HomeMy WebLinkAboutRS_Topgolf_Renton_Phase_I_190429_v1Phase I Environmental Site Assessment
Proposed Topgolf Renton
745 Park Avenue North
Renton,Washington 98057
Prepared for:
Topgolf USA
8750 North Central Expressway, Suite 1200
Dallas,Texas 75231
Prepared by:
Professional Service Industries, Inc.
95 Chastain Road NW, Suite 301
Kennesaw,Georgia 30144
April 20, 2018
PSI Project No.:0581204
Trevor Farrell
Staff Scientist
Elizabeth Noakes
Principal Consultant
TABLE OF CONTENTS
LIST OF COMMONLY USED ACRONYMS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . v
CERTIFICATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . vii
1.0 EXECUTIVE SUMMARY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
1.1 FINDINGS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
1.1.1 SITE DESCRIPTION AND CURRENT USE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
1.1.2 ADJOINING PROPERTY DESCRIPTION AND USE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
1.1.3 HISTORICAL USE OF SITE AND SURROUNDING AREA . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
1.1.4 GOVERNMENTAL RECORDS REVIEW . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
1.1.5 SIGNIFICANT DATA GAPS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
1.2 CONCLUSIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
1.2.1 RECOGNIZED ENVIRONMENTAL CONDITIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
1.2.2 CONTROLLED RECOGNIZED ENVIRONMENTAL CONDITIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
1.2.3 HISTORICAL RECOGNIZED ENVIRONMENTAL CONDITIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3
1.2.4 VAPOR ENCROACHMENT CONDITIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3
1.2.5 DE MINIMIS CONDITIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3
2.0 PHASE I ESA SCOPE AND METHODOLOGY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
2.1 PURPOSE OF SERVICES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
2.2 PHASE I ESA METHODOLOGY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
2.3 LIMITATIONS, EXCEPTIONS, DEVIATIONS AND DATA GAP . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
2.4 SIGNIFICANT ASSUMPTIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
3.0 USER-PROVIDED INFORMATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6
3.1 USER QUESTIONNAIRE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6
3.2 TITLE RECORDS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7
3.3 SUGGESTED INFORMATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8
3.4 HELPFUL DOCUMENTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8
4.0 PHYSICAL SETTING . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12
5.0 SITE RECONNAISSANCE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14
5.1 SUBJECT PROPERTY DESCRIPTION AND CURRENT USES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14
5.2 SUBJECT PROPERTY OBSERVATIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 15
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5.2.1 DRUMS OR OTHER BULK CHEMICAL CONTAINERS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 16
5.2.2 DRAINS OR SUMPS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 17
5.2.3 DRINKING WATER/IRRIGATION/MONITORING WELLS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 17
5.2.4 STAINED SOIL/STRESSED VEGETATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 17
5.3 OFF-SITE OBSERVATIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 17
5.3.1 TRANSFORMERS OR OTHER MECH./ELEC. EQUIPMENT THAT COULD CONTAIN PCBS . . . . . . . 19
6.0 HISTORICAL USES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 20
6.1 SUMMARY OF RESOURCES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 20
6.2 CURRENT AND PRIOR USE INTERVIEWS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21
6.3 PRIOR INVESTIGATIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21
6.4 CITY DIRECTORIES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21
6.5 SUMMARY HISTORY OF SITE AND SURROUNDING AREA . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 22
7.0 ENVIRONMENTAL REGULATORY RECORDS REVIEW . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 25
7.1 DATABASE FINDINGS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 25
7.1.1 SUBJECT PROPERTY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 25
7.1.2 SURROUNDING PROPERTIES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 26
7.2 REGULATORY AGENCY INQUIRIES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 34
8.0 VAPOR ENCROACHMENT SCREENING . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36
8.1 METHODOLOGY . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36
8.2 VES RESULTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 38
8.3 VES LIMITATIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 38
9.0 CONTRACT INFORMATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 39
9.1 STANDARD OF CARE AND WARRANTIES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 39
9.2 RELIANCE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 39
9.3 USE BY OTHER PARTIES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 40
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LIST OF APPENDICES
FIGURES
PHOTOGRAPHS
ENVIRONMENTAL DATABASE REPORT
USER QUESTIONNAIRE RESPONSES
LIEN/AUL DOCUMENTATION
HISTORICAL RESEARCH DOCUMENTATION
INTERVIEW DOCUMENTATION
DATA GAP WORKSHEET
SUPPLEMENTAL DOCUMENTATION
VAPOR ENCROACHMENT SCREENING DOCUMENTATION
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LIST OF COMMONLY USED ACRONYMS
AST Above-ground Storage Tank
AUL Activity and Land Use Limitation
AHERA Asbestos Hazard Emergency Response Act
ACM Asbestos-Containing Materials
AMSL Above Mean Sea Level
APN Assessor's Parcel Number (also referred to as a PIN)
ASTM American Society for Testing and Materials
BER Business Environmental Risk
Bgs Below ground surface
BTEX Benzene, Toluene, Ethylbenzene, Xylenes
COC Chemical(s) of Concern
CERCLA Comprehensive Environmental Response, Compensation and Liability Act
CERCLIS Comprehensive Environmental Response,Compensation and Liability Information System
(now called SEMS)
CESQG Conditionally Exempt Small Quantity Generator of Hazardous Waste
CREC Controlled Recognized Environmental Condition
EP Environmental Professional
EPA U.S. Environmental Protection Agency
ESA Environmental Site Assessment
HREC Historical Recognized Environmental Condition
HVAC Heating, Ventilation, and Air Conditioning
LLP Landowner Liability Protection
LQG Large Quantity Generator of Hazardous Waste
LBP Lead-Based Paint
LUST Leaking Underground Storage Tank
MCL Maximum Concentration Level
MSDS Material Safety Data Sheets (now referred to as Safety Data Sheets)
MTBE Methyl tert Butyl Ether
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μg/L Micrograms per Liter
Mg/kg Milligrams per Kilogram
Mg/L Milligrams per Liter
NPL National Priorities List (aka/Superfund)
NFA No Further Action (also known as No Further Remediation)
ND Not Detected
NOV Notice of Violation
OSHA Occupational Safety and Health Administration
ppb Parts per billion
ppm Parts per million
PCE Perchloroethylene (also known as Tetrachloroethylene)
pCi/L Picocuries per liter
PCB Polychlorinated Biphenyls
REC Recognized Environmental Condition
RCRA Resource Conservation and Recovery Act
TPH Total Petroleum Hydrocarbons
TCE Trichloroethylene
UST Underground Storage Tank
USDA United States Department of Agriculture
USGS United States Geological Survey
VEC Vapor Encroachment Condition
VIC Vapor Intrusion Condition
VOC Volatile Organic Compound
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CERTIFICATION
Professional Service Industries,Inc.(PSI),an Intertek company,has completed a Phase I Environmental Site
Assessment of the Proposed Topgolf Renton located at 745 Park Avenue North in Renton,Washington (“the
Subject Property”).PSI performed the Phase I ESA in general accordance with ASTM E1527-13,Standard
Practice for Environmental Site Assessments:Phase I Environmental Site Assessment Process (the Practice).
The assessment was completed at the request of Topgolf USA (“the Client”)in accordance with the scope of
work outlined in PSI’s Proposal Number 0581-239557,which was authorized by the Client on March 27,2017.
The conclusions developed herein represent our professional judgment based on information and data
available to us at the time of the assessment,and observations made at the time of our site reconnaissance.
In accordance with ASTM E1527-13 §4.6,the report is valid for a period of 180 days from the time of issuance.
Site Assessor:
Trevor Farrell
Staff Scientist
Reviewed by:
Elizabeth Noakes
Principal Consultant
Environmental Professional Certification
I declare that,to the best of my professional knowledge and belief,I meet the definition of Environmental
Professional as defined in 312.10 of this part.I have the specific qualifications based on education,training,
and experience to assess a property of the nature,history,and setting of the subject property.I have
developed and performed the all appropriate inquiries in conformance with the standards and practices set
forth in 40 CFR Part 312.
