DERR-2025-000540

Phase I Environmental Site Assessment
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Salt Lake County, Utah
December 5, 2024 | Terracon Project No. 61247234
Prepared for:
Utah Inland Port Authority
60 E. South Temple, Suite 600
Salt Lake City, Utah
Prepared by:
Terracon Consultants, Inc.
Midvale, Utah
6949 S High Tech Dr Ste 100
Midvale, UT 84047-3707
P 801-545-8500
F 801-545-8600
Terracon.com
Facilities | Environmental | Geotechnical | Materials
December 5, 2024
Utah Inland Port Authority
60 E. South Temple, Suite 600
Salt Lake City, Utah 84111
Attn: Ben Hart
P: [phone]
E:[e-mail]
Re:Phase I Environmental Site Assessment
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Salt Lake County, Utah
Terracon Project No. 61247234
Dear Mr. Hart:
Terracon Consultants, Inc. (Terracon) is pleased to submit the enclosed Phase I
Environmental Site Assessment (ESA) report for the above-referenced subject property
(hereinafter known as the ‘site’). This assessment was performed in accordance with
Terracon Proposal No. P61247234 dated July 26, 2024.
We appreciate the opportunity to be of service to you on this project. In addition to
Phase I services, our professionals provide other environmental, geotechnical,
construction materials, and facilities services on a wide variety of projects locally,
regionally, and nationally. For more detailed information on all of Terracon’s services
please visit our website at www.terracon.com. If there are any questions regarding this
report or if we may be of further assistance, please do not hesitate to contact us.
Sincerely,
Terracon Consultants, Inc.
Ellie Roubal Tina Cheney
Field Geologist ESA Group Manager
Attachments
Facilities | Environmental | Geotechnical | Materials
Table of Contents
EXECUTIVE SUMMARY ....................................................................... i
Findings and Opinions ................................................................................ i
Significant Data Gaps ................................................................................ iii
Conclusions ............................................................................................. iii
Recommendations..................................................................................... iii
1.0 INTRODUCTION ...................................................................... 1
1.1 Site Description ................................................................................ 1
1.2 Scope of Services .............................................................................. 1
1.3 Standard of Care ............................................................................... 2
1.4 Additional Scope Limitations, ASTM Deviations, and Data Gaps ................. 3
1.5 Reliance ....................................................................................... 4
1.6 Client Provided Information ................................................................ 4
2.0 PHYSICAL SETTING ................................................................. 5
3.0 HISTORICAL USE INFORMATION ................................................ 6
3.1 Historical Topographic Maps, Aerial Photographs, and Sanborn Maps ......... 6
3.2 Historical City Directories ................................................................... 8
3.3 Site Ownership ................................................................................. 9
3.4 Title Search ...................................................................................... 9
3.5 Environmental Liens and Activity and Use Limitations ............................. 10
3.6 Interviews Regarding Current and Historical Site Uses ............................ 10
3.7 Prior Report Review .......................................................................... 11
4.0 RECORDS REVIEW ..................................................................13
4.1 Federal and State/Tribal Databases ..................................................... 13
4.2 Local Agency Inquiries ...................................................................... 22
5.0 SITE RECONNAISSANCE ..........................................................23
5.1 General Site Information ................................................................... 23
5.2 Overview of Current Site Occupants and Site Operations ........................ 23
5.3 Site Observations ............................................................................. 24
Facilities | Environmental | Geotechnical | Materials
6.0 ADJOINING PROPERTY RECONNAISSANCE .................................27
7.0 ADDITIONAL SERVICES ...........................................................27
8.0 DECLARATION .......................................................................27
APPENDICES
APPENDIX A Exhibit 1: Topographic Map, Exhibit 2: Site Diagram
APPENDIX B Site Photographs
APPENDIX C Historical Documentation and User Questionnaire
APPENDIX D Environmental Database Information
APPENDIX E Credentials
APPENDIX F Description of Terms and Acronyms
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials i
EXECUTIVE SUMMARY
This Phase I Environmental Site Assessment (ESA) was performed in accordance with
Terracon Proposal No. P61247234 dated July 26, 2024, and was conducted consistent
with the procedures included in ASTM E1527-21,Standard Practice for Environmental
Site Assessments: Phase I Environmental Site Assessment Process. The purpose of this
ESA was to assist the client in developing information to identify Recognized
Environmental Conditions (RECs) in connection with the site as reflected by the scope of
this report. The ESA was conducted under the supervision or responsible charge of Tina
Cheney, Environmental Professional, who performed the site reconnaissance with Ellie
Roubal, Field Geologist, on November 20, 2024.
Findings and Opinions
A summary of findings is provided below. It should be recognized that details were not
included or fully developed in this section, and the report must be read in its entirety for
a comprehensive understanding of the items contained herein.
Site Description and Use
The site is approximately 769.85 acres of land (Salt Lake County previous Parcel ID of
07-35-100-016-0000), which was the former North Temple Landfill (NTL). The current
site Parcel ID 07-35-100-020-0000 acreage (765.06) appears to have decreased due to
the establishment of a roadway easement in the southeastern portion; however, the
easement was not excluded from the site boundary. Active landfilling operations ceased
on the property in late 1970s. Since that time a series of site investigations have taken
place including the current work effort associated with the Voluntary Cleanup Program
(VCP) which includes excavation of test pits, leachate sampling collection, lead shot
scraping, and groundwater sampling. The waste within the landfill remains covered.
Historical Information
The site was undeveloped land with ponds in 1937. In the late 1950s Salt Lake City
opened a municipal landfill on the site. The City continued to operate the landfill until
the late 1970s, at which point the landfill closed. In 1995, wastes from the east-
adjoining North Temple Landfill-East (NTL-E) site was moved and stockpiled on the
southeast portion of the site. From 2001 until 2005 a shotgun range was present in an
area of the southeast portion of the property. From 2009 to 2013 (concurrent with the
construction of the City Creek development) concrete, brick, and excavated soil
(referred to as City Creek demolition material) was transported and stockpiled in the
southwest corner of the site. The City Creek demolition material and the NTL-E waste
remain on the site.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials ii
The ongoing presence of landfill wastes, the impacts to soil from the historical use as a
gun range, and the impacts to soil and groundwater from the site’s historic use as a
landfill represents a REC.
