
Copies: Addressee ( 1 )
Ray Robinson with Integrated Site Design, Inc. (1)
19023 36"' Avenue West, Suite D Lynnwood, WA 98036
Thomas A. Jones, P.E.
Principal
(425) 582-9928
TABLE OF CONTENTS
INTRODUCTION ....................................................................................................................... 1
SITE DESCRIPTION .................................................................................................................. 1
PROJECT UNDERSTANDING .................................................................................................. 1
SITE RECONNAISSANCE. ........................................................................................................ 2
Southeast Tree Removal Area ............................................................................................... 2
Northeast Tree Removal Area ................................................................................................ 3
Northwest Tree Removal Area ............................................................................................... 4
Central Playground Slope Tree Removal Area ....................................................................... 4
SUBSURFACE CONDITIONS ................................................................................................... 4
Published Geologic Mapping .................................................................................................. 4
Soil Conditions ....................................................................................................................... 5
Groundwater Conditions ......................................................................................................... 6
Historic Coal Mine Maps ......................................................................................................... 6
CONCLUSIONS AND RECOMMENDATIONS ........................................................................... 7
General .................................................................................................................................. 7
Geologic Hazard ECA Considerations .................................................................................... 7
Tree Stump and Root System Retention ................................................................................ 8
Planting Recommendations .................................................................................................... 9
Temporary Erosion Control Considerations ........................................................................... 10
Retention of Woody Material ................................................................................................. 10
Off-Site Tree Removal Considerations .................................................................................. 10
General Steep Slope Considerations ..................................................................................... 10
CLOSURE ................................................................................................................................ 11
FIGURES PREPARED BY ZGA
Figure 1 -Vicinity Map
Figure 2 -Site and Exploration Plan
FIGURES PREPARED BY OTHERS
Tree Inventory Plan, Sheet L 1.1
Tree Inventory Table, Sheet L 1.2
APPENDICES
Appendix A -Subsurface Exploration Procedures and Logs
GEOTECHNICAL EVALUATION OF HAZARD TREE REMOVAL PLAN
CHILDREN'S INSTITUTE FOR LEARNING DIFFERENCES
2640 BENSON ROAD SOUTH
RENTON, WASHINGTON
Project No. 1601.01
March 25, 2016
INTRODUCTION
This report documents the surface and subsurface conditions encountered at the site and our
geotechnical evaluation of the Hazard Tree Removal Plan prepared by others for the Children's
Institute for Learning Differences (CHILD) campus located at 2640 Benson Road South in Renton,
Washington. The project description, site conditions, and our geotechnical conclusions and
recommendations are presented in the text of this report. Supporting data including detailed
exploration logs, field exploration procedures, and other supporting information are presented as
appendices.
Our geotechnical scope of services for the project included a document review, site
reconnaissance, subsurface evaluation, geotechnical analysis, and preparation of this report. The
subsurface evaluation consisted of completing four hand auger explorations (designated HA-1
through HA-4) located near proposed tree removal areas and steep slopes. The hand auger
explorations extended approximately 3Y:. to 6 feet below the existing ground surface.
SITE DESCRIPTION
The site is located at 2640 Benson Road South in Renton, Washington. The CHILD facility is
located in the south-central portion of the site and includes campus buildings and a perimeter
access drive with a parking lot on the east side of the facility. The northern portion of the site is
undeveloped and includes mixed evergreen and deciduous trees with a moderately well-
developed understory of brush and groundcover. The site is bounded to the north by a multi-
family residential development, to the south by South 27,,, Street, to the east Benson Road South,
and to the west by a middle school. The approximate site location is shown on the enclosed
Vicinity Map, Figure 1. Existing site features, site topography, and nearby features are shown on
the enclosed Site and Exploration Plan, Figure 2.
PROJECT UNDERSTANDING
The site is mapped by the City of Renton as containing Coal Mine Hazard, Steep Slope Hazard,
and Landslide Hazard Environmental Critical Areas (ECAs). We understand that the City has
requested a geotechnical evaluation of the Hazard Tree Removal Plan be completed to assess
the risk to regulated Geologic Hazard ECAs and their associated buffers, as defined in Part 4-3-
050-G-5 of the City of Renton Municipal Code (RMC) that may result from the planned tree
removal and provide recommendations to mitigate identified risks. Our understanding of the
project is primarily based on a review of the following documents and discussions with Integrated
Site Design and representatives for CHILD.
Zipper Geo Ass, ates, LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
• Tree Risk Assessment, CHILD, 2640 Benson Road South, Renton, Washington, prepared
by Greenforest Incorporated Consulting Arborist, dated December 2, 2015.
• Children's Institute, 2640 Benson Road South, Renton WA, Tree Inventory Plan, Sheet
L 1.1, prepared by Integrated Site Design, dated March 24, 2016.
• Children's Institute, 2640 Benson Road South, Renton WA, Tree Inventory Table, Sheet
L 1.2, prepared by Integrated Site Design, dated March 24, 2016.
Based on our review of the referenced documents, it appears that the hazard tree removal plan
includes the pruning and removal of trees located within the CHILD property, and to a lesser
extent, the removal of trees from the adjacent property to the east. A summary of the planned
tree removal is presented below.
On-Site Hazard Tree Removal: The plan identifies fifty-two trees on the site that have been rated
by Greenforest Incorporated as having a moderate to high risk rating. Fifty of these trees are listed
for removal and two are listed for pruning or deadwood removal. Of the fifty-two identified trees,
forty-six trees are maple, five trees are cottonwood, and one tree is alpine fir. About thirty six of
the fifty-two trees are located within ECA areas or their buffers as shown on Plan Sheet L 1.1
Off-Site Hazard Tree Removal: The plan identifies eleven trees east of the mapped site property
line that have been rated by Greenforest Incorporated as having a moderate to high risk rating
and listed for removal. Off the eleven identified trees, two trees are maple, eight trees are willow,
and one tree is cherry. About ten of the eleven trees are located within ECA areas or their buffers
as shown on Plan Sheet L 1.1
Copies of the Tree Inventory Plan and Tree Inventory Table (Plan Sheets L 1.1 and 1.2) are
enclosed with this report without modification to assist in report interpretation.
SITE RECONNAISSANCE
We completed a reconnaissance of the property and immediate vicinity during a site visit
completed on March 16, 2016. The purpose of the reconnaissance was to identify surficial features
of site conditions such as the presence or absence of groundwater seepage, the presence or
absence of surface erosion, indications of past slope instability, indications of past land use, the
type and extent of existing vegetation, the location of trees identified for removal, and other site
features that may be affected by the planned tree removal. The enclosed Site and Exploration
Plan, Figure 2, shows the approximate location of some of the observed site features. A summary
of our site observations is presented below.
Southeast Tree Removal Area
About 10 trees are listed for removal in this area. The trees are located within a west-facing, off-
site slope that extends down to a relatively new rockery wall constructed just within the property
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Zipper Geo Associate .LC
Children's Institute for Leaming Differences
Project No. 1601.01
March 25, 2016
line. Based on the topographic site plan, the slope inclination above the rockery ranges from about
23 to 44 percent (13 to 23 degrees). The rockery appears to be in good condition, ranges from
about 4 to 6 feet tall, includes a drainage zone of quarry spall backfill, and appears to include a
perforated drain pipe. In addition to the listed trees, slope vegetation includes dense Laurel
bushes, blackbeny, fern, ivy, blue star creeper, and grasses. We did not observe any obvious
indications of past slope movement or distress. Surficial erosion was slight and limited to several
foot paths. We did not observe any obvious indications of groundwater seepage from the exposed
slope surface. However, the rockery drain pipe daylights at the north end of the wall and we
observed about Y. to 1 gpm discharge from this pipe at the time of our site visit. The discharge
flowed down a roadside ditch to a dispersion area in the northwest portion of the site. The
approximate rockery groundwater discharge location and subsequent down-gradient surface
water flow is shown on Figure 2.
Northeast Tree Removal Area
For the purposes of this report, the northeast tree removal area includes the central steep slope
area located in the northern portion of the site and the gently sloping bench located between the
central steep slope area and the east property line.
The north-central, west-facing slope has inclinations ranging from about 23 to 44 percent (13 to
23 degrees). In addition to the trees listed for removal, slope vegetation includes mixed evergreen
and deciduous trees which were considered by the arborist to be of low risk and are not listed for
removal, blackbeny, fern, ivy, and grasses. Areas between vegetation were typically mantled by
several inches of forest duff. We did not observe any obvious indications of past slope movement
or distress. Surficial erosion was slight and limited to several foot paths. We did not observe any
obvious indications of groundwater seepage from the exposed slope surface. We observed what
appears to be a lobe of fill soils extending into the slope area from the eastern bench area. The
fill appeared to be relatively old and may have been associating with mass grading for the CHILD
development. The approximate location of the fill is shown on Figure 2.
The bench area located between the north-central steep slope and the east property line slopes
gently west with inclinations ranging from about 5 to 12 percent (3 to 8 degrees). We estimate
that about 60 to 70 percent on the bench is surfaced with wood chips. The remainder of the area
consists of soil with scattered ferns and grass. We did not observe any obvious indications of
past slope movement or distress associate with the bench or adjacent slopes. Surficial erosion
was slight and limited to several foot paths. We observed slight surface water flow in the northern
portion of the bench area. The flow appeared to be originating from a spring located near the top
of the steep off-site slope which extends up to the adjacent middle school play field. We visually
estimated a flow rate on the order of Y. gallon per minute at the time of our evaluation. The spring
had incised a small drainage feature about two feet wide and one foot deep into the surface of
the off-site slope. Surface water from the spring was infiltrating into the bench soils at the time of
our evaluation and was not running down the north-central steep slope. The approximate location
of the spring and down-gradient surface water flow is shown on Figure 2
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Zipper Geo Ass ates. LLC
Children's Institute for Learning Differences
Project No. 1601 .01
March 25, 2016
Northwest Tree Removal Area
For the purposed of this report, the northwest tree removal area includes the north-central gently
sloping bench area located in the northern portion of the site and the steep slope area located
between the north-central gently sloping bench area and the west property line.
The north-central bench area slopes gently west with inclinations ranging from about 1 O to 17
percent (6 to 10 degrees). In addition to the trees listed for removal, vegetation includes mixed
evergreen and deciduous trees which were considered by the arborist to be of low risk and are
not listed for removal, blackberry, fern, ivy, and grasses. Areas between vegetation were typically
mantled by several inches of forest duff. We did not observe any obvious indications of past slope
movement or distress. Surficial erosion was slight and limited to several foot paths. We did not
observe any obvious indications of groundwater seepage.