Environmental
Professional:
Elizabeth Noakes
Principal Consultant
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1.0 EXECUTIVE SUMMARY
Professional Service Industries,Inc.(PSI)performed a Phase I Environmental Site Assessment (Phase I ESA)
of the Proposed Topgolf Renton located at 745 Park Avenue North,in Renton,Washington,98057.PSI
performed the assessment to comply with the contract between Topgolf USA (the Client) and PSI.
Our assessment included a Phase I ESA and did not include evaluation of business environmental risks that
are beyond the scope of ASTM E1527 (e.g., asbestos, mold, lead based paint, radon, wetlands, etc.).
1.1 FINDINGS
A summary of findings is provided below.The report should be read in its entirety to obtain a more complete
understanding of the information provided and to aid in any decisions made or actions taken based on this
information.
1.1.1 SITE DESCRIPTION AND CURRENT USE
The subject property is located on the the southeast corner of the intersection of Park Avenue North and
North 8th Street,extending west to Logan Avenue North.The site address is 745 Park Avenue North,Renton,
WA 98057.The site is also defined by the King County Assessor as Parcel Number 088661-0010.Currently,the
subject property is a 13.71 acre parcel of undeveloped land with heavily deteriorated paved parking areas.
No hazardous materials were observed during the site reconnaissance.
1.1.2 ADJOINING PROPERTY DESCRIPTION AND USE
Use of the immediately surrounding properties is summarized in the table below.
Direction Description of Property Use
North N 8th Street, followed by a retail shopping center
South Boeing business offices
West Logan Ave N, followed by the Boeing factory facility
East Park Ave N, followed by paved parking areas
1.1.3 HISTORICAL USE OF SITE AND SURROUNDING AREA
The subject property was undeveloped wetlands from at least 1897 to the mid 1940s when Boeing developed
the site and surrounding area into an aircraft development and manufacturing facility.Historical
documentation reviewed by PSI indicates that the former subject property buildings,known as the "10-80
Buildings",were used as storage areas,offices,and photograph development labs.Four ASTs and a UST
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containing diesel fuel were located on the western portion of the subject property.The UST was
decommissioned in 1987.All buildings and ASTs were removed from the subject property by 2011.
Past uses of the adjoining and surrounding properties include vacant/wetlands/wooded,industrial
manufacturing facilities,commercial/office,and a shopping center.Historically,the property north,south,
east,and west of the subject property was operated by Boeing as part of the aircraft development and
manufacturing facility.The Pacific Car and Foundry (PACCAR)plant operated from 1907 to 1988 to the east of
the subject property, beyond Garden Ave N, producing primarily train cars and military vehicles.
1.1.4 GOVERNMENTAL RECORDS REVIEW
PSI subcontracted with EDR,Inc.(EDR),to provide a review of governmental database records for spill sites,
tanks,hazardous waste handlers,and other facilities of potential concern within proximity to the subject
property.
1.1.5 SIGNIFICANT DATA GAPS
The ASTM E1527 Standard Practice defines a significant data gap as a lack of or inability to obtain information
required by the practice that would limit our ability to draw conclusions with regard to RECs in connection
with the subject property.Based on our experience,the information that we gathered and evaluated did not
present significant data gaps that affected our ability to identify RECs in connection with the subject property.
1.2 CONCLUSIONS
PSI performed a Phase I ESA of the subject property in general accordance with the scope and limitations of
ASTM Practice E 1527-13.Any exceptions to or deletions from this practice are described in Section 2.3 of this
report.The following conclusions have been made with regard to evidence of RECs,HRECs,CRECs,VECs,and
de minimis conditions on the subject property, as defined in ASTM E 1527-13.
1.2.1 RECOGNIZED ENVIRONMENTAL CONDITIONS
This assessment has revealed the following evidence of REC(s) in connection with the subject property:
•Prior soil and groundwater assessment has revealed the presence of vinyl chloride in groundwater
and soil gas at the subject property.Although later groundwater sampling has determined that vinyl
chloride is no longer present in groundwater,no records confirming the absence of vinyl chloride in
soil gas were available.The potential presence of vinyl chloride in soil gas is considered a REC and a
VEC in connection with the subject property.
1.2.2 CONTROLLED RECOGNIZED ENVIRONMENTAL CONDITIONS
This assessment has revealed no evidence of CRECs in connection with the subject property.
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1.2.3 HISTORICAL RECOGNIZED ENVIRONMENTAL CONDITIONS
This assessment has revealed no evidence of HRECs in connection with the subject property.
1.2.4 VAPOR ENCROACHMENT CONDITIONS
The ASTM E1527 Standard Practice requires that the environmental professional evaluate the potential for
VECs on the subject property.A VEC is defined in ASTM E2600 as the presence or likely presence of volatile
chemicals in the subsurface that are caused by the release of vapors from contaminated soil or groundwater
either on or near the subject property.PSI identified the following evidence of a VEC(s)on the subject
property:
•The historical presence of vinyl chloride in soil gas at the subject property is considered to represent
a VEC.
1.2.5 DE MINIMIS CONDITIONS
PSI did not identify any evidence of de minimis conditions on the subject property.
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2.0 PHASE I ESA SCOPE AND METHODOLOGY
2.1 PURPOSE OF SERVICES
PSI performed the Phase I ESA in conformance with ASTM E 1527-13,Standard Practice for Environmental
Site Assessments:Phase I Environmental Site Assessment Process (the Practice).The purpose of the Practice
was to define good commercial practice for conducting a Phase I ESA and as such,the Practice is intended
to permit the user to satisfy one of the requirements to qualify for the LLPs.The goal of the processes
established by the Practice is to identify RECs in connection with the property.
2.2 PHASE I ESA METHODOLOGY
PSI performed a Phase I ESA of the subject property.The scope of our services and general methodology is
presented below.
The information sources that PSI used,including published material,material obtained from commercial and
other sources,is listed below and cited as it is presented in the report.The information or excerpts thereof is
appended.
This assessment included four components:
•Records review;
•Reconnaissance;
•Interviews; and,
•Preparation of this report, including our evaluation.
2.3 LIMITATIONS, EXCEPTIONS, DEVIATIONS AND DATA GAP
PSI considers that limitations,exceptions,and deviations from the Practice manifest as a lack of or inability
to obtain information required by the Practice.This represents the definition of the 'data gap'contained in
the Practice.PSI listed the component objectives of the Practice on the appended Data Gap Worksheet and
tracked the information obtained against the objectives.Therefore the limitations,exceptions and deviations
are identified in the Worksheet.
In general,when required information was incomplete,not provided,otherwise not obtained,or indicated a
need for additional information,PSI attempted to use information from other sources to meet the Practices'
performance objectives.When the data gaps affected the Environmental Professional's ability to identify
RECs,PSI considered the data gap(s)to be significant.PSI identified significant data gaps (if any)on the Data
Gap Worksheet and reported them in Section 1.1.5.
2.4 SIGNIFICANT ASSUMPTIONS
PSI made the following assumptions in developing our Phase I ESA findings and conclusions:
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•Regulatory Agency Information -PSI considers all information provided by our environmental
database subcontractor regarding regulatory status of facilities to be complete,accurate,and
current.
•Other Regulatory Information -PSI considers all information obtained from regulatory or
enforcement agencies to be complete, accurate, and current.
•Title,Lien and AUL Information -PSI considers all information provided by real estate title record
review firms regarding property use or ownership,encumbrances or other limitations,if provided,
to be complete, accurate and current.
•Interviews -PSI considers all information provided through interviews to be complete,unbiased and
provided in good faith.
•Groundwater -PSI interpreted and inferred the direction of the shallow groundwater movement
based on the information we obtained and our experience.Actual groundwater flow may be locally
influenced by many factors beyond the scope of this assessment.Subsurface investigation would be
necessary to determine site-specific groundwater flow direction.
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3.0 USER-PROVIDED INFORMATION
PSI considers the Client to be the 'User'of our assessment,defined in ASTM Practice E 1527 as "the party
seeking to use ASTM E 1527 to complete an environmental site assessment of the property.A User may
include,without limitation,a potential purchaser of property,a potential tenant of property,an owner of
property,a lender,or a property manager.The User has specific obligations for completing a successful
application of this practice...."