The north-adjoining land was undeveloped from at least 1937 to 2000, then a road and
warehouses began to be developed. The east-adjoining property was undeveloped land
and/or farmland from at least the 1930s to 1950s. In the 1950s, portions of the east
adjoining property were used as a landfill, known as the North Temple Landfill—East
(NTL-E); this landfill was capped and closed in 1959. In 1995, wastes from the NTL-E
site were excavated and placed on the NTL site. A VCP Application was submitted in
1998 for the east adjoining property identifying the site as the Bonneville Center. The
property remained undeveloped from 1959 until 2004, when the Quality Distribution
Warehouse was built, followed by other commercial buildings. The south-adjoining
properties have been ponds and vacant land with a road from at least 1937 to the
1970s. In 1985, the U.S. Interstate 80 expanded. The remaining land is vacant. The
west-adjoining property has remained undeveloped from at least 1937 to the current
day. Based on the regulatory status of the NTL-E, and the ongoing investigations at the
site, the adjoining properties do not represent a REC to the site.
Records Review
Selected federal and state environmental regulatory databases as well as responses
from state and local regulatory agencies were reviewed. The NTL is listed on the
CERCLIS/SEMS/VCP/Historical Solid Waste and Landfill Facilities (HSWF) databases. As
noted above, the ongoing presence of uninvestigated landfill wastes, and the impacts to
soil and groundwater from the site’s historic use as a landfill represents a REC. In
addition, the on-going involvement in the VCP program, with associated site
characterizations will likely identify additional impacts that represent a REC.
An east-adjoining property was identified as Valspar (Quality Distribution) on the RCRA
Non-Generator database. Due to the regulatory status of the Valspar site, and no
reported release, it does not represent a REC.
Another east adjoining property is also identified as the NTL-E on the CERCLIS/CERLIS
NFRAP/SEMS ARCHIVE databases and the Bonneville Center in the VCP databases. Based
on Bonneville Center VCP’s Certificate of Completion, the active Site Management Plan,
and the removal of the wastes during the VCP closure, the historic NTL-E site does not
represent a REC.
The remaining facilities listed in the database report do not appear to represent RECs to
the site at this time based upon regulatory status, apparent topographic gradient,
and/or distance.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials iii
Site Reconnaissance
Terracon observed several 55-gallon drums, stockpiled soils, vegetation debris,
construction debris, the West Branch Brighton Canal, and monitoring wells during the
site reconnaissance. Based on the site investigations associated with the ongoing VCP
activities, the landfill debris is considered a REC.
Adjoining Properties
The north-adjoining property is 700 North followed by warehouses, a substation, and
vacant land. The east-adjoining properties are Easton Archery, Bureau of Land
Management West Desert District, Quality Distribution/Global Xoom, an Amazon
warehouse, and railroad lines. The south-adjoining properties are the North Temple
Frontage Road, followed by Interstate 80, and vacant land. To the west is vacant land
and a new warehouse building. RECs were not observed with current operations of the
adjoining properties.
Significant Data Gaps
No significant data gaps (SDGs) were identified.
Conclusions
We have performed a Phase I ESA consistent with the procedures included in ASTM
Practice E1527-21 at 6780 North Temple Frontage, Salt Lake City, Salt Lake County,
Utah, the site. Controlled RECs (CRECs) and/or SDGs were not identified. The following
REC was identified in connection with the site:
Releases from the historical use of the site and on-going involvement in
VCP Program: The historical use of the site, presence of landfill wastes, and the
documented presence of hazardous substances in the soil and groundwater
represents a REC. In addition, the on-going involvement in the VCP program will
likely identify additional impacts that represent a REC.
Recommendations
Based on the scope of services, limitations, and conclusions of this assessment, Terracon
recommends the following additional actions.
Awareness of Continuing Obligation(s): All appropriate inquiry (AAI) establishes
landowner liability protections (LLPs) for property owners under CERCLA, as
innocent landowners, bona fide prospective purchasers, and/or contiguous
property owners. In order to use the LLPs under CERCLA, a purchaser must
perform all appropriate inquiry (i.e., their due diligence) before acquiring the
property. Additionally, the United States Environmental Protection Agency (EPA)
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
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requires the purchaser to meet ongoing continuing obligations. These continuing
obligations are generally stated below.
1.compliance with any established environmental land use restrictions
2.take “reasonable steps” with respect to hazardous substance releases
reasonable steps generally include the following: stop continuing releases;
prevent threatened future releases; and prevent or limit human,
environmental, or natural resource exposure to existing hazardous substance
releases
3.provide full cooperation, assistance, and access to authorized personnel to
investigate the site
4.compliance with information requests and administrative subpoenas.
5.providing legally required notices with respect to the discovery or release of
any hazardous substances at the facility
Based on the findings of this assessment, Terracon identified RECs for the site
associated with the releases of hazardous substances in the soils and
groundwater, as well as the presence of uninvestigated wastes. The contaminants
remain in the subsurface at poorly defined concentrations and volumes. Future
development at the site should consider the potential for exposures to the
impacted soils and waste materials, soil vapors, and groundwater, as part of the
continuing obligations.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 1
1.0 INTRODUCTION
1.1 Site Description
Site Name North Temple Landfill (NTL)
Site Location/Address 6780 North Temple Frontage, Salt Lake City, Salt Lake
County, Utah
Land Area Approximately 769.85 acres
Site Improvements None
Anticipated Future Site
Use Redevelopment for commercial use
Reason for the ESA Acquiring the site
The location of the site is depicted on Exhibit 1 of Appendix A, which was reproduced
from a portion of the United States Geological Survey (USGS) 7.5-minute series
topographic map. The site and adjoining properties are depicted on the Site Diagram,
which is included as Exhibit 2 of Appendix A. Acronyms and terms used in this report are
described in Appendix F.
1.2 Scope of Services
This Phase I Environmental Site Assessment (ESA) was performed in accordance with
Terracon Proposal No. P61247234 dated July 26, 2024, and was conducted consistent
with the procedures included in ASTM E1527-21,Standard Practice for Environmental
Site Assessments: Phase I Environmental Site Assessment Process. The purpose of this
ESA was to assist the client in developing information to identify Recognized
Environmental Conditions (RECs) in connection with the site as reflected by the scope of
this report. Recognized environmental conditions are defined by ASTM E1527-21 as “(1)
the presence of hazardous substances or petroleum products in, on, or at the subject
property due to a release to the environment; (2) the likely presence of hazardous
substances or petroleum products in, on, or at the subject property due to a release or
likely release to the environment; or (3) the presence of hazardous substances or
petroleum products in, on, or at the subject property under conditions that pose a
material threat of a future release to the environment.” A de minimis condition is not a
recognized environmental condition.