The west-facing slope located between the north-central bench and the west property line has
typical inclinations ranging from about 30 to 56 percent (17 to 30 degrees). An isolated section
of slope adjacent to the sidewalk has an inclination of about 100 percent (45 degrees) with a
maximum slope height of about 6 feet, and appears to be the result of a cut completed to construct
the sidewalk. In addition to the trees listed for removal, slope vegetation includes mixed evergreen
and deciduous trees which were considered by the arborist to be of low risk and are not listed for
removal, blackberry, fem, ivy, and grasses. Areas between vegetation were typically mantled by
several inches of forest duff. We did not observe any obvious indications of past slope movement
or distress. Surficial erosion was slight and limited to several foot paths. We did not observe any
obvious indications of groundwater seepage, but standing water was present in two drainage
ditches located near the west property line at the time of our evaluation
Central Playground Slope Tree Removal Area
A steep west-facing slope is located near the middle of the site between the playground and the
main parking lot. Slope inclinations range from about 42 to 80 percent (23 to 39 degrees). Slope
vegetation primarily consists of ivy and blackberry brush, with scattered patches of grass in the
southern portions of the slope and several deciduous trees. In general, the trees located on the
slope exhibited pistol-butted growth pattern (bent trunks near the ground surface) which is
indicative of slope creep. We did not observe indications of deep-seated slope movement or
shallow sloughing. Surficial erosion was slight and limited to non-vegetated portions of the slope.
We did not observe any obvious indications of groundwater seepage.
SUBSURFACE CONDITIONS
Published Geologic Mapping
We assessed the geologic setting of the site and surrounding vicinity by reviewing The Geologic
Map of the Renton Quadrangle, King County, Washington, U.S. Geological Survey Map GQ-405,
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Zipper Geo AssoclateALc
Children's Institute for Leaming Differences
Project No. 1601.01
March 25, 2016
1965. The geologic map indicates the site and immediate vicinity are mantled by Quaternary
Ground Moraine deposits (Qg1). This deposit is described as thin glacial ablation till over lodgment
till deposited by the Vashon Stade of the Frasier glaciation. The lodgment till is further described
as a compact, unsorted mixture of sand, silt, clay, and gravel, commonly termed "hardpan". The
ablation till is described as being compositionally similar to lodgment till, but much less dense.
Tertiary age Renton Formation deposits are mapped about Y. mile to the northeast of the site.
The Renton formation is described as arkosic sandstone, mudstone, and shale with several beds
of coal. The Renton Formation has an extensive history of surface and subsurface coal mining.
Stratigraphic information presented in the referenced geologic map indicates that Renton
Formation deposits underlie the surficial glacial deposits at an unspecified depth.
Soil Conditions
The subsurface exploration for this project included four hand auger explorations (HA-1 through
HA-4) located near proposed tree removal areas and steep site slopes. The hand auger
explorations extended approximately 3Y. to 6 feet below the existing ground surface. The
approximate exploration locations are shown on the enclosed Site and Exploration Plan, Figure 2.
Soils were visually classified in general accordance with the Unified Soil Classification System.
Detailed, descriptive logs of the subsurface explorations and the procedures utilized in the
subsurface exploration program are presented in Appendix A. Generalized descriptions of
subsurface soil conditions observed at the exploration locations are presented below. The
stratification and horizontal extent of the soil types observed in our explorations may vary between
explorations. Stratification boundaries on the exploration logs represent the approximate depth
of changes in soil types, although the transition between materials may have been gradual.
Please refer to the hand auger logs in Appendix A for a more detailed description of the conditions
encountered at the exploration locations.
Hand augers HA-1 and HA-2 were completed in the northern portion of the site. In general, the
explorations encountered about 7 to 10 inches of loose, organic-rich silty sand interpreted as topsoil.
Below the topsoil, loose to medium dense silty sand with some gravel was encountered to a depth
of about 2% to 3 feet and is interpreted as weathered glacial till. Dense, silty sand with some gravel,
interpreted as unweathered glacial till, was encountered below the weathered horizon and extended
to the total depth explored of 3Y. feet below existing grade.
Hand augers HA-3 and HA-4 were completed in the west-central and central portions of the site,
respectively. These explorations encountered about 12 inches of loose organic-rich silty sand topsoil
over primarily granular deposits interpreted as glacial outwash. In hand auger HA-3, the outwash
consisted of medium dense sand with some gravel and silt which extended to the total depth explored
of 3.5 feet below existing grade. In hand auger HA-4, the outwash consisted of medium dense fine
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Zipper Geo Ass• 11tes, LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
to medium sand with some silt which extended to the total depth explored of 6 feet below existing
grade.
Groundwater Conditions
Slight groundwater seepage was observed in hand auger HA-2. Groundwater seepage was not
observed in the other hand auger explorations. The groundwater observed in HA-2 is interpreted
to represent water perched above lower permeability glacial till soils encountered at a depth of 3
feet. Given the relatively low permeability of the glacial till soils encountered in the northern
portion of the site, perched groundwater may develop above the till or within sandy zones within
the till during periods of extended wet weather. Perched groundwater may also develop above
lower permeability layers within the glacial outwash deposits, which are often stratified.
These observations represent groundwater conditions at the time of the field exploration.
Groundwater conditions should be expected to fluctuate due to changes in season, precipitation
patterns, site utilization, on-site or off-site irrigation activities, and other on-and off-site factors.
Historic Coal Mine Maps
As part of our site evaluation, we completed a review of historic coal mine maps available from
the Washington State Department of Natural Resources. Based on our review, it appears that
the site is underlain by portions of the Sunbeam Mine and Renton Mine. A summary of our historic
coal mine map review relative to these mines is presented below.
Sunbeam Mine: The Sunbeam Mine was operated by the Renton Coal Company from 1922 to
1929. The Sunbeam portal (or mine entrance) is mapped about 2/3 of a mile north-northwest of
the CHILD site and has a reported main "water level" gangway elevation of about 68 feet. The
mine chutes appear to have extended up and to the south-southwest of the main gangway (away
from the CHILD site) along a coal seam inclined or dipping to the north-northeast at an angle of
about 65 degrees from horizontal. Based on the mapped data, it appears that the Sunbeam mine
workings are primarily west of the CHILD site, with the eastern end of the mine underlying a
portion of Benson Road South and the southwestern portion of the CHILD site. Given a site
ground surface elevation of about 400 feet, it appears that those portions of the mine workings
located below or near the CHILD site are on the order of 200 to 300 feet below the ground surface.
The City of Renton has mapped the mine workings west-southwest of the site (west of Benson
Road South) as having a moderate to high risk, and the workings mapped below the CHILD site
as having a moderate risk.
Renton Mine: The Renton Mine was operated by the Seattle Electric Company in 1919 and the
Renton Coal Company from 1920 to 1955. It appears that the Renton Mine 61" Gangway South
and associated workings extended below the CHILD site. The historic maps do not include explicit
information regarding the elevation of the workings in this area. However, the workings appear to
be an extension of the generally north-northeast dipping coal seam worked in the Sunbeam Mine.
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Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
Based on the elevation of the Sunbeam main water level gangway and the indicated strata dip
angle and orientation, it appears that the Renton Mine workings in the vicinity of the site are likely
greater than 300 feet below the ground surface. The City of Renton has mapped the Renton Mine
workings at the project site and nearby vicinity as having a moderate risk.
CONCLUSIONS AND RECOMMENDATIONS
General
Based on the results of our site reconnaissance, document review, subsurface exploration, and
geotechnical analysis, it is our opinion that the proposed tree removal plan is feasible from a
geotechnical perspective. Provided that the conditions and recommendations contained within this
report and the provisions of the Renton Municipal Code (RMC) are satisfied, it is our opinion that
the proposed Hazard Tree Removal Plan will not increase the potential for soil movement and the
risk of damage to existing structures, the site, and to adjacent properties from soil instability will
not be increased. The following sections provide a discussion regarding City of Renton regulated
ECAs and recommendations to reduce risks associated with the tree removal plan.
Geologic Hazard ECA Considerations
The site is mapped by the City of Renton as containing Coal Mine Hazard, Steep Slope Hazard,
and Landslide Hazard Environmental Critical Areas (ECAs). We understand that the City has
requested a geotechnical evaluation of the Hazard Tree Removal Plan to assess the risk to
regulated Geologic Hazard ECAs and their associated buffers, as defined in Part 4-3-050-G-5 of
the City of Renton Municipal Code (RMC) that may result from the planned tree removal and
provide recommendations to mitigate identified risks.
Part 4-3-050-C-3 of the RMC indicates that the removal of dangerous trees which have been
approved by the City and certified dangerous by a licensed landscape architect or certified arborist
is exempt from RMC ECA restrictions and may be permitted by the City. The following sections
present our evaluation of Coal Mine Hazard, Steep Slope Hazard, and Landslide Hazard ECA's
relative to the Hazard Tree Removal Plan.
Coal Mine Hazard Areas: Coal Mine Hazard Areas include areas with known subsurface coal mine
workings. The site is mapped within a Medium Coal Mine Hazard Risk Area and slightly northeast
of a High Coal Mine Hazard Risk Area. Our review of historic coal mine maps for the site vicinity
(Renton Mine and Sunbeam Mine) indicate mine workings depths in excess of 200 feet. Based on
our document review and site observations, it is our opinion that the site are consistent with the
criteria for a Medium Coal Mine Hazard Risk Area.
Steep Slope Hazard Areas: The City of Renton maps portions of the site as Steep Slope Hazard
Areas. The City mapped hazard areas are primarily located along the eastern property line, within
the northern, undeveloped, wooded portion of the site, and the slope area between the main school
building and the playground area. The enclosed Tree Inventory Plan, Sheet L 1.1 identifies Steep
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Zipper Geo Ass1 ates. LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
Slope Hazard Areas and an associated 15 foot wide buffer based on site topography. Based on
our document review and site reconnaissance, it is our opinion that the critical areas and associated
buffers presented on Sheet L 1.1 are in general accordance with RMC Steep Slope Hazard Area
criteria.