3.1 USER QUESTIONNAIRE
The EPA All Appropriate Inquiry Rule (40 CFR Part 312)and ASTM E1527 Section 6 require the User to
answer certain questions related to the property,in order to obtain certain LLPs from CERCLA liability.To
facilitate this process,PSI provided the Client with a User Questionnaire,which is provided in the Appendix.
A summary of the required questions and client responses is provided below:
Question Yes No Unknown N/A
Client did
not respond
Did a review of recorded land title records or other
sources identify any environmental liens filed or
recorded against the subject property under
federal, tribal, state or local law?
Did a review of land title records or other sources
identify any activity use limitations (AULs), such as
engineering controls, land use restrictions or
institutional controls that are in place on the
subject property?
Do you have specialized knowledge or experience
related to the Subject Property or nearby
properties?
Does the purchase price being paid for the
property reasonably reflect the fair market value of
the property?
If you conclude that there is a difference,
have you considered whether the lower
purchase price is because contamination is
known or believed to be present at the
property?
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Question Yes No Unknown N/A
Client did
not respond
Are you aware of commonly known or reasonable
ascertainable information about the property that
would help the environmental professional to
identify conditions indicative of a releases or
threatened releases?
Do you know of the past uses of the
property?
Do you know of specific chemicals that are
present or were once present at the
property?
Do you know of spills or other chemical
releases that have taken place at the
property?
Do you know of any environmental cleanups
that have taken place at the property?
Based on your knowledge and experience related
to the property are there any obvious indicators
that point to the presence or likely presence of
contamination at the subject property?
Do you know of any pending, threatened, or past
litigation or administrative proceedings relevant to
hazardous substances or petroleum products in,
on, or from the property?
Do you know of any notices from any
governmental entity regarding any possible
violation of environmental laws or possible liability
relating to hazardous substances or petroleum
products?
NOTES
The user indicated the subject property was formerly operated by Boeing relating to airplane manufacturing.
3.2 TITLE RECORDS
Based on a review of the local tax assessor’s records,the subject property is currently owned by ITF
Developments, LLC.
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3.3 SUGGESTED INFORMATION
The client provided PSI with the following suggested information described by the Practice.
•The reason for performing the Phase I ESA.
•The type of property and type of property transaction.
•The complete and correct address of the property.
•The scope of services desired for the Phase I ESA,including any evaluation for business
environmental risk that is beyond the scope of ASTM E1527.
•Identification of all parties who will rely upon the report.
•Identification of the key site contact and contact information.
3.4 HELPFUL DOCUMENTS
The Practice requires that the environmental professional ask the property owner,the key site manager
(if any is identified),and the User for certain helpful documents about the property and certain legal
proceedings involving hazardous substances and the subject property.PSI mailed or e-mailed questions
or performed interviews requesting this information.The responses documenting the persons we
corresponded with, and relevant information obtained, are appended where practical.
Report Title:Phase I Environmental Site Assessment: Boeing Renton Facility Parcel 2 (10-80s Property)
Prepared
For:
The Boeing Company
Prepared
By:
Golder Associates, Inc.
Report
Date:
March 2005
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Summary:The Golder Associates, Inc. (Golder) ESA study area comprises a 22.44 acre section of
Boeing's Renton facility known at the time of the report date as Parcel 2. Parcel 2 includes
the subject property at 745 N Park Avenue. Golder identified four existing ASTs and one
former UST located on the western portion of the subject property near Logan Ave N.
Golder identified four RECs on the subject property:
•Building 10-80 was formerly used as a photographic developing laboratory.
•Building 10-80 was formerly used as a manufacturing facility for commercial
aircraft.
•Building 10-85 formerly housed an elevator sump which may have contained
PCBs.
•Four diesel containing ASTs and one UST were located on the western portion of
the subject property near Logan Ave N.
Golder identified four RECs offsite from the subject property:
•PACCAR site is located east of the subject property near Garden Ave N.
Contamination including metals, PCBs, petroleum products, solvents, and PAHs
had been recorded on the site.
•Building 10-71 is located south adjacent to the subject property. Hazardous
materials were used and stored on the site.
•The Mothers Park site is located south adjacent to the subject property near N
6th St. Groundwater contamination of VOCs and metals had been recorded on
the site.
•Garden Plaza/5th and Park buildings located south of the subject property.
Groundwater contamination of petroleum products and vinyl chloride had been
recorded on the site.
Report Title:Boeing Renton Facility - Parcel 2 (10-80s Property): Phase II Environmental Site
Assessment Report
Prepared
For:
The Boeing Company
Prepared
By:
Golder Associates, Inc.
Report
Date:
July 2005
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Summary:The Golder ESA study area comprises a 22.44 acre section of Boeing's Renton facility
known at the time of the report date as Parcel 2. Parcel 2 includes the subject property at
745 N Park Avenue. Golder conducted soil and groundwater sampling activities to
determine potential impacts to the site from RECs previously identified in the March 2005
Phase I ESA.
Golder groundwater investigation indicated a regulatory exceedance of metals arsenic,
iron, and manganese as well as motor oil ranged petroleum hydrocarbons were present
at the subject property.
Report Title:Boeing Renton Facility - Parcel 2 (10-80s Property): Continued Phase II Environmental Site
Assessment
Prepared
For:
The Boeing Company
Prepared
By:
Golder Associates, Inc.
Report
Date:
January 30, 2008
Summary:The Golder ESA study area comprises a 22.44 acre section of Boeing's Renton Facility
known at the time of the report date as Parcel 2. Parcel 2 includes the subject property at
745 N Park Avenue. Golder conducted additional soil, groundwater, and soil vapor
sampling activities to further define potential impacts to the site from RECs previously
identified in the March 2005 Phase 1 ESA.
Golder groundwater investigation indicated a regulatory exceedance of vinyl chloride
ranging from 0.9 μg/L to 3.2 was present in five sampling locations on the northwest
portion of the subject property. The Department of Ecology cleanup level for vinyl chloride
is 0.2 μg/L. Additionally, a regulatory exceedence of benzene and trichloroethene was
detected at one sample location.
Golder soil investigation indicated a regulatory exceedance of arsenic ranging from 5 mg/
kg to 21 mg/kg was present at the subject property. The current, most stringent
regulatory cleanup level for arsenic in soil is 0.667 mg/kg
Golder soil vapor investigation indicated a regulatory exceedance of VOCs
(1,2,4-trimethylbenzene, 1,3-butadiene, benzene, chloroform, and vinyl chloride) was
present at the northwest portion of the subject property.
Report Title:Draft Cleanup Action Plan: Boeing Renton Facility
Prepared
For:
The Boeing Company
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Prepared
By:
AMEC Environment & Infrastructure, Inc.
Report
Date:
September 2012
Summary:The AMEC Cleanup Action Plan (CAP) comprises portions of Boeing's Renton Facility to the
south and west of the subject property at 745 N Park Avenue. The CAP identifies areas of
concern, constituents of concern, and their associated proposed remediation options.
Information obtained from the Department of Ecology indicates the CAP has been
approved and cleanup is ongoing on the Renton Facility.
Report Title:Renton 10-80 Groundwater Monitoring Data
Prepared
For:
Prepared
By:
Shannon & Wilson, Inc.
Report
Date:
Summary:PSI obtained groundwater data from Shannon & Wilson who sampled the groundwater
monitoring wells on the subject property between April 28, 2008 and December 8, 2011.
Groundwater was tested for acetone, 2-butanone, cis-1,2-dicholoroethene, methylene
chloride, and vinyl chloride. Results from the most recent sampling event indicate
constituents were all below cleanup levels.Based on this information, the former
presence of vinyl chloride in groundwater and soil gas is not considered to represent a
REC in connection with the subject property.
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4.0 PHYSICAL SETTING
PSI reviewed a USGS topographic (topo)map,information from the USDA and/or Natural Resources
Conservation Service (NRCS)and/or other information regarding the physical setting of the subject property
to assist with the interpretation of subsurface water movement near the subject property.Physical setting
information is summarized in the table below.