This purpose was undertaken through user-provided information, a regulatory database
review, historical and physical records review, interviews (including local government
inquiries, as applicable), and a visual noninvasive reconnaissance of the site and
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 2
adjoining properties. Limitations, ASTM deviations, and significant data gaps (if
identified) are noted in the applicable sections of the report.
Review of Perfluoroalkyl and Polyfluoroalkyl Substances
Perfluoroalkyl and Polyfluoroalkyl Substances (PFAS) are a family of compounds which
are considered emerging contaminants of concern due to their mobility and longevity in
the environment. PFAS has been used in many products, including but not limited to
fire-fighting foam, anti-stick coatings, stain and water-repellent coatings, electroplating,
and paper products, among others. On July 8, 2024, EPA designated two PFAS
compounds, perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS),
including their salts and structural isomers, as hazardous substances under CERCLA;
accordingly, PFOA and PFOS was evaluated within the scope of ASTM E1527-21. Please
note that PFAS compounds are ubiquitous in the environment and this limited review is
not to be construed as confirmation that PFAS compounds are not present in, at or
under the site.
1.3 Standard of Care
This ESA was performed in accordance with generally accepted practices of this
profession, undertaken in similar studies at the same time and in the same geographical
area. We have endeavored to meet this standard of care, but may be limited by
conditions encountered during performance, a client-driven scope of work, or inability to
review information not received by the report date. Where appropriate, these limitations
are discussed in the text of the report, and an evaluation of their significance with
respect to our findings has been conducted.
Phase I ESAs, such as the one performed at this site, are of limited scope, are
noninvasive, and cannot eliminate the potential that hazardous, toxic, or petroleum
substances are present or have been released at the site beyond what is identified by
the limited scope of this ESA. In conducting the limited scope of services described
herein, certain sources of information and public records were not reviewed. It should be
recognized that environmental concerns may be documented in public records that were
not reviewed. No ESA can wholly eliminate uncertainty regarding the potential for RECs
in connection with a property. Performance of this practice is intended to reduce, but not
eliminate, uncertainty regarding the potential for RECs. No warranties, express or
implied, are intended or made. The limitations herein must be considered when the user
of this report formulates opinions as to risks associated with the site or otherwise uses
the report for any other purpose. These risks may be further evaluated—but not
eliminated—through additional research or assessment. We will, upon request, advise
you of additional research or assessment options that may be available and associated
costs.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 3
1.4 Additional Scope Limitations, ASTM Deviations, and Data
Gaps
Based upon the agreed-on scope of services, this ESA did not include subsurface or
other invasive assessments, vapor intrusion assessments or indoor air quality
assessments (i.e., evaluation of the presence of vapors within a building structure),
business environmental risk evaluations, or other services not particularly identified and
discussed herein. Credentials of the company (Statement of Qualifications) have not
been included in this report but are available upon request. Pertinent documents are
referred to in the text of this report, and a separate reference section has not been
included. Reasonable attempts were made to obtain information within the scope and
time constraints set forth by the client; however, in some instances, information
requested is not, or was not, received by the issuance date of the report. Information
obtained for this ESA was received from several sources that we believe to be reliable;
nonetheless, the authenticity or reliability of these sources cannot and is not warranted
hereunder. This ESA was further limited by the following:
During the site reconnaissance, portions of the site could not be observed due to
limited access, vegetation, and the amount of land included. Dirt roads were
driven and an overview from a high spot observed the majority of the site. Based
on other resources and knowledge of the site, this is not anticipated to be a
significant limitation.
An evaluation of the significance of limitations and missing information with respect to
our findings has been conducted, and where appropriate, significant data gaps are
identified and discussed in the text of the report. However, it should be recognized that
an evaluation of significant data gaps is based on the information available at the time
of report issuance, and an evaluation of information received after the report issuance
date may result in an alteration of our conclusions, recommendations, or opinions. We
have no obligation to provide information obtained or discovered by us after the
issuance date of the report, or to perform any additional services, regardless of whether
the information would affect any conclusions, recommendations, or opinions in the
report. This disclaimer specifically applies to any information that has not been provided
by the client.
This report represents our service to you as of the report date and constitutes our final
document; its text may not be altered after final issuance. Findings in this report are
based upon the site’s current utilization, information derived from the most recent
reconnaissance, and from other activities described herein; such information is subject
to change. Certain indicators of the presence of hazardous substances, petroleum
products or PFAS compounds may have been latent, inaccessible, unobservable, or not
present during the most recent reconnaissance and may subsequently become
observable (such as after site renovation or development). Further, these services are
not to be construed as legal interpretation or advice.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 4
1.5 Reliance
This ESA report is prepared for the exclusive use and reliance of Utah Inland Port
Authority (UIPA). Use or reliance by any other party is prohibited without the written
authorization of UIPA and Terracon Consultants, Inc. (Terracon).
Reliance on the ESA by the client and all authorized parties will be subject to the terms,
conditions, and limitations stated in the proposal, ESA report, and Terracon’s Agreement
for Services. The limitation of liability defined in the Agreement for Services is the
aggregate limit of Terracon’s liability to the client and all relying parties.
Continued viability of this report is subject to ASTM E1527-21 Section 4.6. If the ESA
will be used by a different user (third party) than the user for whom the ESA was
originally prepared, the third party must also satisfy the user’s responsibilities in Section
6 of ASTM E1527-21.
1.6 Client Provided Information
Prior to the site visit, Mona Smith, client’s representative, was asked to provide the
following user questionnaire information as described in ASTM E1527-21 Section 6.
Client Questionnaire Responses
Client Questionnaire Item Client Did
Not Respond
Client’s
Response
Yes No
Specialized Knowledge or Experience that is material to
a REC in connection with the site.
X
Actual Knowledge of Environmental Liens or Activity
Use Limitations (AULs) that may encumber the site.
X
Actual Knowledge of a Lower Purchase Price because
contamination is known or believed to be present at
the site.
N/A
Commonly Known or Reasonably Ascertainable
Information that is material to a REC in connection with
the site.