Landslide Hazard Areas: The City of Renton ECA maps generally identify the central and western
portions of the northern, undeveloped, wooded area and the slope between the playground and the
school facility as High Landslide Hazard Areas, although the City mapped hazard areas to not
appear to correlate well to the site specific topography presented on Sheet L 1.1. This may be due
to the City's use of a more regional topographic database to identify hazard area. The RMC defines
a high landslide hazard area as an area with slopes greater than 40 percent, and areas with slopes
between fifteen and forty percent and underlain by soils consisting largely of silt and clay. Based on
our document review and subsurface explorations, it is our opinion that site slopes exceeding forty
percent are consistent with the RMC criteria for Landslide Hazard Areas. These areas are generally
identified on the Tree Inventory Plan, sheet 1.1.
Risk Evaluation Summary: Based on mapped mine working depths in excess of 200 feet below
existing grade, it is our opinion that the Hazard Tree Removal Plan will have no measurable adverse
impact on the Coal Mine Hazard and will not increase the risk of coal mine induced damage to the
subject site or adjacent properties. Provided that the conditions and recommendations contained
within this report and the provisions of the Renton Municipal Code (RMC) are satisfied, it is our
opinion that the proposed Hazard Tree Removal Plan will not increase the potential for soil
movement and the risk of damage to existing structures, the site, and to adjacent properties from
soil instability will not be increased.
Tree Stump and Root System Retention
Tree root systems provide erosion protection and bio-reinforcement for slope soils, thereby
increasing the strength of the soil mass and reducing the risk of slope instability. However, the
weight of the tree can increase the forces tending to drive slope instability and the rocking action
of the root mass during high winds can result in loosening of the slope soils, resulting in a
reduction in slope stability, particularly for large, heavy trees located on or near the crest of steep
slopes. There is some debate in the scientific community regarding the relative contributions of
these different factors to slope stability, but the general consensus appears to be that under most
conditions the presence of trees (in particular the bio-reinforcement they provide) results in a net
improvement to slope stability.
Based on our review of the Tree Inventory Table, it appears that about 61 of the 63 trees listed
for removal or pruning consist of cottonwood, maple, or willow. These tree species often survive
cutting by generating new growth from the stump, often referred to as stump sprouting. Stump
sprouts provide nourishment for maintenance of the root system while greatly reducing the
negative impact of tree weight and wind driven soil loosening. We therefore recommend that the
trees planned for removal be cut off near the ground surface and that the stumps and root masses
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Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
be left in place within the Steep Slope Hazard Areas and associated buffers identified on Sheet
L 1.1. We anticipate that there may be some benefit to potential utilization of the site by removing
stumps from the gently sloping bench areas located in the northern portion of the site. In our
opinion, the removal of stumps within the bench areas is feasible from a geotechnical perspective
without adversely affecting the site slopes. An 8-inch diameter alpine fir (tree #4) is listed for
removal from a grass lawn area near the perimeter access drive. In our opinion, the stump of this
tree may also be removed to facilitate landscape maintenance without adversely affecting the site
slopes.
Planting Recommendations
Some portion of the cut trees may not develop stump sprouts or may not receive adequate
nutrients from the sprouts to prevent decay of the root mass over time. Based on our evaluation
of the site conditions, it is our opinion that the decay of the root systems associated with trees 1
through 3 located near the top of the steep central slope adjacent to the playground could result
in a reduction in the stability of the slope near the removed trees relative to shallow surficial sliding.
In our experience, it typically takes about 3 to 5 years to realize a significant reduction in the bio-
reinforcement provided by a tree that does not survive cutting.
As a precautionary measure, we recommend that the Hazard Tree Removal Plan include new
plantings near trees 1 through 3. We recommend that native woody shrubs or small trees be
considered to reduce the need for watering and keep the weight and wind loading characteristics
of the new growth to reasonable levels as it matures. The following table provides some plant
species that could be considered to reduce the potential for erosion and increase resistance to
shallow surficial sloughing. The information presented below is a relatively small sampling of plant
species discussed in the 1993 publication Slope Stabilization and Erosion Control using
Vegetation, produced by the Washington State Department of Ecology (Publication 93-30). The
table below is by no means intended to be comprehensive or restrictive relative to the selection
of appropriate plantings.
POTENTIAL PLANT SELECTION GUIDE
Plant Name Form& Habit Mature Rooting Recommended
Size Characteristics Spacing
Snowberry Evergreen shrub; Height: 4' Fibrous,
(Symphoricarpos Albus) spreads by runners to Spread: 3' Shallow depth. 2'+
form thicket
Sala! Evergreen shrub; Height: 3' Fibrous,
(Gaultheria Sha/Ion) spreads by runners to Spread: 3' Shallow depth. 2'+
form thicket
Evergreen Huckleberry Evergreen shrub; does Height: 6' Fibrous, 3'+ Oemleria Cerasiformisl not spread Spread: 3' Shallow depth.
Ocean Spray Deciduous shrub; does Height: 10'+ Fibrous,
(Holodiscus Discolor) not always spread Spread: 6' Moderate depth. 4'+
aaaressivelv
Page9
Zipper Geo Ass ates. LLC
Children's Institute for Leaming Differences
Project No. 1601.01
March 25, 2016
Vine Maple Deciduous shrub; does
(Acer Circinatum) not always spread
annressivelv
Hooker Willow Deciduous shrub; does
(Salix Hookeriana) not spread
•
Height: 15'+ Fibrous,
Spread: 10' Moderate depth. 8'+
Height: 20'+ Fibrous, 3'+ Soread: 15' Moderate deoth.
Reference: Slope Stabilization and Erosion Control using Vegetation, Washington State Department of
Ecolnav Publication 93-30, 1993.
Temporary Erosion Control Considerations
We anticipate that the tree removal process will likely result in disturbance of the ground surface
and a temporary increase in the potential for erosion. We therefore recommend that the tree
removal service utilize means and methods intended to minimize ground disturbance. In addition,
we recommend that soils exposed within Steep Slope Hazard Areas and their buffers be covered
with a temporary erosion control material, such as sterile straw or arborist mulch.
Retention of Woody Material
In our opinion it appears geotechnically feasible to retain much of the woody debris generated
from the hazard tree removal as habitat enhancement within wooded portions of the site.
However, based on our evaluation, we recommend that woody material greater than 6-inches in
diameter be removed from the following areas as the weight of the material could adversely affect
steep slopes or the performance of existing drainage features.
• The drainage features near Benson Road South and adjacent steep slopes identified on
Figure 2.
• The steep slope located between the playground and the school facility and the 15-foot
wide buffer above this steep slope area.
Off-Site Tree Removal Considerations
The Hazard Tree Removal Plan appears to include the removal of 11 trees located beyond (east
of) the subject property. We recommend that all agreements and/or permits that may be needed
to complete off site work be coordinated with the adjacent property owner and the City before
beginning work.
General Steep Slope Considerations
Owners of properties containing or adjacent to steep slopes should recognize that soil loss or
downslope displacement from steep slopes is a naturally occurring mass wasting process, and
that some soil loss from steep slopes should be expected over time, particularly in response to
episodic severe storm events. The conclusions and recommendations presented in this report are
intended to allow for the removal of hazard trees while maintaining the existing stability of the site
slopes. The findings presented in this report should not be interpreted as indicating that the site
steep slopes will be stable under all possible future conditions.
Page 10
Zipper Geo AssoclateA.Lc
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
CLOSURE
The analysis and recommendations presented in this report are based, in part, on the explorations
completed for this study. The number, location, and depth of the explorations were completed
within the constraints of budget and site access so as to yield the information to formulate our
recommendations.
This report has been prepared for the exclusive use of The Children's Institute for Learning
Differences, Integrated Site Design, and their agents, for specific application to this project and
has been prepared in accordance with generally accepted geotechnical engineering practices.
No warranties, express or implied, are intended or made. Site safety is the responsibility of others.
In the event that changes in the nature, design, or location of the tree removal as outlined in this
report are planned, the conclusions and recommendations contained in this report shall not be
considered valid unless Zipper Geo Associates, LLC reviews the changes and either verifies or
modifies the conclusions of this report in writing.
Page 11
REFERENCE: GOOGLE EARTH 2016 . NOT TO SCALE
CHILDREN'S INSTITUTE FOR LEARN ING DIFFERENCES
2640 Benson Road South
Ren ton, Washington
VICINITY MAP
DATE: March 2016 Job No. 1601.01
Zipper Geo Associates, LLC FIGURE 1 19023 36th Ave. W.,Suite D
Lynnwood, WA SH T. 1 of 1
GROUNDWATER SEEPAGE
NE.AA FENCE LINE
W •=• TREE PREVIOUSLY REMOVED
~TREE.1998
~ TREE TO BE RETAINED -TREE TO BE REMOVED
D CRITICAL AREA BOUNDARY ,--,
15' CRJTJCAL AREA BUFFER SETBACK
AREA TO BE CLEARED
FUTURE BUILDING SITE
TREE INVENTORY PLA N
SCA LE: 1" = so·
·-,
~ ~ -,~ ~ i.:::_
CONSULTING ARBORISTS FOR THE CHILO INSTITUTE DATED DECEMBER 2.
201S.
THE REPORT INCLUDED A GENERAL PLAN ANO TREE lNVENTORY. WH1CH
DOCUMENTED THE HAZARD TREE S IZE. SPECIES. CONDITION. RISK RATING.
ANO RECOMMENDED ACTION. THE TREES HAVE BEEN IDENTIFIED ON SITE
ANO TAGGED BY NUMBER WHICH CORRESPONDS WITH THE TREE
INVENTORY.
ALL TREES THAT THE ARBORIST SURVEYED ANO TAGGED IN THE FIELD ARE
RECOMMENDED FOR REMOVAL.
I ...... ~ .. ..-"'
tV'32ffiA\( C 10ins. ~-2S ~--Dll1.~c:OIII
CHILORENS INSTITUTE
26~0 Benson Rood S.
Renton WA
TRE( JNl,{Nl0RY Pl.AN
NOTE ,
SEE ARBOR1srs REPORT FOR TREE INVENTORY TABLE ON L 1·2
0 ~50 100
SCALE IN FEET
LEGEND
S HA-1
,Y
---
150
I
"'°" ~,!!!