Summary of Physical Setting Information
Physical Setting Attributes Description Source
Subject property elevation:Approximately 35 feet-feet AMSL USGS Topo Map
"Renton, WA" and "Mercer
Island"7.5 minute
Quadrangle 2014
Topographic gradient:The subject property and surrounding
area is generally flat with slight surface
slope towards the west.The
surrounding areas are generally flat
with gradual surface slopes to the
west-northwest.The subject property is
located approximately 1,500 feet east
from Ceder River and approximately
2,300 feet south from Lake Washington.
USGS Topo Map
"Renton, WA" and "Mercer
Island"7.5 minute
Quadrangle 2014
Closest surface water:Ceder River lies approximately 1,500
feet to the west
USGS Topo Map
"Renton, WA" and "Mercer
Island"7.5 minute
Quadrangle 2014
Other resource or physical
characteristics mapped on
the subject property?
No EDR Radius Map Report
Is a flood plain mapped on
the subject property?
No EDR Radius Map Report
Predominant soil type(s)
mapped on the subject
property:
The soil at the subject property is
comprised of Urban Land. Urban Land is
a Class D clayey soil with very
slow infiltration rates.
EDR Radius Map Report
Estimated depth to first
groundwater:
3-9 feet below ground surface Review of previous ESAs
conducted at the subject
property.
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Physical Setting Attributes Description Source
Anticipated regional
groundwater flow direction:
West-northwest EDR Radius Map Report.
Oil and Gas Resources:None mapped on, or adjacent to Subject
Property
EDR Radius Map Report
Mining Resources:None mapped on, or adjacent to Subject
Property
EDR Radius Map Report
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5.0 SITE RECONNAISSANCE
The location and approximate boundaries of the subject property are illustrated on the appended figures.
The legal description of the subject property, if provided to PSI, is appended.
Jessica Sanberg,Real Estate Development Manager for Topgolf USA,granted PSI access to the subject
property. Our assessors were unescorted during the site reconnaissance.
The ground reconnaissance consisted of observing the periphery of the subject property and viewing the
subject property from accessible adjoining public access areas.Visual reconnaissance of adjoining properties
was limited to areas and facilities that were readily observable from the subject property or from public
access areas.PSI also systematically toured the interior portions of the subject property parcels to provide
an overlapping field of view.
The peripheries of surface features and/or structures,where present on the subject property,were observed
along with accessible interior common areas.PSI photo-documented selected features.The photo log is
included in the Appendix.
5.1 SUBJECT PROPERTY DESCRIPTION AND CURRENT USES
General Site Information
Subject Property Address 745 Park Avenue North,Renton,Washington 98057
Parcel Size (acres)13 acres +/-
Site Contact/Escort Jessica Sanberg /N/A
Date of Reconnaissance April 3, 2018
Building Information
Building Description N/A
Size (square feet)N/A
Number of Stories N/A
Approx. Construction
Date
N/A
Utilities
Water City of Renton
Wastewater/Sewer City of Renton
Electricity Puget Sound Energy
Natural Gas Puget Sound Energy
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Heating Source N/A
The subject property is currently undeveloped with a heavily deteriorated paved parking area in the western
portion and heavily deteriorated paved driveway bisecting the property north to south on the central portion.
Catch basins were observed throughout the subject property.The remaining ground cover consists of grassy
and vegetated areas and exposed soil and gravel.
5.2 SUBJECT PROPERTY OBSERVATIONS
A summary of the subject property uses and conditions is tabulated below.Detailed information is discussed
following the summary for any “yes” answers, along with an opinion about the significance of the listing.
Identified?
(check if
Yes)Item Description
Equipment/Activities/Uses
Emergency Generators
Elevators
Hydraulic Lifts
Dry Cleaners/Laundromats
Photo Processing
Medical/Dental Offices - Biomedical Wastes
Automotive/Equipment Repair
Grease Traps and Oil/Water Separators
Wastewater Treatment Systems
Septic or Sewage Tanks
Air Compressors
Transformers or Other Mech./Elec. Equipment That Could Contain PCBs
Pipeline Markers
Oil and Gas Wells
Stormwater Ponds
Quarries, Pits, Lakes, or Lagoons
Use, Storage, or Disposal of Hazardous Substances
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Identified?
(check if
Yes)Item Description
Use, Storage, or Disposal of Petroleum Products
ASTs/USTs
Drums or Other Bulk Chemical Containers
Suspect Containers/Unidentified Contents
Drains and Sumps
Drinking Water, Irrigation or Monitoring Wells
Agrochemical Use/Application
Railroad Spur/Tracks
Potential Evidence of Releases
Interior/Pavement Stains or Corrosion
Stained Soil/Stressed Vegetation
Chemical Odors
Surface Water Sheen or Discoloration
Exterior Pipe Discharges/Unknown Pipes/Effluent Discharges
Pools of Liquid or Standing Water
Solid Waste Dumping/Landfilling/Suspect Fill Material
Construction Debris/Material Stockpiles
Other Uses or Conditions of Concern
5.2.1 DRUMS OR OTHER BULK CHEMICAL CONTAINERS
PSI observed a black,approximately 20-25 gallon,steel drum on site next to the monitoring wells on the north
central portion of the property.The drum was labeled "Non-Regulated Waste"however PSI was not able to
determine the contents.The drum is considered likely to contain investigative-derived waste related to the
presence of monitoring wells on the property,and likely contains soil cuttings and/or purge water.The drum
is not considered to be a REC;however,it should be removed in accordance with local,state and federal
regulations.
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5.2.2 DRAINS OR SUMPS
PSI observed nine catch basins on the subject property.PSI did not observe evidence of a release or staining
and does not consider the presence of catch basins to be a REC to the subject property.
5.2.3 DRINKING WATER/IRRIGATION/MONITORING WELLS
PSI observed four monitoring wells on the north central portion of the subject property.See section 3.4
for more detailed information about the monitoring wells.In themselves,the monitoring wells are not
considered to represent a REC.
5.2.4 STAINED SOIL/STRESSED VEGETATION
PSI observed stressed vegetation in the vicinity around the monitoring wells on the north central portion of
the subject property. The ground surface was predominantly exposed soil with minimal plant growth.
5.3 OFF-SITE OBSERVATIONS
A summary of our interpretation of the current and past uses and conditions of adjoining and surrounding
property based on historical records and observations is provided below.
Identified?
(check if
Yes)Item Description
Equipment/Activities/Uses
Emergency Generators
Elevators
Hydraulic Lifts
Dry Cleaners/Laundromats
Photo Processing
Medical/Dental Offices - Biomedical Wastes
Automotive/Equipment Repair
Grease Traps and Oil/Water Separators
Wastewater Treatment Systems
Septic or Sewage Tanks
Air Compressors
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Identified?
(check if
Yes)Item Description
Transformers or Other Mech/Elec. Equipment That Could Contain PCBs
Pipeline Markers
Oil and Gas Wells
Stormwater Ponds
Quarries, Pits, Lakes, or Lagoons
Use, Storage, or Disposal of Hazardous Substances
Use, Storage, or Disposal of Petroleum Products
ASTs/USTs
Drums or Other Bulk Chemical Containers
Suspect Containers/Unidentified Contents
Drains or Sumps
Drinking Water, Irrigation or Monitoring Wells
Agrochemical Use/Application
Railroad Spur/Tracks
Potential Evidence of Releases
Interior/Pavement Stains or Corrosion
Stained Soil/Stressed Vegetation
Chemical Odors
Surface Water Sheen or Discoloration
Exterior Pipe Discharges/Unknown Pipes/Effluent Discharges
Pools of Liquid or Standing Water
Solid Waste Dumping/Landfilling/Suspect Fill Material
Construction Debris/Material Stockpiles
Other Uses or Conditions of Concern
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5.3.1 TRANSFORMERS OR OTHER MECH./ELEC. EQUIPMENT THAT COULD CONTAIN PCBS
PSI observed a utility building on the south adjoining Boeing property.The utility building appeared to be in
good condition.Historically,PCBs have been found in transformers and their presence cannot be ruled out,
however, PSI does not consider the presence of a utility building to represent a REC to the subject property.