X
Obvious Indicators of Releases at the site.X
Ms. Mona Smith, representative for Utah Inland Port Authority (UIPA), completed a user
questionnaire dated November 19, 2024. According to her, the knowledge of the site is
based upon publicly available information. She stated that the site has known impacts,
and the price appropriately reflects that. Ms. Smith stated that UIPA has no independent
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 5
knowledge or experience regarding the site. Terracon’s consideration of the client
provided information coincides with RECs identified for the site and are further discussed
in Section 4.1. A copy of the questionnaire is included in Appendix C.
2.0 PHYSICAL SETTING
Physical Setting Information Source
Topography
Site Elevation Approximately 4,220 feet above sea level
USGS Topographic Map,
Bailey’s Lake, Utah
Quadrangle, 1997
(Appendix A)
Topographic
Gradient Very gently sloping towards the north
Closest
Surface Water
The West Branch Brighton canal transects
the site.
Soil Characteristics
Soil Type
Dumps
Jordan-Saltair complex, 0 to 1 percent
slopes
Lasil silt loam, 0 to 2 percent slopes
Terminal silt loam, 0 to 1 percent slopes
Salt Lake County, Utah
USDA-NRCS Web Soil
Survey
https://websoilsurvey
Accessed November 25,
2024Description
The majority of the site is listed as a
dump. The Jordan-Saltair, Lasil silt loam
and Terminal silt loam all have the same
landform of lake plains, parent material of
Lacustrine deposits, and the natural
drainage is somewhat poorly drained
Geology/Hydrogeology
Formation
Qh: Human disturbance (historical)
Qldy: Younger lacustrine and deltaic
deposits, Great Salt Lake (Holocene to
upper Pleistocene?)Utah Geological Survey
https://geology.utah.gov
Accessed November 25,
2024Description
Qh: Deposits and disturbed areas from
human development; includes some
Kennecott/Rio Tinto and other mining
operations, gravel pits and quarries, waste
management facilities, wastewater and
storm water ponds, the Grantsville
reservoir, motor sports area, and thicker
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 6
Physical Setting Information Source
fill for I-80 and its overpasses; also
mapped in several stacked units; laterally
extensive mine dumps, mine tailings, and
evaporation ponds are mapped separately
(see below); additional unmapped
disturbed areas and smaller fill deposits
are common throughout the map area;
thickness generally less than about 20
feet (6 m).
Qldy: Clay, silt, sand, and minor pebble
gravel deposited by the ancestral Jordan
River where it entered Great Salt Lake;
locally includes a loess mantle; form a
broad, gently sloping surface with some
channel remnants; exposed thickness less
than 10 feet (3 m).
Estimated
Depth to First
Occurrence of
Groundwater
Approximately 4–11 feet below ground
surface 2022 Airport West VCP,
Phase I Area Remedial
Action Plan, Utah DEQ*Hydrogeologic
Gradient North
* The groundwater flow direction and the depth to groundwater would likely vary depending
upon seasonal variations in rainfall and other hydrogeological features.
3.0 HISTORICAL USE INFORMATION
Terracon reviewed the following historical sources to develop a history of the previous
uses of the site and surrounding area, in order to help identify RECs associated with past
uses. Copies of selected historical documents are included in Appendix C.
3.1 Historical Topographic Maps, Aerial Photographs, and
Sanborn Maps
Readily available historical USGS topographic maps, selected historical aerial
photographs (at approximately 10-to-15-year intervals), and historical fire insurance
maps produced by the Sanborn Map Company were reviewed to evaluate land
development and obtain information concerning the history of development on and near
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 7
the site. Reviewed historical topographic maps, aerial photographs, and Sanborn maps
are summarized below.
Historical fire insurance maps produced by the Sanborn Map Company were requested
from ERIS to evaluate past uses and relevant characteristics of the site and surrounding
properties. Based upon inquiries to the above-listed Sanborn provider, Sanborn maps
were not available for the site.
Topographic maps:
o Saltair, Utah,1951,and 1972 (1:24,000)
o Bailey’s Lake, Utah,1997, 2017, and 2020 (1:24,000)
Aerial photographs: ERIS,1937, 1950, 1953, 1965, 1971, 1977, 1985,
1994, 2004, 2006, 2009, 2011, 2014, 2016,2018,and 2021 (1”=1,300’)
Historical Maps and Aerial Photographs
Direction Description
Site
Ponded water on the southwest side extending to the south-adjoining
property, canal transecting the site, vacant land and additional smaller
ponds observed (1937); undeveloped land, West Branch Brighton Canal
site from the southeast corner to the northwest corner and a canal along
the eastern and southern boundaries depicted (1950–1953); landfill cells
visible on the east side of the site, with active cells in the center (1965);
landfill cells visible throughout the majority of the site with active cells in
the northeast quadrant (1971); landfill cells observed and pond in the
southwestern portion, West Branch Brighton Canal, access road through
central portion depicted (1972); active cells on the west portion of the
site observed, pond in the southwest portion appears dry (1977); landfill
cells appear covered and the site does not appear to be an active landfill
(1985); tailings, access road, rail spur along eastern portion, West Branch
Brighton Canal depicted (1997); grading and disturbance that appears to
be associated with the placement of wastes from the NTL-E site that were
relocated to the site observed (1997–2006); ground disturbance in
southwest portion of site that appears to be from concrete debris and soil
associated with the development of City Creek observed (2009–2016);
several man-made pits, an access road, a canal transecting the site from
northwest corner to southeast portion and along the north, east, and
south boundaries, wetland vegetation along the southern portion, and rail
spur along the eastern boundary depicted (2017); landfill cells, access
roads, canal transecting the site, grading and disturbance in southwestern
portion observed (2018);
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 8
Direction Description
Site
(cont.)
several man-made pits, an access road, a canal transecting the site from
northwest corner to southeast portion and along the north, east, and
south boundaries, wetlands along the southern portion, landfill cells in the
eastern portion, and a rail spur along the eastern boundary depicted
(2020); landfill cells, Bonneville Landfill waste berm, access roads, canal
transecting the site, grading and disturbance in southwestern portion
observed (2021)
North
Undeveloped land (1937–2020); sections of undeveloped land, grading
and disturbance, substation, new roadways, and three warehouse
buildings observed (2021)
East
Undeveloped farmland observed (1937–1953); landfill cells are visible
(1971); railroad tracks east of site followed by landfill cells, a canal, and
farmland observed (1977–1985); vacant land observed (1994); the
Quality Distribution warehouse observed (2004–2009); Easton Archery in
the northern portion observed (2011–2017); Amazon warehouse to the
southeast built (2018-2020); development of Bureau of Land
Management Office building observed (2021)
South
Pond that extends north to the site, vacant land, and a road observed
(1937–1971); the pond at the southwest portion appears dry (1975–
1977); U.S. Interstate 80 expansion and developed ramp and frontage
road observed (1985–2021)
West
Undeveloped land (1937–2021); vacant land, road development followed
by grading and disturbance to the northwest associated with development
(2021)
Tailings were identified for the site on the 1997 topographic map. Based on the
regulatory review and known historical use of the site, the location of the tailings is
likely referring to the Bonneville Landfill Waste, and not mining tailings. The Bonneville
Landfill Waste is further discussed in Section 4.1.