HAND A UGER NU MBER A ND
APPROXIMA TE LOCATION
APPROXIMA TE LOCA TION OF
GROUNDWATER SEEPAGE
APPROXIMA TE LOCA TIO N OF
S URFACE WATER FLOW
CHILDREN'S INSTITUTE FOR LEARNING DIFERENCES
264-0 Benson Road South
Renton. Washington
SITE AND EXPLORATION PLAN
DATE: March 2()16 Job No. 1601.01
Zipper Geo Assoc/1fH , UC FIGURE
19023 36th Ave. W .. Su,te D 2
Lynnwood, WA SHT.1 ol 1
~ ,nng TREE PREVIOUSLY REMOVED
~TREE#1998
~ TREE TO BE RETAINED
~ TREE TO BE REMOVED
~ CRITICAL AREA BOUNDARY
r---,
L __ _J
Wf?d~ ~gr~
15' CRITICAL AREA BUFFER SETBACK
AREA TO BE CLEARED
FUTURE BUILDING SITE
E) TREE INVENTORY PLAN
SCALE: 1" -50'
THE REPORT INCLUDED A GENERAL PLAN AND TREE INVENTORY, WHICH
DOCUMENTED THE HAZARD TREE SIZE, SPECIES, CONDITION, RISK RATING,
AND RECOMMENDED ACTION. THE TREES HAVE BEEN IDENTIFIED ON SITE
AND TAGGED BY NUMBER WHICH CORRESPONDS WITH THE TREE
INVENTORY.
ALL TREES THAT THE ARBORIST SURVEYED AND TAGGED IN THE FIELD ARE
RECOMMENDED FOR REMOVAL.
1,-Dm-k
1m.J :.lll Ml:IIE
Eml.t .. 11115 , .........
_ Mh' 1111• SCID
CHILDRENS lNSlTTUTE
2640 Benson Rood S.
Renton1 WA
TREE INVENTORY PLAN
EXIS~NG BUii.DiNG
NDll.39' Hf.
FiRST l'UI. D.£V, 4\J.8'
BSIIT. Fl.It. EllV. '403.&'
NOTE:
)
SEE ARBORIST'S REPORT FOR TREE INVENTORY TABLE ON L 1-2
0 50 100
SCALE IN FEET
150
""l
,1]12-ff-1~--
-1 -
,._
·201311
LI.I
~
,,
I
i
I
N N N . . .
f • • • • i i
I I
APPENDIX A
FIELD EXPLORATION PROCEDURES AND LOGS
FIELD EXPLORATION PROCEDURES
Field Exploration Description
Our field exploration for this project included four hand auger explorations completed on March
16, 2016. The approximate exploration locations are presented on the enclosed Site and
Exploration Plan, Figure 2. Exploration locations were determined in the field by measuring
distances from existing site features with a fiberglass tape relative to a 23 January 2014 Tree
Inventory Plan prepared by Integrated Site Design. The vertical datum is not known. Ground surface
elevations at the explorations interpolated from topographic lines presented on the referend plan.
As such, the exploration locations and elevations should be considered accurate only to the
degree implied by the means and methods to establish them. The following sections describe
our procedures associated with the explorations. Descriptive logs of the explorations are
enclosed in this appendix.
Hand Auger Procedures
An engineering geologist from our firm advanced a 3.5-inch diameter auger by hand, continuously
observing the soil cuttings as they were retrieved. Representative portions of the soils retrieved
were placed in moisture tight containers and returned to our laboratory for further visual
classification and testing.
The enclosed hand auger logs indicate the vertical sequence of soils and materials encountered
in each exploration, based primarily on our field classifications and supported by our subsequent
laboratory testing. Where a soil contact was observed to be gradational or undulating, our logs
indicate the average contact depth. Our logs also indicate the approximate depths of any sidewall
caving or groundwater seepage observed in the explorations, as well as all sample numbers and
sampling locations.
71 PPER GEO ASSOCIATF-LLC
19023 36m Avenue West, Suite D, Lynnwood. Washin 8036
HAND AUGER HA-I
Project: Children's Institute
Location: See Site And Exploration Plan, Figure 2 Project No: 1601.01
Approximate Ground Elevation: 382 Feet Date Excavated: 03-16-2016
Depth Material Description Sample Ne %M Testing
(ft)
Loose, moist to wet, dark brown, silty SAND, with roots and fine
organic material (Topsoil) _________________________________
1 Loose to mediwn dense, moist grading to wet, mottled brown, silty
SAND, some gravel, moderate iron oxide staining
(Weathered Glacial Till) S-1@1.5'
2
-----------------------------------------------------
3 Dense, moist, gray to gray-brown, silty SAND, some gravel, slight
iron oxide staining (Glacial Till)
Hand Auger completed at 3.3 feet on 3/16/20 l 6.
4 No groundwater seepage observed at time of exploration.
No caving observed.
5
6
7
8
9
10
11
12
Note: Ne is the Dynamic Cone Penctrometer blow count per ASTM
Special Publication #399.
HAND AUGER HA-2
Project: Children's Institute
Location: See Site And Exploration Plan, Figure 2 Project No: 1601.01
Approximate Ground Elevation; 366 Feet Date Excavated: 03-16-2016
Depth Material Description Sample Ne %M Testing
(ft)
Loose, moist to wet, dark brown, silty SAND, with roots and fine
organic material (Topsoil)
1 ~-----------------------------------------------------
Loose to medium dense, moist to wet, mottled gray-brown, silty
SAND, some gravel, moderate iron oxide staining
2 (Weathered Glacial Till)
3 -----------------------------------------------------
Dense, moist, gray, silty SAND, some gravel (Glacial Till)
4 Hand Auger completed at 3.5 feet on 3/16/2016.
Very slight perched groundwater seepage observed at 3 feet at time
of exploration.
No caving observed.
5
6
7
8
9
10
11
12
Note: Ne is the Dynamic Cone Penetrometer blow count per ASTM
Special Publication #399.
71 PPER GEO ASSOCIAT,-, LLC
19023 3611,. Avenue West, Suite D, Lynnwood, Washin 8036
HAND AUGER HA-3
Project: Children's Institute
Location: See Site And Exploration Plan, Figure 2 Project No: 1601.01
Approximate Ground Elevation: 3 7 4 Feet Date Excavated: 03-16-2016
Depth Material Description Sample Ne 0/oM Testing
(ft)
Loose, moist to wet, dark brown, silty SAND, with roots and fine
organic material (Topsoil)
I -----------------------------------------------------
Mediwn dense, moist, gray-brown SAND, some silt and gravel
(Weathered Glacial Outwash)
S-1@1.5'
2
3
4 Hand Auger completed at 3.5 feet on 3/16/2016.
No groundwater seepage observed at time of exploration.
Slight caving observed below 12 inches.
5
6
7
8
9
10
11
12
Note: Ne is the Dynamic Cone Peoetromcter blow count per ASTM
Special Publication #399.
ZIPPr-GEO ASSOCIATES, LL""
19023 .venue West, Suite D, Lynnwood. Washington 98036
HAND AUGER HA-4
Project: Children's Institute
Location: See Site And Exploration Plan, Figure 2 Project No: 1601.01
Approximate Ground Elevation: 398 Feet Date Excavated: 03-16-2016
Depth Material Description Sample Ne o/eM Testing
(ft)
Loose, moist to wet, dark brown, silty SAND, with roots and fine
organic material (Topsoil)
1 -----------------------------------------------------
Medium dense, moist, gray-brown, fine to medium SAND, some silt
(Weathered Glacial Outwash)
2
S-1@2'
3
4
5
6
Hand Auger completed at 6 feet on 3/16/2016.
7
No groundwater seepage observed at time of exploration.
No caving observed.
8
9
10
11
12
Note: Ne is the Dynamic Cone Penetrometer blow count per ASTM
Special Publication #399.
•
GEOTECHNICAL EVALUATION OF HAZARD
TREE REMOVAL PLAN
Children's Institute for Learning Differences
2640 Benson Road South
Renton, Washington
Project No. 1601.01
March 25, 2016
Prepared for:
Children's Institute for Learning Differences
Prepared by:
ZGA
Zipper Geo Associates, LLC
Geotechnical and Environmental Consultants
19023 36 1h Avenue West, Suite D
Lynnwood, WA 98036
Zipper Geo Associates. LLC
Geotechnical and Environmental Consulting
Children's Institute for Learning Differences
2640 Benson Road South
Renton, Washington 98055
Attention: Ms. Carrie Fannin
Project Number 1601.01
March 25, 2016
Subject: Geotechnical Evaluation of Hazard Tree Removal Plan
Children's Institute for Learning Differences
2640 Benson Road South
Renton, Washington 98055
Dear Ms. Fannin,
In accordance with your request and written authorization, Zipper Geo Associates, LLC (ZGA)
has completed the subsurface exploration and geotechnical evaluation of the Hazard Tree
Removal Plan prepared by others for the Children's Institute for Learning Differences (CHILD)
campus located at 2640 Benson Road South in Renton, Washington. This report presents the
findings of our site reconnaissance and subsurface exploration, and our geotechnical
recommendations for the project. Our work was completed in general accordance with our
Proposal for Geotechnica/ Engineering Services (Proposal No. P16151) dated March 4, 2016.
We appreciate the opportunity to be of service to you on this project. If you have any questions
concerning this report, or if we may be of further service, please contact us.
Sincerely,
Zipper Geo Associates LLC
James P. Georgis, L.E.G.
Principal
Copies: Addressee (1)
Ray Robinson with Integrated Site Design, Inc. (1)
19023 36th Avenue West, Suite D Lynnwood, WA 98036
Thomas A. Jones, P.E.
Principal
(425) 582-9928
•
TABLE OF CONTENTS
INTRODUCTION ....................................................................................................................... 1
SITE DESCRIPTION .................................................................................................................. 1
PROJECT UNDERSTANDING .................................................................................................. 1
SITE RECONNAISSANCE ......................................................................................................... 2
Southeast Tree Removal Area ............................................................................................... 2
Northeast Tree Removal Area ................................................................................................ 3
Northwest Tree Removal Area ............................................................................................... 4
Central Playground Slope Tree Removal Area ....................................................................... 4
SUBSURFACE CONDITIONS ................................................................................................... 4
Published Geologic Mapping .................................................................................................. 4
Soil Conditions ....................................................................................................................... 5
Groundwater Conditions ......................................................................................................... 6
Historic Coal Mine Maps ......................................................................................................... 6
CONCLUSIONS AND RECOMMENDATIONS ........................................................................... 7
General .................................................................................................................................. 7
Geologic Hazard ECA Considerations .................................................................................... 7
Tree Stump and Root System Retention ................................................................................ 8
Planting Recommendations .................................................................................................... 9
Temporary Erosion Control Considerations ........................................................................... 10
Retention of Woody Material ................................................................................................. 10
Off-Site Tree Removal Considerations .................................................................................. 10
General Steep Slope Considerations ..................................................................................... 10
CLOSURE ................................................................................................................................ 11
FIGURES PREPARED BY ZGA
Figure 1 -Vicinity Map
Figure 2 -Site and Exploration Plan
FIGURES PREPARED BY OTHERS
Tree Inventory Plan, Sheet L 1.1
Tree Inventory Table, Sheet L 1.2
APPENDICES
Appendix A -Subsurface Exploration Procedures and Logs
GEOTECHNICAL EVALUATION OF HAZARD TREE REMOVAL PLAN
CHILDREN'S INSTITUTE FOR LEARNING DIFFERENCES
2640 BENSON ROAD SOUTH
RENTON, WASHINGTON
Project No. 1601.01
March 25, 2016
INTRODUCTION
This report documents the surface and subsurface conditions encountered at the site and our
geotechnical evaluation of the Hazard Tree Removal Plan prepared by others for the Children's
Institute for Leaming Differences (CHILD) campus located at 2640 Benson Road South in Renton,
Washington. The project description, site conditions, and our geotechnical conclusions and
recommendations are presented in the text of this report. Supporting data including detailed
exploration logs, field exploration procedures, and other supporting information are presented as
appendices.