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6.0 HISTORICAL USES
PSI utilized readily ascertainable historical data resources in order to research the history of the site and
surrounding area.The intent of this review was to identify historical tenancies or uses of the subject property
and surrounding area,which might be considered evidence of a recognized environmental condition.
Generally,PSI reviewed the following readily ascertainable historic data resources,where they were available:
•Readily available historical topographic maps were reviewed to evaluate land development in the
area over time.It should be noted that the scale of topographic maps in some cases does not allow
for mapping of individual structures and developed areas may be shown by shading only.
•Selected historical aerial photographs were reviewed at 5-10 year intervals to obtain information
concerning the development and history of the subject property and surroundings.
•PSI reviewed readily ascertainable historical city directories at 5-10 year intervals in order to obtain
information on tenancies on the subject property and adjoining properties.
•PSI requested available historical fire insurance maps from EDR,Inc.The Sanborn Map Company
and other regional providers historically mapped urban areas for use by insurance underwriters.In
some cases these maps provide useful information in evaluating previous tenancies and uses of the
subject property and surrounding area.
Copies of select historical documents are provided in the report appendix;however,it should be noted that
some of the resources used by PSI may be copyrighted and PSI has summarized these resources herein,but
we have not included copies of these resources in the appendix.
6.1 SUMMARY OF RESOURCES
PSI reviewed the following resources in order to evaluate the historic uses of the subject property and
surrounding area:
Source Type Years Reviewed Source
USGS Topo Maps 1895, 1897, 1900, 1949/1950, 1968, 1973, 1983,
1994, 2014
EDR
Aerial Photographs 1943, 1965, 1968, 1977, 1980, 1985, 1990, 2006,
2011, 2015
EDR
City Directories 1964, 1969, 1975, 1982, 1987, 1992, 1995, 2000,
2005, 2010, 2014
EDR
Sanborn Fire Insurance
Maps
1962 EDR
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6.2 CURRENT AND PRIOR USE INTERVIEWS
PSI conducted interviews with persons who are knowledgeable of the current use and history of the site.The
following individuals were interviewed:
Name Title/Role Date Interviewed Comments
Scott Gibson Current Site
Owner
4/4/2018 Filled out questionnaire
Kristin Daves Washington
Department of
Ecology
4/6/2018 FOIA request
Dudley Jackson Renton Regional
Fire Authority
3/28/2018 No records of hazardous material
response
6.3 PRIOR INVESTIGATIONS
The client provided PSI with the reports or documents discussed in Section 3.4 of this report.
6.4 CITY DIRECTORIES
The following table lists the chronological city directories for the subject property and immediately adjacent
properties.
Property Address: Listing Description by Year
Subject Property Logan Ave N and 8th Ave N Intersects
1964, 1969 - Boeing Airplane Co manufacturers; Boeing Employees Credit Union
1975 - Boeing Co; Boeing Co (Technology Service)
1982, 1987 - Boeing Co
North Not Listed
South 605 Park Ave N
1964 - Bob's Mobile Service Gas Station; Doug's Parking Auto
1969 - Paul's Mobile Service Gas Station
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Property Address: Listing Description by Year
East 692 Park Ave N
1964 - Mother's Park (North Renton Recreation Center)
700 Park Ave N
1964 - Torren's Industries (parking lot)
West Not Listed
6.5 SUMMARY HISTORY OF SITE AND SURROUNDING AREA
A chronological summary of the history/use of the subject property and immediately adjacent properties is
provided in the following table.
Date Resource Interpreted Use/Observations
SUBJECT PROPERTY
1897-1900 Topo Maps The subject property appeared to be wetlands.
1943 Aerial Photos The subject property appears to be vacant and undeveloped
land
1949/1950 Topo Maps The subject property appeared to be developed and
contained a structure.
1968-1994 Aerial Photos and
Topo Maps
The previous structure on the subject property appeared to
have been removed and replaced with three new structures.
2006 Aerial Photos and
Topo Maps
The structure on the southeast portion of the subject
property appeared to have been removed.
2011-2015 Aerial Photos and
Topo Maps
All structures appeared to have been removed. The subject
property appeared vacant.
NORTH ADJOINING PROPERTY
1897-1900 Topo Maps The north adjoining property appeared to be wetlands.
1943-1949/1950 Aerial Photos The north adjoining property appeared to be developed with
a road followed by partially wooded land.
1965 Aerial Photos The north adjoining property appeared to be developed with
a driveway/parking area followed by a structure.
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Date Resource Interpreted Use/Observations
1968-1994 Aerial Photos and
Topo Maps
The north adjoining property appeared to be developed with
a driveway/parking area. Beyond which the previous structure
appeared to have been expanded.
2006 Aerial Photos and
Topo Maps
The north adjoining property appeared to be developed with
a driveway/parking area. Beyond which the previous structure
appeared to have been removed and the land vacant.
2011-2015 Aerial Photos and
Topo Maps
The north adjoining property appeared to be developed with
N 8th Street followed by multiple commercial structures.
SOUTH ADJOINING PROPERTY
1897-1900 Topo Maps The south adjoining property appeared to be wetlands.
1943 Aerial Photos The south adjoining property appeared to be mostly vacant
land with numerous small structures adjacent to Logan Ave N
and Park Ave N.
1949/1950 Topo Maps The south adjoining property appeared to be mostly vacant
with numerous small structures adjacent to Logan Ave N
and a larger structure.
1965 Aerial Photos The south adjoining property appeared to be developed with
four structures.
1968-1973 Aerial Photos and
Topo Maps
A new structure appeared to have been added to the south
adjoining property.
1977-1985 Aerial Photos and
Topo Maps
A new structure appeared to have been added to the south
adjoining property.
1990-1994 Aerial Photos and
Topo Maps
Two previous structure appeared to have been removed and
replaced by new structures.
2006 Aerial Photos and
Topo Maps
A previous structure appeared to have been removed.
2011-2015 Aerial Photos and
Topo Maps
A previous structure appeared to have been removed. A new
structure appeared to have been added.
WEST ADJOINING PROPERTY
1897-1900 Topo Maps The west adjoining property appeared to be wetlands,
transected by a road.
1943 Aerial Photos and
Topo Maps
The west adjoining property appeared to be developed with
railroad tracks and Logan Ave N, followed by agricultural
land.
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Date Resource Interpreted Use/Observations
1949/1950 Topo Maps The west adjoining property appeared to be developed with
railroad tracks and Logan Ave N, followed by parking areas.
1965-1994 Aerial Photos and
Topo Maps
The west adjoining property appeared to be developed with
railroad tracks and Logan Ave N, followed by parking areas
and a structure.
2006-2011 Aerial Photos and
Topo Maps
A new structure appeared to have been added to the west
adjoining property.
2015 Aerial Photos The new structure appeared to have been removed from the
west adjoining property.
EAST ADJOINING PROPERTY
1897-1900 Topo Maps The east adjoining property appeared to be wetlands.
1943-1949/1950 Aerial Photos and
Topo Maps
The east adjoining property appeared to be developed with
Park Ave N, followed by wooded land.
1965-2015 Aerial Photos and
Topo Maps
The east adjoining property appeared to be developed with
Park Ave N, followed by a parking lot.
The subject property was undeveloped wetlands from at least 1897 to the mid 1940s.A structure was
observed in the central portion,near N 8th Street in 1949/1950.By 1965 this structure was replaced with a
complex of new structures which remained relatively unaltered until their removal from the subject property
by 2011.
Past uses of the adjoining and surrounding properties include vacant/wetlands/wooded,industrial
manufacturing facilities, commercial/office, and a shopping center.
Environmentally suspect listings on adjoining properties are discussed in detail in Section 7.1.2.
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7.0 ENVIRONMENTAL REGULATORY RECORDS REVIEW
7.1 DATABASE FINDINGS
PSI retained EDR to provide environmental database information attributed to the subject property and its
surroundings.EDR obtains environmental databases published by local,state,tribal,and federal agencies
and maps the information for electronic searches.EDR's service includes reporting Standard Environmental
Records Sources and, in most cases, some Additional Environmental Records Sources.