3.2 Historical City Directories
The city directories used in this study were made available through ERIS (selected years
reviewed: 1925–2022) and were reviewed at approximate five-year intervals, if readily
available. City directories not available prior to 2000. The current street address for the
site was identified as 6780 North Temple Frontage, and a historical address for the site
was identified as 581 North John Glenn Road
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Historical City Directories
Direction Description
Site 6780 North Temple Frontage: No listing (1925–2022)
581 North John Glenn Road: No listing (1925–2022)
North
7902 West 700 North: No listing (1925–2022)
7026 West 700 North: No listing (1925–2022)
6942 West 700 North: No listing (1925–2022)
6934 West 700 North: No listing (1925–2022)
6904 West 700 North: No listing (1925–2022)
6792 West 700 North: No listing (1925–2022)
6628 West 700 North: No listing (1925–2022)
808 North 6550 West: No listing (1925–2022)
6338 West 700 North: No listing (1925–2022)
6210 West 700 North: No listing (1925–2022)
6180 West 700 North: No listing (1925–2022)
East
575 North John Glenn Road: No listing (1925–2012); Easton Salt Lake
Archery Center (2016–2022)
491 North John Glenn Road: No listing (1925–2016); Bureau of Land
Management (2022)
421 North John Glenn Road: No listing (1925–2003); Quality Carriers,
Quality Distribution, Spicers Paper (2008); Quality Distribution, Quality
Distribution Inc, Crown Packaging Corp (2012–2022)
355 North John Glenn Road: No listing (1925–2022)
South 6 North 7200 West: No listing (1925–2022)
15 North 7200 West: No listing (1925–2022)
West 7610 North Temple Frontage: No listing (1925–2022)
7420 North Temple Frontage: No listing (1925–2022)
3.3 Site Ownership
Based on a review of the Salt Lake County Assessors website, the site owner is School
and Institutional Trust Land Administration.
3.4 Title Search
At the direction of the client, a title search was included as part of the scope of services.
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County Deed Records were reviewed by Texas Environmental Research of Rockwall,
Texas to obtain a chain-of-title for the site. Ownership records were reviewed back to
1939. The title information is included in Appendix C.
Based on a review of the title provider’s research, the current site owner is School and
Institutional Trust Land Administration, who obtained title on March 1, 2018, from
Suburban Land Reserve Incorporated. Previous site owners include Suburban Land
Reserve LLC, Zions Securities Corporation, Property Reserve Incorporated, Corporate
Latter Day Saints Incorporated, and various private individuals.
3.5 Environmental Liens and Activity and Use Limitations
At the direction of the client, performance of a review of environmental liens and activity
and use limitations was included as part of the scope of services for which Terracon
engaged Texas Environmental Research of Rockwall, Texas. Based on a review of the
title provider’s research, environmental liens or activity and use limitations were not
identified. In addition, the ERIS regulatory database report included a review of both
Federal and State Engineering Control (EC) and Institutional Control (IC) databases.
Based on a review of the database report, the site was not listed on the EC or IC
databases.
3.6 Interviews Regarding Current and Historical Site Uses
The following individuals were interviewed regarding the current and historical use of the
site.
Interviews
Interviewer Name/Phone or
Email Title Date
Tina Cheney Kyle Pasley/
[phone] Managing Director November 22, 2024
Tina Cheney Gary McEntee/
[e-mail]
Principal, Ninigret
Construction November 20, 2024
Terracon contacted Mr. Kyle Pasley, Managing Director, SITLA, regarding environmental
concerns associated with the site. Mr. Pasley stated the site was acquired by SITLA in
approximately January 2018 as a donation from Suburban Land Reserve (SLR). He has
been familiar with the site since approximately 2020. Mr. Pasley stated remediation
activities in connection to the former use of the site as the North Temple Landfill have
been ongoing since 2018. Activities include lead scraping and characterization work as
outlined in the site Remedial Action Plan (RAP). The RAP is further discussed in Section
4.1. He stated that the metal impact area has been scrapped and is in a pile near the
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Bonneville Landfill repository. According to Mr. Pasley, the leachate system discussed in
the RAP is not in operation currently. Mr. Pasley also stated that in addition to the
ongoing remediation activities, further investigation and characterization was conducted.
Mr. Pasley stated that he is not aware of any pending lawsuits or administrative
proceedings in connection with the site.
Terracon interviewed Mr. Gary McEntee, Principal for Ninigret Construction, during the
site reconnaissance. Mr. McEntee has been familiar with the property since 2006. He
stated the City Creek waste concrete is on the southwest side of the site, and the
concrete will be crushed soon by Staker Parsons. The clay soils from City Creek have
been separated and are in a pile on the east side of 7200 West. He said the lead scape
from the former shooting range is complete; however, the cleanup will not be complete
until the windowed lead shot soil is incorporated into the new Phase I waste repository.
The lead scaped soil, approximately 12,000 cubic yards, is currently in a pile located
near the Bonneville Landfill repository.
3.7 Prior Report Review
Terracon requested the client provide any previous environmental reports they are
aware of for the site. Previous reports were provided by the client to Terracon for
review.