Our geotechnical scope of services for the project included a document review, site
reconnaissance, subsurface evaluation, geotechnical analysis, and preparation of this report. The
subsurface evaluation consisted of completing four hand auger explorations (designated HA-1
through HA-4) located near proposed tree removal areas and steep slopes. The hand auger
explorations extended approximately 3Y. to 6 feet below the existing ground surface.
SITE DESCRIPTION
The site is located at 2640 Benson Road South in Renton, Washington. The CHILD facility is
located in the south-central portion of the site and includes campus buildings and a perimeter
access drive with a parking lot on the east side of the facility. The northern portion of the site is
undeveloped and includes mixed evergreen and deciduous trees with a moderately well-
developed understory of brush and groundcover. The site is bounded to the north by a multi-
family residential development, to the south by South 27'" Street, to the east Benson Road South,
and to the west by a middle school. The approximate site location is shown on the enclosed
Vicinity Map, Figure 1. Existing site features, site topography, and nearby features are shown on
the enclosed Site and Exploration Plan, Figure 2.
PROJECT UNDERSTANDING
The site is mapped by the City of Renton as containing Coal Mine Hazard, Steep Slope Hazard,
and Landslide Hazard Environmental Critical Areas (ECAs). We understand that the City has
requested a geotechnical evaluation of the Hazard Tree Removal Plan be completed to assess
the risk to regulated Geologic Hazard ECAs and their associated buffers, as defined in Part 4-3-
050-G-5 of the City of Renton Municipal Code (RMC) that may result from the planned tree
removal and provide recommendations to mitigate identified risks. Our understanding of the
project is primarily based on a review of the following documents and discussions with Integrated
Site Design and representatives for CHILD.
Zipper Geo Associates. LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
• Tree Risk Assessment, CHILD, 2640 Benson Road South, Renton, Washington, prepared
by Greenforest Incorporated Consulting Arborist, dated December 2, 2015.
• Children's Institute, 2640 Benson Road South, Renton WA, Tree Inventory Plan, Sheet
L 1.1, prepared by Integrated Site Design, dated March 24, 2016.
• Children's Institute, 2640 Benson Road South, Renton WA, Tree Inventory Table, Sheet
L 1.2, prepared by Integrated Site Design, dated March 24, 2016.
Based on our review of the referenced documents, it appears that the hazard tree removal plan
includes the pruning and removal of trees located within the CHILD property, and to a lesser
extent, the removal of trees from the adjacent property to the east. A summary of the planned
tree removal is presented below.
On-Site Hazard Tree Removal: The plan identifies fifty-two trees on the site that have been rated
by Greenforest Incorporated as having a moderate to high risk rating. Fifty of these trees are listed
for removal and two are listed for pruning or deadwood removal. Of the fifty-two identified trees,
forty-six trees are maple, five trees are cottonwood, and one tree is alpine fir. About thirty six of
the fifty-two trees are located within ECA areas or their buffers as shown on Plan Sheet L 1.1
Off-Site Hazard Tree Removal: The plan identifies eleven trees east of the mapped site property
line that have been rated by Greenforest Incorporated as having a moderate to high risk rating
and listed for removal. Off the eleven identified trees, two trees are maple, eight trees are willow,
and one tree is cherry. About ten of the eleven trees are located within ECA areas or their buffers
as shown on Plan Sheet L 1.1
Copies of the Tree Inventory Plan and Tree Inventory Table (Plan Sheets L 1.1 and 1.2) are
enclosed with this report without modification to assist in report interpretation.
SITE RECONNAISSANCE
We completed a reconnaissance of the property and immediate vicinity during a site visit
completed on March 16, 2016. The purpose of the reconnaissance was to identify surficial features
of site conditions such as the presence or absence of groundwater seepage, the presence or
absence of surface erosion, indications of past slope instability, indications of past land use, the
type and extent of existing vegetation, the location of trees identified for removal, and other site
features that may be affected by the planned tree removal. The enclosed Site and Exploration
Plan, Figure 2, shows the approximate location of some of the observed site features. A summary
of our site observations is presented below.
Southeast Tree Removal Area
About 10 trees are listed for removal in this area. The trees are located within a west-facing, off-
site slope that extends down to a relatively new rockery wall constructed just within the property
Page2
Zipper Geo Associates. LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
line. Based on the topographic site plan, the slope inclination above the rockery ranges from about
23 to 44 percent (13 to 23 degrees). The rockery appears to be in good condition, ranges from
about 4 to 6 feet tall, includes a drainage zone of quarry spall backfill, and appears to include a
perforated drain pipe. In addition to the listed trees, slope vegetation includes dense Laurel
bushes, blackberry, fern, ivy, blue star creeper, and grasses. We did not observe any obvious
indications of past slope movement or distress. Surficial erosion was slight and limited to several
foot paths. We did not observe any obvious indications of groundwater seepage from the exposed
slope surface. However, the rockery drain pipe daylights at the north end of the wall and we
observed about Y. to 1 gpm discharge from this pipe at the time of our site visit. The discharge
flowed down a roadside ditch to a dispersion area in the northwest portion of the site. The
approximate rockery groundwater discharge location and subsequent down-gradient surface
water flow is shown on Figure 2.
Northeast Tree Removal Area
For the purposes of this report, the northeast tree removal area includes the central steep slope
area located in the northern portion of the site and the gently sloping bench located between the
central steep slope area and the east property line.
The north-central, west-facing slope has inclinations ranging from about 23 to 44 percent (13 to
23 degrees). In addition to the trees listed for removal, slope vegetation includes mixed evergreen
and deciduous trees which were considered by the arborist to be of low risk and are not listed for
removal, blackberry, fern, ivy, and grasses. Areas between vegetation were typically mantled by
several inches of forest duff. We did not observe any obvious indications of past slope movement
or distress. Surficial erosion was slight and limited to several foot paths. We did not observe any
obvious indications of groundwater seepage from the exposed slope surface. We observed what
appears to be a lobe of fill soils extending into the slope area from the eastern bench area. The
fill appeared to be relatively old and may have been associating with mass grading for the CHILD
development. The approximate location of the fill is shown on Figure 2.
The bench area located between the north-central steep slope and the east property line slopes
gently west with inclinations ranging from about 5 to 12 percent (3 to 8 degrees). We estimate
that about 60 to 70 percent on the bench is surfaced with wood chips. The remainder of the area
consists of soil with scattered ferns and grass. We did not observe any obvious indications of
past slope movement or distress associate with the bench or adjacent slopes. Surficial erosion
was slight and limited to several foot paths. We observed slight surface water flow in the northern
portion of the bench area. The flow appeared to be originating from a spring located near the top
of the steep off-site slope which extends up to the adjacent middle school play field. We visually
estimated a flow rate on the order of Y. gallon per minute at the time of our evaluation. The spring
had incised a small drainage feature about two feet wide and one foot deep into the surface of
the off-site slope. Surface water from the spring was infiltrating into the bench soils at the time of
our evaluation and was not running down the north-central steep slope. The approximate location
of the spring and down-gradient surface water flow is shown on Figure 2
Page 3
Zipper Geo Associates. LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
Northwest Tree Removal Area
For the purposed of this report, the northwest tree removal area includes the north-central gently
sloping bench area located in the northern portion of the site and the steep slope area located
between the north-central gently sloping bench area and the west property line.
The north-central bench area slopes gently west with inclinations ranging from about 1 O to 17
percent (6 to 10 degrees). In addition to the trees listed for removal, vegetation includes mixed
evergreen and deciduous trees which were considered by the arborist to be of low risk and are
not listed for removal, blackberry, fem, ivy, and grasses. Areas between vegetation were typically
mantled by several inches of forest duff. We did not observe any obvious indications of past slope
movement or distress. Surficial erosion was slight and limited to several foot paths. We did not
observe any obvious indications of groundwater seepage.
The west-facing slope located between the north-central bench and the west property line has
typical inclinations ranging from about 30 to 56 percent (17 to 30 degrees). An isolated section
of slope adjacent to the sidewalk has an inclination of about 100 percent (45 degrees) with a
maximum slope height of about 6 feet, and appears to be the result of a cut completed to construct
the sidewalk. In addition to the trees listed for removal, slope vegetation includes mixed evergreen
and deciduous trees which were considered by the arborist to be of low risk and are not listed for
removal, blackberry, fern, ivy, and grasses. Areas between vegetation were typically mantled by
several inches of forest duff. We did not observe any obvious indications of past slope movement
or distress. Surficial erosion was slight and limited to several foot paths. We did not observe any
obvious indications of groundwater seepage, but standing water was present in two drainage
ditches located near the west property line at the time of our evaluation
Central Playground Slope Tree Removal Area
A steep west-facing slope is located near the middle of the site between the playground and the
main parking lot. Slope inclinations range from about 42 to 80 percent (23 to 39 degrees). Slope
vegetation primarily consists of ivy and blackberry brush, with scattered patches of grass in the
southern portions of the slope and several deciduous trees. In general, the trees located on the
slope exhibited pistol-butted growth pattern (bent trunks near the ground surface) which is
indicative of slope creep. We did not observe indications of deep-seated slope movement or
shallow sloughing. Surficial erosion was slight and limited to non-vegetated portions of the slope.
We did not observe any obvious indications of groundwater seepage.