The search was performed to AMSDs listed in ASTM E 1527-13.The search radius required by ASTM varies
by database.
Unmappable (orphan)sites (if any were listed)having insufficient address information to be mapped were
evaluated for potential location within the AMSD.Those that could be determined to be within the AMSD are
discussed, as appropriate.
The distribution of listed sites with respect to the subject property is tabulated and mapped in EDR's Radius
Map Report,which is appended.The reader is referred to the table,which can be found near the front
of EDR's report.The full names of the abbreviations used below and in EDR’s report can be found in the
Government Records Searched/Data Currency Tracking section of EDR’s report.
7.1.1 SUBJECT PROPERTY
The subject property was listed on one or more regulatory databases as summarized in the following table.
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Facility
Name &
Address Database(s)Comments
Boeing
Company
Renton (AKA:
10-80
Building
Area)
8th & Logan
Ave North
SEMS-ARCHIVE;SEMS-ARCHIVE (Superfund Enterprise Management System Archive)
tracks sites that have no further interest under the Federal Superfund
Program based on available information. The list was formerly known
as the CERCLIS-NFRAP, renamed to SEMS ARCHIVE by the EPA in 2015.
EPA may perform a minimal level of assessment work at a site while it
is archived if site conditions change and/or new information becomes
available. Archived sites have been removed and archived from the
inventory of SEMS sites. Archived status indicates that, to the best of
EPA’s knowledge, assessment at a site has been completed and that
EPA has determined no further steps will be taken to list the site on
the National Priorities List (NPL), unless new information indicates this
decision was not appropriate or other considerations require a
recommendation for listing at a later time. The decision does not
necessarily mean that there is no hazard associated with a given site; it
only means that, based upon available information, the location is not
judged to be potential NPL site.
Information obtained from the Department of Ecology indicates a
550-gallon diesel UST existed on the southeast corner of the subject
property, known at the time as "Building 10-81". This UST and
associated petroleum impacted soil was removed in 1987.
Confirmation soil and groundwater sampling taken in 1999 near the
former indicate remaining petroleum products and PAHs are
present near the former UST location. The highest detected
constituents are below current minimum cleanup levels.Based on
this information, the former presence of a diesel UST is not considered
to represent a REC in connection with the subject property.
An Agreed Order (No 8191) is currently in place between the
Department of Ecology and the Boeing Company as part of the Boeing
Renton facility cleanup. On December 12, 2007, the Agreed Order was
amended to exclude the subject property from further cleanup action.
7.1.2 SURROUNDING PROPERTIES
PSI identified a number of regulated facilities and/or spill sites within the search radius.However,none of
these sites are adjacent to the subject property and PSI considered the remaining database listings unlikely
to impact the subject property based upon factors including (but not limited to):
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•The nature of the listing;
•The use of the facility;
•When the facility was listed and its current listed status;
•The developmental density of the setting;
•The potential for vapors to encroach from the property to the subject property;
•The distance between the listing and subject sites related to whether releases are likely to migrate
based on local surface and subsurface drainage conditions; and/or
•The presence of intervening drainage divides; and/or inferred groundwater movement.
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Facility
Name &
Address
Distance (feet)
& Direction
Elevation
Difference
(feet)Database(s)Comments
Renton Plant
737 Logan
Ave N; 800 N
6th Street
EDR Site ID:
A3; A4; A11;
G42; G43
157 feet
North- West-
Southwest-
South
Varies UST; HSL;
CSCSL;
ALLSITES;
SPILLS;
MANIFEST;
NPDES;
CORRACTS;
RCRA-TSDF;
RECRA-LQG;
US ENG
CONTROLS;
US INST
CONTROL;
US FIN
ASSUR; 2-2
COR ACTION;
FINDS;
ECHO;ICR,
RAATS
The Boeing facility at 737 Logan Ave N
(Facility Site ID #2097)is listed on the
UST database as being the location of
48 USTs.Eight USTs are listed as being
currently operational.
The Boeing Facility at 800 N 6th Street is
listed on the ICR database as being the
location of 1996 a soil and groundwater
cleanup of petroleum products.
The site is listed on the CSCSL database
as the location of an ongoing soil and
groundwater cleanup of asbestos,
corrosive wastes,metals,
non-halogenated solvents,petroleum
products,phenolic compounds,PCBs,
and PAHs.
The site is listed on the WA MANIFEST
database as a hazardous waste
generator as of 2009.No notices of
violation have been recorded.
The site is listed on the RCRA-LQG
database.The EPA RCRA Program
identifies and tracks hazardous waste
from the point of generation to the
point of disposal.The database includes
selective information on sites which
generate,transport,store and/or
dispose of hazardous waste as defined
by RCRA.LQGs generate over 1,000 kg
of hazardous waste,or over 1 kg of
acutely hazardous waste per month.A
number of violations have been
recorded between since 1985,however
the site currently has achieved
compliance for each.
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Facility
Name &
Address
Distance (feet)
& Direction
Elevation
Difference
(feet)Database(s)Comments
The site is listed on the FINDS database.
The FINDS database contains both site
information and “pointers”to other
databases that contain more detail.A
listing on the FINDS database is not
inherently indicative of a REC.
The site is listed on the ECHO
database.The ECHO database provides
integrated compliance and
enforcement information for about
800,000 properties nationwide.
Information obtained from the Ecology
indicate this site is currently undergoing
soil and groundwater remediation.
Dick's
Sporting
Goods 621
915 N
Landing Way
EDR Site ID
B17; B18
336 feet
North-northeast
35 feet
higher
RCRA-CESQG;
ALLSITES; WA
MANIFEST
Dick's Sporting Goods 621 is listed on
the RCRA-CESQG database for multiple
kinds of hazardous waste.The EPA
RCRA Program identifies and tracks
hazardous waste from the point of
generation to the point of disposal.The
database includes selective information
on sites which generate,transport,
store and/or dispose of hazardous
waste as defined by RCRA.CESQGs
generate less than 100 kg of hazardous
waste or less than 1 kg of acutely
hazardous waste per month.No
violations are associated with this listing
and based on this information,Dick's
Sporting Goods 621 is not considered to
represent a REC in connection with the
subject property.
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Facility
Name &
Address
Distance (feet)
& Direction
Elevation
Difference
(feet)Database(s)Comments
Kenny's Auto
Rebuild, Inc.
618 Park Ave
N
EDR Site ID:
C19
536 feet
Southeast
40 feet
higher
ALLSITES;
RCRA
NonGen/
NLR; FINDS;
MANIFEST
Kenny's Auto Rebuild,Inc.is listed on
the RCRA NonGen/NLR database.The
EPA RCRA Program identifies and tracks
hazardous waste from the point of
generation to the point of disposal.The
database includes selective information
on sites which generate,transport,
store and/or dispose of hazardous
waste as defined by RCRA.
Non-Generators do not presently
generate hazardous waste or were
verified not to have ever generated
hazardous waste.No violations are
associated with this listing and based on
this information,Kenny's Auto Rebuild,
Inc.is not considered to represent a
REC in connection to the subject
property.
Dunlap Paul
605 Park Ave
EDR Site ID:
C22
643 feet
Southeast
39 feet
higher
EDR Hist
Auto
Dunlap Paul is listed on the EDR Hist
Auto database.EDR has searched
selected national collections of business
directories and has collected listings of
potential gas station/filling station/
service station sites that were available
to EDR researchers.EDR’s review was
limited to those categories of sources
that might,in EDR’s opinion,include gas
station/filling station/service station
establishments.The categories
reviewed included,but were not limited
to,gas,gas station,gasoline station,
filling station,auto,automobile repair,
auto service station,service station,etc.
No spills,releases,or cleanups at the
site have been reported.Based on the
current regulatory status,Dunlap Paul
is not considered to represent a REC in
connection to the subject property.