North Temple Landfill ESA
581 North John Glenn Road
Dated: February 9, 2018, Revised February 22, 2018
Prepared by: Terracon Consultants
For: Utah School & Institutional Trust Lands Administration (SITLA)
The Terracon February 22, 2018, North Temple Landfill ESA reported the site to consist
of approximately 769.85 acres of land (Salt Lake County Parcel Number 07-35-100-016-
0000), which was the former NTL. The ESA findings include the NTL identified as listed
on the CERCLIS/SEMS/Voluntary Cleanup Program (VCP)/Historical Solid Waste and
Landfill Facilities (HSWF), and above ground storage tank (AST) databases. The ESA
report stated that the ongoing presence of uninvestigated landfill wastes, the impacts to
soil from the historical use as a gun range, and the impacts to soil and groundwater
from the site’s historic use as a landfill represents a REC. In addition, the on-going
involvement in the VCP program, with associated site characterizations will likely identify
additional impacts that represent a REC.
The following recommendations were also provided:
Awareness of Continuing Obligation(s): All appropriate inquiry (AAI) establishes
landowner liability protections (LLPs) for property owners under CERCLA, as
innocent landowners, bona fide prospective purchasers, and/or contiguous property
owners. In order to use the LLPs under CERCLA, a purchaser must perform all
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appropriate inquiry (i.e., their due diligence) before acquiring the property.
Additionally, the EPA requires the purchaser to meet ongoing continuing obligations.
These continuing obligations are generally stated below.
compliance with any established environmental land use restrictions
take “reasonable steps” with respect to hazardous substance releases.
reasonable steps generally include the following: stop continuing releases,
prevent threatened future releases, and prevent or limit human, environmental,
or natural resource exposure to existing hazardous substance releases
provide full cooperation, assistance, and access to authorized personnel to
investigate the site
compliance with information requests and administrative subpoenas
providing legally required notices with respect to the discovery or release of any
hazardous substances at the facility
Based on the findings of this assessment, Terracon identified RECs for the site
associated with the releases of hazardous substances in the soils and groundwater on
the site, and with the presence of uninvestigated wastes. The contaminants remain in
the subsurface at poorly defined concentrations and volumes. Future development at the
site should consider the potential for exposures to the impacted soils and waste
materials, soil vapors, and groundwater, as part of the continuing obligations.
North Temple Landfill ESA
6780 North Temple Frontage
Dated: October 20, 2023
Prepared by: Terracon Consultants
For: Utah Inland Port Authority Crossroads Public Infrastructure District
The Terracon October 20, 2023, North Temple Landfill ESA, reported the site to consist
of approximately 769.85 acres of land (Salt Lake County previous Parcel ID of 07-35-
100-016-0000), which was the former NTL. The current site Parcel ID 07-35-100-020-
0000 acreage (765.06) appears to have decreased due to the establishment of a
roadway easement in the southeastern portion. Since the 2018 report, additional
investigations have taken place including the current work effort associated with the VCP
which includes excavation of test pits, leachate sampling collection, lead shot scraping,
and groundwater sampling. The waste within the landfill remains covered, with the
exception of scraped materials in the Phase I Area. The following RECs were identified:
Releases from the historical use of the site:The ongoing presence of landfill
wastes, the impacts to soil from the historical use as a gun range, and the
impacts to soil and groundwater from the site’s historical use as a landfill
represents a REC.
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On-going involvement in VCP Program: The historical use of the site and the
documented presence of hazardous substances in the soil and groundwater
represents a REC. In addition, the on-going involvement in the VCP program will
likely identify additional impacts that represent a REC.
Terracon’s recommendations remained similar to the 2018 report.
4.0 RECORDS REVIEW
Regulatory database information was provided by a contract information services
company. The purpose of the records review was to obtain sufficient information to
assist the environmental professional in determining if a REC, historical REC, controlled
REC, or a de minimis condition exists at the site in connection with the listing.
Information in this section is subject to the accuracy of the data provided by the
information services company and the date at which the information is updated. The
scope herein did not include confirmation of facilities listed as "unmappable" by
regulatory databases.
In some of the following subsections, the words up-gradient, cross-gradient, and down-
gradient refer to the topographic gradient in relation to the site. As stated previously,
the groundwater flow direction and the depth to shallow groundwater, if present, would
likely vary depending upon seasonal variations in rainfall and the depth to the
soil/bedrock interface. Without the benefit of on-site groundwater monitoring wells
surveyed to a datum, groundwater depth and flow direction beneath the site cannot be
directly ascertained.
4.1 Federal and State/Tribal Databases
Terracon reviewed standard federal, state, and tribal environmental record sources
within the approximate minimum search distances, as required by ASTME1527-21 and
presented in Table 2 of Section 8.0 (Types of Government Records to be Reviewed) in
the ASTM standard. Further, to enhance and supplement the standard environmental
record sources, Terracon reviewed additional federal, state, tribal, local, and proprietary
environmental record sources, provided by the database firm, if potentially useful and
reasonably ascertainable. Please refer to Appendix D (the environmental regulatory
database report) for the number of listings within each database reviewed and database
definitions and descriptions.
The following table summarizes the site-specific information provided by the database
and/or gathered by this office for identified facilities. Facilities are listed in order of
proximity to the site. Additional discussion for selected facilities follows the summary
table.
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December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 14
Listed Facilities
Facility Name and
Location
Estimated
Distance/
Direction/Gradient
Database Listings
Findings
Summary
North Temple Landfill
7200 West North
Temple
Site CERCLIS/SEMS/VCP/
HSWF/FINDS/FRS/C
ONTAM POTENTIAL
REC, based on
file review
discussed
below
Airport West VCP
581 North John Glenn
Road
Site VCP/RESPONSE REC, based on
file review
discussed
below
Bonneville Center
Landfill (a.k.a. North
Temple Landfill—East)
7200 West North
Temple
East-adjoining/
up-gradient
CERCLIS/CERLIS
NFRAP/
SEMS ARCHIVE/
No, based on
file review
discussed
below
Amazon.com Services
LLC—SUT1
6338 West 700 North
North-adjoining/
down-gradient
RCRA—SQG/TIER 2 No, based on
file review
discussed
below
Amazon.com Services
LLC SLC9
808 North 6550 West
North-adjoining/
down-gradient
RCRA—SQG/TIER 2 No, based on
file review
discussed
below
Amazon.com Services
LLC SLC3
355 John Glenn Road
East-adjoining/
down-gradient
RCRA—SQG/TIER 2 No, based on
file review
discussed
below
Valspar (Quality
Distribution)
421 John Glenn Road
East-adjoining/
up-gradient
RCRA-NonGen/
/PFAS IND
No, based on
file review
discussed below
Kennecott (North
Zone)
12000 West 2100
South
Approximately 600
feet/southwest/
cross-gradient
Proposed NPL/NPL
UT/CERCLIS/SEMS/
SUPERFUND ROD
No, based file
review
discussed below
Facilities | Environmental | Geotechnical | Materials 15
North Temple Landfill/CERCLA UTD000463489/VCP C046
The NTL is an approximately 770-acre landfill located just north of U.S. Interstate 80 (I-
80) on the site (between 5600 West and 7200 West). The landfill was operated by Salt
Lake City Corporation from the late 1950s until the late 1970s.