SUBSURFACE CONDITIONS
Published Geologic Mapping
We assessed the geologic setting of the site and surrounding vicinity by reviewing The Geologic
Map of the Renton Quadrangle, King County, Washington, U.S. Geological Survey Map GQ-405,
Page4
Zipper Geo Associates. LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
1965. The geologic map indicates the site and immediate vicinity are mantled by Quaternary
Ground Moraine deposits (091). This deposit is described as thin glacial ablation till over lodgment
till deposited by the Vashon Stade of the Frasier glaciation. The lodgment till is further described
as a compact, unsorted mixture of sand, sill, clay, and gravel, commonly termed "hardpan". The
ablation till is described as being compositionally similar to lodgment till, but much less dense.
Tertiary age Renton Formation deposits are mapped about Y. mile to the northeast of the site.
The Renton formation is described as arkosic sandstone, mudstone, and shale with several beds
of coal. The Renton Formation has an extensive history of surface and subsurface coal mining.
Stratigraphic information presented in the referenced geologic map indicates that Renton
Formation deposits underlie the surficial glacial deposits at an unspecified depth.
Soil Conditions
The subsurface exploration for this project included four hand auger explorations (HA-1 through
HA-4) located near proposed tree removal areas and steep site slopes. The hand auger
explorations extended approximately 3Y. to 6 feet below the existing ground surface. The
approximate exploration locations are shown on the enclosed Site and Exploration Plan, Figure 2.
Soils were visually classified in general accordance with the Unified Soil Classification System.
Detailed, descriptive logs of the subsurface explorations and the procedures utilized in the
subsurface exploration program are presented in Appendix A. Generalized descriptions of
subsurface soil conditions observed at the exploration locations are presented below. The
stratification and horizontal extent of the soil types observed in our explorations may vary between
explorations. Stratification boundaries on the exploration logs represent the approximate depth
of changes in soil types, although the transition between materials may have been gradual.
Please refer to the hand auger logs in Appendix A for a more detailed description of the conditions
encountered at the exploration locations.
Hand augers HA-1 and HA-2 were completed in the northern portion of the site. In general, the
explorations encountered about 7 to 10 inches of loose, organic-rich silty sand interpreted as topsoil.
Below the topsoil, loose to medium dense silty sand with some gravel was encountered to a depth
of about 2Y. lo 3 feet and is interpreted as weathered glacial till. Dense, silty sand with some gravel,
interpreted as unweathered glacial till, was encountered below the weathered horizon and extended
to the total depth explored of 3Y. feet below existing grade.
Hand augers HA-3 and HA-4 were completed in the west-central and central portions of the site,
respectively. These explorations encountered about 12 inches of loose organic-rich silty sand topsoil
over primarily granular deposits interpreted as glacial outwash. In hand auger HA-3, the outwash
consisted of medium dense sand with some gravel and silt which extended to the total depth explored
of 3.5 feet below existing grade. In hand auger HA-4, the oulwash consisted of medium dense fine
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Zipper Geo Associates. LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
to medium sand with some silt which extended to the total depth explored of 6 feet below existing
grade.
Groundwater Conditions
Slight groundwater seepage was observed in hand auger HA-2. Groundwater seepage was not
observed in the other hand auger explorations. The groundwater observed in HA-2 is interpreted
to represent water perched above lower permeability glacial till soils encountered at a depth of 3
feet. Given the relatively low permeability of the glacial till soils encountered in the northern
portion of the site, perched groundwater may develop above the till or within sandy zones within
the till during periods of extended wet weather. Perched groundwater may also develop above
lower permeability layers within the glacial outwash deposits, which are often stratified.
These observations represent groundwater conditions at the time of the field exploration.
Groundwater conditions should be expected to fluctuate due to changes in season, precipitation
patterns, site utilization, on-site or off-site irrigation activities, and other on-and off-site factors.
Historic Coal Mine Maps
As part of our site evaluation, we completed a review of historic coal mine maps available from
the Washington State Department of Natural Resources. Based on our review, it appears that
the site is underlain by portions of the Sunbeam Mine and Renton Mine. A summary of our historic
coal mine map review relative to these mines is presented below.
Sunbeam Mine: The Sunbeam Mine was operated by the Renton Coal Company from 1922 to
1929. The Sunbeam portal (or mine entrance) is mapped about 2/3 of a mile north-northwest of
the CHILD site and has a reported main "water level" gangway elevation of about 68 feet. The
mine chutes appear to have extended up and to the south-southwest of the main gangway (away
from the CHILD site) along a coal seam inclined or dipping to the north-northeast at an angle of
about 65 degrees from horizontal. Based on the mapped data, it appears that the Sunbeam mine
workings are primarily west of the CHILD site, with the eastern end of the mine underlying a
portion of Benson Road South and the southwestern portion of the CH I LD site. Given a site
ground surface elevation of about 400 feet, it appears that those portions of the mine workings
located below or near the CHILD site are on the order of 200 to 300 feet below the ground surface.
The City of Renton has mapped the mine workings west-southwest of the site (west of Benson
Road South) as having a moderate to high risk, and the workings mapped below the CHILD site
as having a moderate risk.
Renton Mine: The Renton Mine was operated by the Seattle Electric Company in 1919 and the
Renton Coal Company from 1920 to 1955. It appears that the Renton Mine 6th Gangway South
and associated workings extended below the CHILD site. The historic maps do not include explicit
information regarding the elevation of the workings in this area. However, the workings appear to
be an extension of the generally north-northeast dipping coal seam worked in the Sunbeam Mine.
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Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
Based on the elevation of the Sunbeam main water level gangway and the indicated strata dip
angle and orientation, it appears that the Renton Mine workings in the vicinity of the site are likely
greater than 300 feet below the ground surface. The City of Renton has mapped the Renton Mine
workings at the project site and nearby vicinity as having a moderate risk.
CONCLUSIONS AND RECOMMENDATIONS
General
Based on the results of our site reconnaissance, document review, subsurface exploration, and
geotechnical analysis, it is our opinion that the proposed tree removal plan is feasible from a
geotechnical perspective. Provided that the conditions and recommendations contained within this
report and the provisions of the Renton Municipal Code (RMC) are satisfied, it is our opinion that
the proposed Hazard Tree Removal Plan will not increase the potential for soil movement and the
risk of damage to existing structures, the site, and to adjacent properties from soil instability will
not be increased. The following sections provide a discussion regarding City of Renton regulated
ECAs and recommendations to reduce risks associated with the tree removal plan.
Geologlc Hazard ECA Considerations
The site is mapped by the City of Renton as containing Coal Mine Hazard, Steep Slope Hazard,
and Landslide Hazard Environmental Critical Areas (ECAs). We understand that the City has
requested a geotechnical evaluation of the Hazard Tree Removal Plan to assess the risk to
regulated Geologic Hazard ECAs and their associated buffers, as defined in Part 4-3-050-G-5 of
the City of Renton Municipal Code (RMC) that may result from the planned tree removal and
provide recommendations to mitigate identified risks.
Part 4-3-050-C-3 of the RMC indicates that the removal of dangerous trees which have been
approved by the City and certified dangerous by a licensed landscape architect or certified arborist
is exempt from RMC ECA restrictions and may be permitted by the City. The following sections
present our evaluation of Coal Mine Hazard, Steep Slope Hazard, and Landslide Hazard ECA's
relative to the Hazard Tree Removal Plan.
Coal Mine Hazard Areas: Coal Mine Hazard Areas include areas with known subsurface coal mine
workings. The site is mapped within a Medium Coal Mine Hazard Risk Area and slightly northeast
of a High Coal Mine Hazard Risk Area. Our review of historic coal mine maps for the site vicinity
(Renton Mine and Sunbeam Mine) indicate mine workings depths in excess of 200 feet. Based on
our document review and site observations, it is our opinion that the site are consistent with the
criteria for a Medium Coal Mine Hazard Risk Area.
Steep Slope Hazard Areas: The City of Renton maps portions of the site as Steep Slope Hazard
Areas. The City mapped hazard areas are primarily located along the eastern property line, within
the northern, undeveloped, wooded portion of the site, and the slope area between the main school
building and the playground area. The enclosed Tree Inventory Plan, Sheet L 1.1 identifies Steep
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Zipper Geo Associates, LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
Slope Hazard Areas and an associated 15 foot wide buffer based on site topography. Based on
our document review and site reconnaissance, it is our opinion that the critical areas and associated
buffers presented on Sheet L 1.1 are in general accordance with RMC Steep Slope Hazard Area
criteria.
Landslide Hazard Areas: The City of Renton ECA maps generally identify the central and western
portions of the northern, undeveloped, wooded area and the slope between the playground and the
school facility as High Landslide Hazard Areas, although the City mapped hazard areas to not
appear to correlate well to the site specific topography presented on Sheet L 1.1. This may be due
to the City's use of a more regional topographic database to identify hazard area. The RMC defines
a high landslide hazard area as an area with slopes greater than 40 percent, and areas with slopes
between fifteen and forty percent and underlain by soils consisting largely of silt and clay. Based on
our document review and subsurface explorations, it is our opinion that site slopes exceeding forty
percent are consistent with the RMC criteria for Landslide Hazard Areas. These areas are generally
identified on the Tree Inventory Plan, sheet 1.1.
Risk Evaluation Summary: Based on mapped mine working depths in excess of 200 feet below
existing grade, it is our opinion that the Hazard Tree Removal Plan will have no measurable adverse
impact on the Coal Mine Hazard and will not increase the risk of coal mine induced damage to the
subject site or adjacent properties. Provided that the conditions and recommendations contained
within this report and the provisions of the Renton Municipal Code (RMC) are satisfied, it is our
opinion that the proposed Hazard Tree Removal Plan will not increase the potential for soil
movement and the risk of damage to existing structures, the site, and to adjacent properties from
soil instability will not be increased.
Tree Stump and Root System Retention
Tree root systems provide erosion protection and bio-reinforcement for slope soils, thereby
increasing the strength of the soil mass and reducing the risk of slope instability. However, the
weight of the tree can increase the forces tending to drive slope instability and the rocking action
of the root mass during high winds can result in loosening of the slope soils, resulting in a
reduction in slope stability, particularly for large, heavy trees located on or near the crest of steep
slopes. There is some debate in the scientific community regarding the relative contributions of
these different factors to slope stability, but the general consensus appears to be that under most
conditions the presence of trees (in particular the bio-reinforcement they provide) results in a net
improvement to slope stability.