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Facility
Name &
Address
Distance (feet)
& Direction
Elevation
Difference
(feet)Database(s)Comments
Garden Plaza
Park Ave N
and N 6th St
EDR Site ID:
C25
734 feet
Southeast
39 feet
higher
INST
CONTROL;
ICR; VCP;
ALLSITES;
CSCSL NFA
Garden Plaza (Facility ID #2475)is listed
on the INST CONTROL database.
Information obtained from the
Department of Ecology indicate the site
was formerly the location of a coal and
oil distribution facility from 1943 until
1967.A restrictive covenant was placed
on the site in 1994 and 2001
following cleanup and groundwater
monitoring of petroleum products,vinyl
chloride,and arsenic.Washington
Department of Ecology issued a
conditional NFA determination for the
site in 2001 and noted the remaining
groundwater contamination is likely
due to the upgradient PACCAR site.
Garden Plaza is subject to five year
periodic reviews by the Department of
Ecology to assess the protection of
human health and the environment.
Based on the current regulatory status,
Garden Plaza is not considered to
represent a REC in connection to the
subject property.
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Facility
Name &
Address
Distance (feet)
& Direction
Elevation
Difference
(feet)Database(s)Comments
Kenworth
Truck Co
1601 N 8th
Street
EDR Site ID:
H39
1201 feet
East
48 feet
higher
RCRA-LQG;
ALLSITES;
TRIS; ICIS; US
AIRS; FINDS;
ECHO;
MANIFEST;
NPDES
The Kenworth Truck Co is listed on the
RCRA-LQG database.The EPA RCRA
Program identifies and tracks
hazardous waste from the point of
generation to the point of disposal.The
database includes selective information
on sites which generate,transport,
store and/or dispose of hazardous
waste as defined by RCRA.LQGs
generate over 1,000 kg of hazardous
waste,or over 1 kg of acutely hazardous
waste per month.The Kenworth Truck
Co most recently received a notice of
violation in December 2016.
Compliance was achieved in February
2017.
The Kenworth Truck Co is listed on the
ECHO database.The ECHO database
provides integrated compliance and
enforcement information for about
800,000 properties nationwide.
Based on the current regulatory status
the Kenworth Truck Co is not
considered to represent a REC to the
subject property.
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Facility
Name &
Address
Distance (feet)
& Direction
Elevation
Difference
(feet)Database(s)Comments
Pacific Car &
Foundry Co.
1400 N 4th
Street; 480,
502 Houser
Way
EDR Site ID:
65; N67; N73;
N74
2177 feet
South-southeast
42 feet
higher
NPL; SEMS;
US ENG
CONTROLS;
US INST
CONTROL;
HSL; CSCSL;
INST
CONTROL;
ALLSITES;
RCRA
NonGen/
NLR; ROD;
MANIFEST;
NPDES;
FINDS; UST;
CSCSL NFA;
ICR; Financial
Assurance
The Pacific Car &Foundry Co (PACCAR)
site (Facility Site ID #2065)is listed on
the NPL database.Historically,PACCAR
operated as a foundry and railroad car
and military vehicle manufacturing
plant.The PACCAR plant was closed in
1988.Information obtained from
Washington Department of Ecology
indicate that the site was subject to
cleanup activities from 1990 to 1997
with regard to soil contamination which
included halogenated organics,metals,
non-halogenated solvents,petroleum
products,phenolic compounds,PCBs,
and PAHs,as well as metals and
halogenated organics impacted
groundwater.Currently,the PACCAR
site is subject to groundwater
monitoring by Ecology under EPA
direction.Additionally,a restrictive
covenant has been placed on the
property.
The site is listed on the SEMS database.
The SEMS database tracks hazardous
waste sites,potentially hazardous waste
sites,and remedial activities performed
in support of EPA’s Superfund Program
across the United States.The list was
formerly known as CERCLIS,renamed
to SEMS by the EPA in 2015.The list
contains data on potentially hazardous
waste sites that have been reported to
the EPA by states,municipalities,private
companies,and private persons,
pursuant to Section 103 of CERCLA.This
database also contains sites which are
either proposed to or on the NPL and
the sites which are in the screening and
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Facility
Name &
Address
Distance (feet)
& Direction
Elevation
Difference
(feet)Database(s)Comments
assessment phase for possible
inclusion on the NPL.
Most recent groundwater monitoring
data indicates the continued presence
of vinyl chloride and arsenic above
established standards;however,at low
concentrations.Based on the low
concentrations,the continued
monitoring,and the location (does not
directly adjoin the subject property),the
PACCAR facility is not considered to
represent evidence of a REC in
connection with the subject property.
7.2 REGULATORY AGENCY INQUIRIES
PSI requested records or information about the subject property and/or surrounding area from the
governmental agencies listed in the following sections.Information was requested by telephone,in person,
via e-mail or through a written FOIA or equivalent request, as appropriate.
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FIRE DEPARTMENT
Renton Regional Fire Authority responded via e-mail to a FOIA request on March 28,2018.Renton Regional
Fire Authority had no records of hazardous material response related to the subject property.
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8.0 VAPOR ENCROACHMENT SCREENING
8.1 METHODOLOGY
Vapor encroachment is an emerging concern associated with the potential for volatile chemicals,such
as petroleum fuels and chlorinated solvents to migrate through the subsurface in the gas phase from
contaminated soil and/or groundwater plumes.Vapor encroachment may be a concern if subsurface volatile
contaminants migrate into occupied buildings through cracks and penetrations in the building slab.
The ASTM E1527-13 Standard Practice for Environmental Site Assessments:Phase I Environmental Site
Assessment process requires the Environmental Professional to evaluate the potential for vapor
encroachment onto the subject property,and to determine if such vapor encroachment constitutes evidence
of a REC on the subject property.The E1527-13 Standard Practice does not specifically state the methods
that must be used to screen for potential vapor encroachment issues.However,ASTM has developed a
separate Standard Guide for Vapor Encroachment Screening on Property Involved in Real Estate Transactions
(ASTM E2600-15).The vapor encroachment screening guidance outlines a methodology to conduct vapor
encroachment screening,which will satisfy the vapor screening requirements under the Phase I ESA Standard
Practice.PSI utilized the ASTM E2600-15 Standard Guide to conduct vapor encroachment screening for the
subject property.
The goal of conducting Vapor Encroachment Screening (VES)is to identify a VEC,which is defined as the
presence or likely presence of COC vapors in the subsurface of the subject property caused by the release of
vapors from contaminated soil either on or near the subject property.If a VEC is identified,the environmental
professional must determine whether the VEC represents evidence of a REC on the subject property under
the context of the Phase I ESA Standard Practice.It should be noted that the identification of a VEC on
the subject property does not necessarily indicate that a potential for migration of vapors into existing or
proposed structures on the subject property is likely.The environmental professional will identify the VEC as
a REC where the potential for vapor migration into structures is considered likely,or where the contaminant
concentrations in the soil,groundwater,or soil vapors on the subject property are significant and likely to
result in enforcement against on-site or off-site responsible parties.
The VES utilizes information regarding the potential presence of releases on or near the subject property that
were collected as a normal part of the Phase I ESA process,such as governmental database records,review of
governmental files,historical data sources,etc.No additional data was collected specifically for the purpose
of the VES.In order to identify potential sites of concern within the approximate minimum search distance,
PSI reviewed Sanborn Maps,governmental database records,regulatory agency files,aerial photographs,
and other information as available and appropriate.
VES Standard Guide prescribes a two tier approach for screening of sites for potential vapor encroachment.
In Tier I,potential sites of concern within the search radii are identified and the environmental professional
must determine whether a VEC exists or not based on the information that is available within the context
of the Phase I ESA data gathering.If the available information indicates that a VEC exists based on available
information,the environmental professional,in consultation with the User,may conduct Tier II screening
to further evaluate the potential risk.Under Tier II,the environmental professional would review available
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reports through the regulatory agency or other reasonably ascertainable sources to determine the status of
assessment/remediation,size and migration pathways for any associated plumes,geologic conditions,and
other geologic information.This information would be utilized to determine the distance between the plume
and the target property boundary.For example,if the distance from the edge of a plume in a downgradient
position to the subject property boundary exceeds 100 feet for VOCs or petroleum free product,or 30 feet
for dissolved petroleum hydrocarbons (PHCs),then the site may be screened out and a VEC does not exist.