In 2006, Zions Securities signed a Voluntary Cleanup Program agreement with the Utah
Department of Environmental Quality (UDEQ). In 2007, Suburban Land Reserves (SLR)
signed a VCP agreement with DEQ as well.
According to Application and Agreement for VCP for the NTL, submitted by Zions
Securities in December 2005, the NTL was a repository for multitude of household and
industrial wastes disposed of at the landfill. No official manifest system existed
throughout the majority of the life of the landfill operations. The Preliminary Assessment
(DEQ, March 20, 1987) provided limited documentation on wastes placed in the landfill.
In addition, multiple borings and trenches have been completed in the landfill over the
years. In general wastes appear to be typical of landfills associated with large
municipalities in the era before the Resource Conservation and Reclamation Act.
Municipal wastes and some limited industrial/commercial wastes have been identified in
the investigations. In addition, a significant amount of construction debris was
reportedly thought to be placed on the site in the late 1970’s.
The site was investigated under CERCLA with a Preliminary Assessment (PA) conducted
in 1987 (UDEQ, March 20, 1987). The PA evaluated the NTL and the east adjacent NTL-E
site. The findings of the PA recommended further site investigation. The site
investigation included the installation of seven monitoring wells and the collection of
surface water and sediment sampled from the open channels surrounding the site.
Samples were analyzed for major cations and anions, heavy metals, volatile organic
compounds (VOCs), semi-volatile organic compounds (SVOCs), and pesticides. The draft
revised Analytical Results Report dated October 26, 1988, did not find any VOCs, and no
other contaminants of concern except arsenic and manganese in a down-gradient
monitoring well. The report recommended a Hazard Ranking Score be prepared to
determine if the site would score high enough to be on the National Priority List (NPL).
The report did note that no emergency response actions were necessary.
In 1995, 318,000 cubic yards of landfill debris was excavated from the adjoining NTL-E
site and placed on the southeast quadrant of the NTL. This material was capped and
remains at the site. From 2001 until 2005, a shotgun range operated in the southeast
quadrant of the site. The investigation of the range (CDM, April 26, 2010) for SLR in
2010 found the presence of lead shot was widespread and a significant mass of lead
pellets remain at the site, but concentrations of lead in the soil were all below 800
mg/kg and most were below 400 mg/kg. This area has been additionally investigated
and discussed under the VCP 92 below.
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In 2009, the Salt Lake Valley Health Department issued a permit to process construction
debris (clean concrete, brick, and soil) from the demolition of buildings associated with
the City Creek, Salt Lake City development. City Creek demolition material was
deposited in the southwest quadrant of the site, where it remains today. The permit was
closed in 2013.
Multiple soil and groundwater studies have been conducted since the late 1970s.
Currently there are three piezometers and nine monitoring wells around the perimeter of
the site. These investigations have found that subsurface consists of landfill debris
located in closed cells, covered with an average of two feet of fill. Debris is present in
some of the fill materials. Native soils consist of low permeable soils such as fine sands
and silts.
Groundwater flow is complex due to open channels surrounding the site and the West
Branch Brighton Canal that transects the site. These waterways act as groundwater
drains. In general, it appears the shallow unconfined groundwater flow is in a westerly
and northwesterly direction, but the groundwater may be influenced by the open
channels within the vicinity of the site.
The on-site wells have been sampled during several groundwater monitoring events
(2009-2021). Laboratory analysis has detected various VOCs, SVOCs, organochlorine
pesticides, metals (arsenic, lead, and barium), and gasoline range-petroleum
hydrocarbons (TPH-GRO) and diesel range-petroleum hydrocarbons (TPH-DRO) at the
site above project specific screening levels.
The Subsurface Investigation Report—Final (Cardno, June 1, 2016) included the
advancement of 13 borings for collection of soil and groundwater samples on the
adjoining property to the west of the NTL, near the western NTL perimeter. Four existing
piezometers and seven new monitoring wells were sampled. Samples were analyzed for
VOCs, SVOCs, TPH-GRO, TPH-DRO, metals, pesticides, and Polychlorinated Biphenyl
(PCBs). A subset of the groundwater samples was also analyzed for dioxins/furans. The
2016 Cardno investigation found no significant impact to soils above applicable
screening levels, although trace concentrations of several VOCs and TPH (GRO and DRO)
were identified at concentrations above the laboratory detection limits. The groundwater
sampling identified several VOC and SVOC constituent concentrations above screening
levels, and TPH (GRO and DRO) concentrations above DERR’s Initial Screen Levels
(ISLs).
VOCs identified at the site included: benzene: ethylbenzene; toluene; xylenes; 1,1-
dichloroethane; 1,1-dicholorethene; vinyl chloride; 1,2-dichlorobenzene; 1,4-
dichlorobenzene; 1,4-dioxane; acetone; chloroethane; chlorobenzene; chloromethane;
dichlorfluromethane; tetrahydrofuran; ethyl ether; isopropylbenzene; trans-1,2-
dichloroethene; and cis 1,2,-dichloroethene; however, only the benzene; vinyl chloride;
1,2-dichlorobenzene; and 1,1-dicholorethene were measured above their Maximum
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Concentration Levels (MCLs). Additionally, the following VOCs EPA Tap Water Screening
Levels: 1,1-dichloroethane and 1,4-dioxane.
Review of the SVOC results indicated the presence of benzaldehyde, bis (2-ethylhexyl)
phthalate, n-nitrosodiphenylamine, and 4-chloro-3-methylphenol. Only bis (2-
ethylhexyl) phthalate exceeded the MCL.
Review of the TPH-GRO and TPH-DRO data indicated the presence of TPH-GRO and TPH-
DRO in several of the monitoring wells. The data indicate that Utah’s ISL for TPH-DRO of
1.0 mg/L was exceeded at multiple locations along the west boundary of the site.