Based on our review of the Tree Inventory Table, it appears that about 61 of the 63 trees listed
for removal or pruning consist of cottonwood, maple, or willow. These tree species often survive
cutting by generating new growth from the stump, often referred to as stump sprouting. Stump
sprouts provide nourishment for maintenance of the root system while greatly reducing the
negative impact of tree weight and wind driven soil loosening. We therefore recommend that the
trees planned for removal be cut off near the ground surface and that the stumps and root masses
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Zipper Geo Associates, LLC
Children's Institute for Leaming Differences
Project No. 1601.01
March 25, 2016
be left In place within the Steep Slope Hazard Areas and associated buffers identified on Sheet
L 1.1. We anticipate that there may be some benefit to potential utilization of the site by removing
stumps from the gently sloping bench areas located in the northern portion of the site. In our
opinion, the removal of stumps within the bench areas is feasible from a geotechnical perspective
without adversely affecting the site slopes. An 8-inch diameter alpine fir (tree #4) is listed for
removal from a grass lawn area near the perimeter access drive. In our opinion, the stump of this
tree may also be removed to facilitate landscape maintenance without adversely affecting the site
slopes.
Planting Recommendations
Some portion of the cut trees may not develop stump sprouts or may not receive adequate
nutrients from the sprouts to prevent decay of the root mass over time. Based on our evaluation
of the site conditions, it is our opinion that the decay of the root systems associated with trees 1
through 3 located near the top of the steep central slope adjacent to the playground could result
in a reduction in the stability of the slope near the removed trees relative to shallow surficial sliding.
In our experience, it typically takes about 3 to 5 years to realize a significant reduction in the bio-
reinforcement provided by a tree that does not survive cutting.
As a precautionary measure, we recommend that the Hazard Tree Removal Plan include new
plantings near trees 1 through 3. We recommend that native woody shrubs or small trees be
considered to reduce the need for watering and keep the weight and wind loading characteristics
of the new growth to reasonable levels as it matures. The following table provides some plant
species that could be considered to reduce the potential for erosion and increase resistance to
shallow surficial sloughing. The information presented below is a relatively small sampling of plant
species discussed in the 1993 publication Slope Stabilization and Erosion Control using
Vegetation, produced by the Washington State Department of Ecology (Publication 93-30). The
table below is by no means intended to be comprehensive or restrictive relative to the selection
of appropriate plantings.
POTENTIAL PLANT SELECTION GUIDE
Plant Name Form&Habit Mature Rooting Recommended
Size Characteristics Spacing
Snowberry Evergreen shrub; Height: 4' Fibrous,
(Symphoricarpos Albus) spreads by runners to Spread: 3' Shallow depth. 2'+
form thicket
Salal Evergreen shrub; Height: 3' Fibrous,
(Gaultheria Sha/Ion) spreads by runners to Spread: 3' Shallow depth. 2'+
form thicket
Evergreen Huckleberry Evergreen shrub; does Height: 6' Fibrous, 3'+ Oemleria Cerasiformis) not spread Spread: 3' Shallow depth.
Ocean Spray Deciduous shrub; does Height: 10'+ Fibrous,
(Holodiscus Discolor) not always spread Spread: 6' Moderate depth. 4'+
annressivelv
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Zipper Geo Associates. LLC
Children's Institute for Learning Differences
Project No. 1601.01
March 25, 2016
Vine Maple Deciduous shrub; does
(Acer Circinatum) not always spread
annressivelv
Hooker Willow Deciduous shrub; does
/Salix Hookerianal not soread
Height: 15'+ Fibrous,
Spread; 10' Moderate depth. 8'+
Height: 20'+ Fibrous, 3'+ Soread: 15' Moderate deoth.
Reference: Slope Stabilization and Erosion Control using Vegetation, Washington State Department of
Ecolonu Publication 93-30, 1993.
Temporary Erosion Control Considerations
We anticipate that the tree removal process will likely result in disturbance of the ground surface
and a temporary increase in the potential for erosion. We therefore recommend that the tree
removal service utilize means and methods intended to minimize ground disturbance. In addition,
we recommend that soils exposed within Steep Slope Hazard Areas and their buffers be covered
with a temporary erosion control material, such as sterile straw or arborist mulch.
Retention of Woody Material
In our opinion it appears geotechnically feasible to retain much of the woody debris generated
from the hazard tree removal as habitat enhancement within wooded portions of the site.
However, based on our evaluation, we recommend that woody material greater than 6-inches in
diameter be removed from the following areas as the weight of the material could adversely affect
steep slopes or the performance of existing drainage features.
• The drainage features near Benson Road South and adjacent sleep slopes identified on
Figure 2.
• The steep slope located between the playground and the school facility and the 15-foot
wide buffer above this steep slope area.
Off-Site Tree Removal Considerations
The Hazard Tree Removal Plan appears to include the removal of 11 trees located beyond (east
of) the subject property. We recommend that all agreements and/or permits that may be needed
to complete off site work be coordinated with the adjacent property owner and the City before
beginning work.
General Steep Slope Considerations
Owners of properties containing or adjacent to steep slopes should recognize that soil loss or
downslope displacement from steep slopes is a naturally occurring mass wasting process, and
that some soil loss from steep slopes should be expected over time, particularly in response to
episodic severe storm events. The conclusions and recommendations presented in this report are
intended to allow for the removal of hazard trees while maintaining the existing stability of the site
slopes. The findings presented in this report should not be interpreted as indicating that the site
steep slopes will be stable under all possible future conditions.
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Zipper Geo Associates. LLC
Children's Institute for Leaming Differences
Project No. 1601.01
March 25, 2016
CLOSURE
The analysis and recommendations presented in this report are based, in part, on the explorations
completed for this study. The number, location, and depth of the explorations were completed
within the constraints of budget and site access so as to yield the infonnation to formulate our
recommendations.
This report has been prepared for the exclusive use of The Children's Institute for Learning
Differences, Integrated Site Design, and their agents, for specific application to this project and
has been prepared in accordance with generally accepted geotechnical engineering practices.
No warranties, express or implied, are intended or made. Site safety is the responsibility of others.
In the event that changes in the nature, design, or location of the tree removal as outlined in this
report are planned, the conclusions and recommendations contained in this report shall not be
considered valid unless Zipper Geo Associates, LLC reviews the changes and either verifies or
modifies the conclusions of this report in writing.
Page 11
REFERENCE: GOOGLE EARTH 2016. NOT TO SCALE
CH ILDREN'S INSTITUTE FOR LEARN ING DIFFERENCES
2640 Benson Road South
Renton , Washington
1----------~
VICINITY MAP
DATE: March 2016 Job No . 1601.0 1
Zipper Geo Associates, LLC FIGURE 1 19023 36th Ave. W.,Suite D
Lynnwood, WA SH T. 1 of 1
J e-_
,,-CROUNOWATER SEEPAGE
_, NEAR FENCE LINE --
W •=• TREE PREYIOUSL Y REMOVED
~TREEi/1998
~ TREE TO BE RETAINED
®ii~· TREE TO BE REMOVED
D CRITICAL AREA B OUNDARY
,-----i
L __ _J 15' CRITICAL AREA BUFFER SETBACK
AREA TO BE CLEARED
FUTURE BUILDING SITE
TREE INVENTORY PLAN
SCALE: 1" ~ 50'
,-"
2015.
THE REPORT INCLUDED A GENERAL Pl.AN A.ND TREE INVENTORY. WHICH
DOCUMENTED THE HAZARD TREE SIZE. SPECIES. CONDITION. RISK RAT ING.
AND RECOMMENDED ACTION THE TREES HAVE BEEN IDENTIFIED ON SITE
ANO TAGGED BY NUMBER WHICH CORRESPONDS WITH THE TREE
INVENTORY
ALL TREES THAT THE ARSORIST SURVEYED ANO T AGGEO IN THE FIELD ARE
RECOMMENDED FOR REMOVAL
I ._ .... .._ ..
tOOJfllA'CIC
3UrU••1S
",,,.,.,_ 8'UC91191ia~HJXW
CHILDRENS INSTITUTE
2640 Benson Rood S.
Renton, WA
TRE( IH'-'tNTORT PL.AN
t'
.. ,~....__-' , .... • f ~:-;·
NOTE:
SEE ARBORISTS REPORT FOR TREE INVENTORY TABLE ON L 1-2
0 ~50 100
SCALE IN FEET
LEGEND
S HA-1
,-·
150
I
" ....
.!!:,Jll
HAND AUGER NUMBER AND
APPROXIMATE LOCATION
APPROXIMATE LOCATION OF
GROUNDWATER SEEPAGE
APPROXIMATE LOCATION OF
SURFACE WATER FL OW
CtillDREN'S INSTITUTE FOO LEARNING OlFERENCES
:IB40 Benson Road Sooth
__ Reotoo. Washington
SITE AND EXPLORATION PLAN
DATE Mardi 2016 Job No. 1601.01 z:=~:1::0~·.·;i~;tc FIGURE 2
Lynnwood. WA SHT 1 of 1
~ ,--L. . •--:::C·~~\?,o•."•,,, •.
_TREE INVENTORY LEGEND -~~~ .
~ TREE PREVIOUSLY REMOVED -'t-\S~)' I ~--:,
TREE#1998 • ''} .1\ \ (/1..__
7
r---~ TREETOBERETAINEO ~i,...Jf__L \ '~~~--..,_-:="-'*~'
~-TREE TO BE REMOVED
CRITICAL AREA BOUNDARY
~~::;.~\~ \4. -"1-4-~~ ~ ~~::~\--~
THE TREES ON THIS PLAN SHOWN AS TO BE REMOVED ARE BASED ON AN ~
ARBOREAL ASSESSMENT REPORT PREPARED BY GREENFOREST
CONSUL TING ARBORISTS FOR THE CHILD INSTITUTE DATED DECEMBER 2,
2015.
THE REPORT INCLUDED A GENERAL PLAN AND TREE INVENTORY, WHICH NOTE:
DOCUMENTED THE HAZARD TREE SIZE, SPECIES, CONDITION, RISK RATING, SEEARBORIST'S REPORT FOR TREE INVENTORY TABLE ON L 1-2
ANO RECOMMENDED ACTION. THE TREES HAVE BEEN IDENTIFIED ON SITE
15' CRITICAL AREA BUFFER SETBACK
AREA TO BE CLEARED
FUTURE BUILDING SITE
E) Jc~~E,..'~~f.NTORY PLAN
AND TAGGED BY NUMBER WHICH CORRESPONDS WITH THE TREE
INVENTORY O 50 100
All TREES THAT THEARBORIST SURVEYED AND TAGGED IN THE FIELD ARE
RECOMMENDED FOR REMOVAL.