Functionally,where Tier II information is readily available during the normal course of conducting the Phase
I ESA,PSI has combined the Tier I and Tier II steps herein.Where agency files are not readily available for
nearby contaminated sites within the typical schedule for a Phase I ESA,then Tier II screening might be
recommended as a separate step subsequent to the Phase I ESA.Where Tier II screening is recommended,
the sites of concern where data is lacking are considered a VEC until further information is available and/or
further screening is completed.
The VES Standard Guide requires the environmental professional to search for potential sites of concern
within the following databases and search distances,where groundwater flow is not known and/or
preferential pathways for groundwater or vapor flow may exist:
Standard Environmental Records Sources
Minimum Search Distance
(miles) - VOCs, excluding
PHCs
Minimum Search
Distance (miles) -
PHCs
State and tribal HWS lists 1/3 1/10
State or tribal-equivalent NPL 1/3 1/10
State or tribal-equivalent CERCLIS list 1/3 1/10
State or tribal landfill or solid waste site list 1/3 1/10
State or tribal leaking storage tank lists 1/3 1/10
State and tribal registered tank lists Subject property only Subject property only
State and tribal IC/EC registries Subject property only Subject property only
State and tribal voluntary cleanup site lists 1/3 1/10
State and tribal brownfield sites list 1/3 1/10
Federal NPL site list 1/3 1/10
Federal CERCLIS list 1/3 1/10
Federal RCRA CORRACTS list 1/3 1/10
Federal RCRA non-CORRACTS TSD List 1/3 1/10
Federal RCRA Generators List Subject property only Subject property only
Federal IC/EC registries Subject property only Subject property only
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Standard Environmental Records Sources
Minimum Search Distance
(miles) - VOCs, excluding
PHCs
Minimum Search
Distance (miles) -
PHCs
Federal ERNS list Subject property only Subject property only
The default search distances may be expanded or reduced in the upgradient,downgradient,or
cross-gradient directions by the environmental professional based on experience in the local area and
applying professional judgment to factors such as where a well-defined regional groundwater flow direction
is identified,or whether other geologic features such as low permeability soils or hydrogeologic boundaries
such as rivers or streams exist which would tend to limit the potential for migration of groundwater or vapors
in a particular direction.
8.2 VES RESULTS
Site Name/
Address
Distance,
Direction,
Relative
Elevation
to the
Subject
Property
Does the
site
represent
a VEC?Comments
10-80
Building
Area
Subject
Property
Yes Vinyl chloride has historically been present in soil gas at
the subject property.
The presence of vinyl chloride in groundwater and soil gas at the subject property is considered to represent
a VEC.
8.3 VES LIMITATIONS
The VES process is not intended to be an exhaustive screening and cannot wholly eliminate uncertainty
regarding the presence of VECs in connection with the subject property.Screening is intended to reduce,but
not eliminate uncertainty regarding whether or not a VEC exists in connection with the subject property.
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9.0 CONTRACT INFORMATION
9.1 STANDARD OF CARE AND WARRANTIES
Our services were not intended to be technically exhaustive.There is a possibility that with the proper
application of methodologies,conditions may exist on the property that could not be identified within the
scope of the assessment(s) or that were not reasonably identifiable from the available information.
No ESA can wholly eliminate uncertainty regarding the potential for RECs in connection with the property.
The ESA was intended to reduce,but not eliminate uncertainty regarding the potential for RECs in connection
with a property.
Our report is based on commonly known and reasonably ascertainable information,including limited,
ground-level visual inspection of the property except where otherwise explicitly indicated,in general
conformance with ASTM E1527-13.Findings and conclusions derived from the methodologies described in
the Practice contain all of the inherent limitations in the methodologies that are referred to in the Practice.
PSI has assumed that factual information provided to us by the Client,or obtained from governmental and
historical research firm,the public domain,interviews,and other sources is accurate and unbiased.PSI
assumes no liability for the accuracy of data provided to us by others.
PSI did not perform exploratory probing or discovery,perform tests,operate specific equipment,or take
measurements or samples to perform the ESA scope.The ESA was not a building code,safety,regulatory or
environmental compliance inspection.The ESA is not intended to reduce the risk of the presence of mold and
physical deficiencies conducive to mold nor the risk that mold or physical deficiencies conducive to mold may
pose to the buildings and building occupants.
The methodologies include reviewing information provided by other sources.PSI treats information obtained
from the record reviews and interviews concerning the property as reliable and the ASTM protocol does not
require PSI to independently verify the information.Therefore,PSI cannot and does not warrant or guarantee
that the information provided by these other sources is accurate or complete.
PSI has performed the services in a manner consistent with that level of care and skill ordinarily exercised
by other members of our profession currently practicing in the same locality and under similar conditions,
within the limitations of ASTM E1527-13 standard,and the All Appropriate Inquiries Rule established by the
U.S. Environmental Protection Agency (40 C.F.R. Part 312). No other warranties are implied or expressed.
The observations and recommendations presented in this report are time dependent,and conditions will
change. This report speaks only as of its date.
9.2 RELIANCE
Topgolf USA, PSI's client, may rely on this report.
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9.3 USE BY OTHER PARTIES
This report was prepared pursuant to a contract between PSI and its client.That contractual relationship
included an exchange of information about the property that was unique and serves as the basis upon which
this report was prepared.Because of the importance of these understandings,our assessment may not be
sufficient for the intended purposes of another party.
Reliance or any use of this report by anyone other than those parties identified above for which it was
prepared,except with express written permission,is prohibited and therefore not foreseeable to PSI.Any
unauthorized reliance on or use of this report,including any of the information or conclusions contained
herein,will be at the third party's risk.No warranties or representations expressed or implied in this report
are made to any such third party.
Third party reliance letters may be issued:
•upon timely request;
•subject to the permission of our original client; and
•payment of the then-current fee for such letters.
All third parties relying on our report,by such reliance,agree that such reliance is limited by our proposal
and/or General Conditions, as applicable.
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FIGURES
PSI, INC.
6032 N. CUTTER CIRCLE, SUITE 480
PORTLAND, OREGON 97217
(503) 289-1778
DATE:
APRIL
2018
PSI PROJECT NUMBER
0581204-1
DRAWN BY:
TMF SITE VICINITY MAP
FIGURE 1
PROPOSED TOPGOLF RENTON
745 PARK AVE N
RENTON, WA 98057
PHOTOGRAPHS
Project Number: 0581-204
Proposed Topgolf Renton
www.intertek.com/building
Photo 1 – View of north side of subject property, facing north.
Photo 2 – View of east side of subject property, facing east.
Project Number: 0581-204
Proposed Topgolf Renton
www.intertek.com/building
Photo 3 – View of south side of subject property, facing south.
Photo 4 – View of west side of subject property, facing west.
Project Number: 0581-204
Proposed Topgolf Renton
www.intertek.com/building
Photo 5 – View of north adjoining property, facing northwest.
Photo 6 – View of north adjoining property, facing northeast.
Project Number: 0581-204
Proposed Topgolf Renton
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Photo 7 – View of east adjoining property, facing northeast.
Photo 8 – View of south adjoining property (utility building), facing east.
Project Number: 0581-204
Proposed Topgolf Renton
www.intertek.com/building
Photo 9 – View of south adjoining property, facing south.
Photo 10 – View of west adjoining property, facing west.
Project Number: 0581-204
Proposed Topgolf Renton
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Photo 11 – View of paved areas, west portion of the subject property, facing south.
Photo 12 – View of a catch-basin, facing north.
Project Number: 0581-204
Proposed Topgolf Renton
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Photo 13 – View of a monitoring well, north-central portion of the subject property.
Photo 14 – View of a monitoring well, north-central portion of the subject property.
Project Number: 0581-204
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Photo 15 – View of an approximately 20-25-gal steel drum, north-central portion of subject
property.
Photo 16 – View of exposed soil with limited plant growth near monitoring wells, north-central
portion of subject property facing east.