1-~n-,~ CHILDRENS INSTITUTE
1:ma .... •'j[ 111: 2640 Benson Road S.
iunr. • NUS Rentan, WA , .......
·-~~··, ~.._H.all lREE INVENTORY PLAN
SCALE IN FEET
150
_,,..,,,.,,1--
--
" ...
·2ou11 ..
Ll.1
Greenforest @ Registered Consulting Arborist
C:.rrle hnr*I.~ Dlred!N"•OIILD
RE: Trtt Risk i1messn1ent _,...,
Pap,9o'12
Att.chmtn1 No. -4 Tree~
T-.... . .. llemrili,,1111:111111
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' " -""'"" ......... ,~ ...... ...
' , .. , ---,;,rmufti -" ......... " • -• w= --..._ ...
" • • ""' --......... • • " , ..... ...... ... .._ ... ., " ........ ....... .........
Doublo, ..... lndulled
s .... -.... •• · or ·-· • IIN!m1 . ..... ... " • ----~tree
~deadl&" n ., ~dleltatk n -~ ...........
..._L ~-----SI ··ormultl..i.stams --"'m _,ll ~,10 ~---w ---'--1-• incksln1nml< orffl\lRl•lffl'l'ls " --.. • ""' ----• 512: 5 crxlcslntnnl or multi .... st.ms " ......... " • ""' --...........
• cno:b rn tNlll w-.. ~ ---" " • ---·----" .. •• ~-~_lnuunk .... .... " ......... " • Mr" ----~ --n """" .. 01ldailnw il!ormuit;:.--::-stllffll·-" ---.. 1411uo • -or mull!·"" stems -.. _ ...
12 '411& -·· u, ..... " ........... .. .. ,, • w-1 ---~ ~---u IU&-}4 ... -· wm• ·-" ........... .. u -USt.ii--·--~ --" .... • wm, ..~ " --.. DKay.~falh .....
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~ " .. ~ ·---·-,----" u -.. --" Relll-tl'M
GModtmll lilnpl Cllfb, .. .. ... --.........
d«ay, pre/lolls Wure. .. ,. .. c.-blntrllnk --...... ..
" " ...... -........ ·-. ........ ~--1818-10 .. , .. ormu~stitna --
•u
Smd stem dnd, top af Prullelltll'1!ffl0d .. ' Cl'lckslntnm s w -..........
" --$1·-'· orm-~e mm, ·-6"stem1nd " '"" "'"" l'ffll!oosfallu111 ,w -' ......... .. 1" 16 M --ormultl..a..~, " ---T-·-... necoo,w,.-lded ... "'" .. --'-1: Most ••-k,to Fall --"""' ... .-,_ ,_ ... ..,.--~ ll«Q1¥ikiMkd ............... .... ... --"''" ""'"
u ,,110-1• ····'· -~-SI 'ormu-· · ffi!ffl5 . ......... .. ,•10-1• ... -.. m•• -""" .._ ... --· Crad.s In trwnk, decay, ---" 10,U,14 ... --M -··orm-···-..........
" . " ... -SI · or mufti-'-sterru ,.~ .. _ ... Cl'te:b ln In.ink, decl!V,
$twnp$l)rtlllt.deay, " . ,. . .. -_Sl!P or mu_. stems -. .. _ ... ---... cncb In trunl<. ck-e,y, ·-"' •••u ·-· -Sl""leormultl""'itl!ITIS ·---" W.12" ...... 51--·-ormu~·-~ .. _ ... --· ··--·· OKbln trunk, dKl,y,
51-~-Of----·~ sterm ·-. -.-" "" ,anu .... d«lne --" .... • ........ ·~~-..-mulll""'!!tl!ms ,-.. _ .... " s• 10-u -w -........ --Stumpi;prout,. decay, " • ------........ .......... -·-_!' "' ------· .__tf!!_
" . ,, • ·-··--·-ounultl"'t! stems ·-. ......... " ... -• or mull: •= .... .... .. _ .... ---" ,. WT""' ' w ·--..........
..... --" u, ..... ' mm --.. _ ...
" 1.;1·~ 12 -1 ••· luwmultl"""sttms ,-......... --· --· "' '''6-14 .. -,.._ SI ·ormu-···mms ,--·-... --'-· . " IS 6-14 .... _ ... _
' w--....... .........
" '"' 10-U -ormu ··---" ... .,., .... .......,,., ' wm, -........ ..........
... -·-" ... ,. ..... Pl'Nllusflillure ' M--·-· --" uu I=, 1-· • ormu"'•lestems. --.. _ ... I
"'"'""""' " 14114 M ,. -· SI -··ormulll"'"'stam' ··-.. _ ... " •.
CHILDRENS INSTilUTE 1 1:1-1 --201lll 1-w-~ 100-IMII 2640 Benson Rood S.
:Dn.t. •mm Renton WA Ll.2 ........ .. .-..... TREE lN'IENTOR'i' TA81...E --. ---~-
APPENDIX A
FIELD EXPLORATION PROCEDURES AND LOGS
FIELD EXPLORATION PROCEDURES
Field Exploration Description
Our field exploration for this project included four hand auger explorations completed on March
16, 2016. The approximate exploration locations are presented on the enclosed Site and
Exploration Plan, Figure 2. Exploration locations were determined in the field by measuring
distances from existing site features with a fiberglass tape relative to a 23 January 2014 Tree
Inventory Plan prepared by Integrated Site Design. The vertical datum is not known. Ground surface
elevations at the explorations interpolated from topographic lines presented on the referend plan.
As such, the exploration locations and elevations should be considered accurate only to the
degree implied by the means and methods to establish them. The following sections describe
our procedures associated with the explorations. Descriptive logs of the explorations are
enclosed in this appendix.
Hand Auger Procedures
An engineering geologist from our firm advanced a 3.5-inch diameter auger by hand, continuously
observing the soil cuttings as they were retrieved. Representative portions of the soils retrieved
were placed in moisture tight containers and returned to our laboratory for further visual
classification and testing.
The enclosed hand auger logs indicate the vertical sequence of soils and materials encountered
in each exploration, based primarily on our field classifications and supported by our subsequent
laboratory testing. Where a soil contact was observed to be gradational or undulating, our logs
indicate the average contact depth. Our logs also indicate the approximate depths of any sidewall
caving or groundwater seepage observed in the explorations, as well as all sample numbers and
sampling locations.
PPER GEO ASSOCIATI , LLC
19023 36& Avenue West, Suite D, Lynnwood., Washington 98036
HAND AUGER HA-1
Project: Children's Institute
Location: See Site And Exploration Plan, Figure 2 Project No: 1601.01
Approximate Ground Elevation: 3 82 Feel Date Excavated: 03-16-2016
Depth Material Description Sample Ne o/oM Testing
(ft)
Loose, moist to wet, dark brown, silty SAND, with roots and fine
organic material (Topsoil) -----------------------------------------------------
I Loose to medium dense, moist grading to wet, mottled brown, silty
SAND, some gravel, moderate iron oxide staining
(Weathered Glacial Till)
S-1@1.5'
2
-----------------------------------------------------
3 Dense, moist, gray to gray-brown, silty SAND, some gravel, slight
iron oxide staining (Glacial Till)
Hand Auger completed at 3.3 feet on 3/16/2016.
4 No groundwater seepage observed at time of exploration.
No caving observed.
5
6
7
8
9
10
II
12
Note: Ne is the Dynamic Cone Penetrometer blow count per ASTM
Special Publication #399.
ZIPPI GEO ASSOCIATES, LL
19023 36-Avenue West, Suite D, Lynnwood, Washington 98036
HAND AUGER HA-2
Project: Children's Institute
Location: See Site And Exploration Plan, Figure 2 Project No: 1601.01
Approximate Ground Elevation: 366 Feet Date Excavated: 03-16-2016
Depth Material Description Sample Ne %M Testing
(ft)
Loose, moist to wet, dark brown, silty SAND, with roots and fine
organic material (Topsoil)
I -----------------------------------------------------
Loose to mediwn dense, moist to wet, mottled gray-brown, silty
SAND, some gravel, moderate iron oxide staining
2 (Weathered Glacial Till)
3 -----------------------------------------------------
Dense, moist, gray, silty SAND, some gravel (Glacial Till)
4 Hand Auger completed at 3.5 feet on 3/16/2016.
Very slight perched groundwater seepage observed at 3 feet at time
of exploration.
No caving observed.
5
6
7
8
9
10
11
12
Note: Ne is the Dynamic Cone Penetrometer blow count per ASTM
Special Publication #399.
PPER GEO ASSOCIATI , LLC
19023 361h Avenue West, Suite D, Lynnwood, Washington 98036
HAND AUGER HA-3
Project: Children's Institute
Location: See Site And Exploration Plan, Figure 2 Project No: 1601.01
Approximate Ground Elevation: 374 Feet Date Excavated: 03-16-2016
Depth Material Description Sample Ne %M Testing
(ft)
Loose, moist to wet, dark brown, silty SAND, with roots and fine
organic material (Topsoil)
I -----------------------------------------------------
Medium dense, moist, gray-brown SAND, some silt and gravel
(Weathered Glacial Outwash)
S-1@1.5'
2
3
4 Hand Auger completed at 3.5 feet on 3/16/2016.
No groundwater seepage observed at time of exploration.
Slight caving observed below 12 inches.
5
6
7
8
9
10
11
12
Note: Ne is the Dynamic Cone Penetrometer blow count per ASTM
Special Publication #399.
ZIPPr GEO ASSOCIATES, LL
19023 36m Avenue West, Suite D, Lynnwood, Washington 98036
HAND AUGER HA-4
Project: Children's Institute
Location: See Site And Exploration Plan, Figure 2 Project No: 1601.01
Approximate Ground Elevation: 398 Feet Date Excavated: 03-16-2016
Depth Material Description Sample Ne o/eM Testing
(ft)
Loose, moist to wet, dark brown, silty SAND, with roots and fine
organic material (Topsoil)
I -----------------------------------------------------Mediwn dense, moist, gray-brown, fine to mediwn SAND, some silt
(Weathered Glacial Outwash)
2
S-1@2'
3
4
5
6
Hand Auger completed at 6 feet on 3/16/2016.
7
No groundwater seepage observed at time of exploration.
No caving observed.
8
9
10
11
12
Note: Ne is the Dynamic Cone Penetrometer blow count per ASTM
Special Publication #399.