Arsenic, barium, chromium, lead, mercury, and selenium were common in the
groundwater samples submitted for analysis. A comparison of the concentrations to the
UDEQ Groundwater Protection Standards indicates arsenic and barium were the only
metals measured above their respective standards.
No pesticides were detected above their respective MCLs. However, beta-BHC
(hexachlorocyclohexane) was present in a single sample at concentrations above its Tap
Water Screening Level.
Review of the PCB results indicated no detection of constituents above the laboratory
reporting limits.
Dioxins and furans were detected in the groundwater in all four wells sampled; however,
none of the concentrations exceed EPA MCLs or Tap Water Screening Levels.
The Update on Utility Corridor Testing (RMEC, October 31, 2016) sampled soil and
groundwater samples at five locations immediately north of the NTL perimeter (one of
two potential corridor routes), and from an additional five borings approximately 0.25
miles farther north (along the second potential corridor route). This investigation did not
identify any constituents in soil at concentrations above screening levels. One
groundwater sample reported 1,1-dichloroethane, at a concentration of 9.42 ug/l that
was above its screening level of 2.8 ug/l; additionally, several VOC constituents were
detected at low concentrations above the laboratory reporting limits. The sample with
the elevated concentrations of 1,1-dichloroethane was collected from a boring
approximately mid-way between wells NTL-GW-04 and NTL-GW-06, on the north side of
the site. The RMEC investigation did not identify any other groundwater constituent
concentrations above screening levels except arsenic, nickel, and antimony, which were
generally discussed as being consistent with “elevated levels of naturally occurring
dissolved metals in groundwater.” This report was not present in DERR files and has not
been reviewed by DERR but was summarized in the Summary of Site Conditions
(Ninigret Group, 2016).
According to the UDEQ, the VCP application was terminated on June 4, 2019 due to the
opening of the Airport West VCP discussed below. Based on the known soil and
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groundwater impacts to the site and surrounding area, and the ongoing remedial
actions, the facility contributes to the RECs identified for the site.
Airport West VCP/ VCP C092
The Airport West VCP facility includes the former NTL. In 2018, SITLA submitted a VCP
application to the UDEQ, which was approved. Approximately 175 acres of the NTL (the
Phase I Area) is currently planned for landfill remediation. According to the Airport West
VCP Project Design and Contingency Plan (PDCP) dated November 8, 2022 and prepared
by Wasatch Environmental, the Phase I Area includes three areas including: 130 acres of
the former landfill containing buried municipal solid waste (MSW), 45 acres south of the
West Branch Brighton Canal that does not contain MSW, and 41 acres of land that will be
the location for the new repository to be constructed to receive MSW excavated from the
130 acres. The Bonneville Pile, waste previously located at the former NTL East Landfill,
is located within the Phase I Area. The Airport West VCP Project Design and Contingency
Plan stated that previous investigations conducted between 2018 and 2021 included
over one hundred investigative sample locations using wells, test pits and soil borings to
evaluate the waste cells and characterize the condition of the water and soil. It was
determined the waste within the Phase I Area is shallow, slightly above the groundwater
depth with minimal leachate. According to the PDCP, Asbestos Containing Material
(ACM), if any, will be deposited into an on-site repository. The Phase 1 Area 2021
Supplemental Investigation Report, dated August 2022 was also reviewed, and a portion
is included in Appendix C. The report discussed sampling results in soil, groundwater,
and the leachate operations. Arsenic was detected in the soil above the Project
Screening Level (PSL). Groundwater detected dissolved metals, TDS, VOCs and PFAS
above the PSLs. Test pit leachate detected dissolved metals, TDS, VOCs, SVOCs and
PFAS above their respective PSLs. Additionally, groundwater detected dissolved metals,
TDS, VOCs, and PFAS above the PSLs. Test pit leachate detected dissolved metals, TDS,
VOCs, SVOCs, and PFAS above their respective PSLs.
According to a letter dated November 17, 2021, NT Development used a drone to collect
weighted average methane emissions data for the site. The investigation concluded that
methane emissions did not exceed 80 parts per million (ppm), which is less than the 500
ppm EPA New Source Performance Standards (NSPS) threshold.
The 2019 Cardno Expanded Subsurface Investigation Results Report (ESI) dated
December 10, 2021, further characterized aquifer and soil conditions present on the site
and adjoining properties. According to the ESI, the report supplements previous
investigations, specifically to determine the extent and level of reported contaminants of
impacts along the western NTL boundary. According to the ESI, 66 groundwater samples
were collected including 30 offsite between 200-900 feet (downgradient); six along the
western boundary; five along the northern boundary; four along the southwest
boundary; three along the southeast boundary (upgradient); and seven new wells in the
eastern portion of the site (downgradient). Elevated concentrations of 1,4-dioxane and
Facilities | Environmental | Geotechnical | Materials 19
arsenic were detected throughout the onsite wells sampled, with highest concentrations
identified in the western perimeter and western perimeter interior wells. According to
the 2021 ESI, preliminary evaluations have identified the target groundwater
concentrations to be higher than levels which may pose an inhalation risk. The ESI
reported 1,1-dichloroethane was detected in two of the six wells of, one below the PSL
and one within the same order of magnitude as the PSL. Detection of the SVOC 1,1-
biphenyl was detected at the PSL in one of the wells, and the very northeast well
continues to show detection of vinyl chloride concentrations at the PSL. Soil gas samples
taken along the western perimeter and downgradient from the site exceeded regulatory
screen thresholds for residential and commercial indoor air risk exposures for benzene,
chloroform; 1,1-dichloroethane; and vinyl chloride. Elevated concentrations detected
offsite and downgradient include arsenic; 1,1,- DCA; and 1,4-dioxane. According to the
ESI, localized groundwater flow direction along the western boundary of the NTL, west of
the canal, was determined to be in a west to southwest direction. The eastern portion of
the site has a northerly flow direction. The variation in groundwater flow is anticipated to
be as a result of the West Branch of the Brighton Canal transecting the site.
The Airport West VCP—Phase I Area Remedial Action Plan (RAP), dated December 2022
was accepted by DERR as of December 6, 2022. The RAP includes odor control
measures, multiple components designed to minimize future impacts to area
groundwater, leachate treatment and disposal, an impermeable landfill cap, site access
controls, and additional groundwater mitigation and environmental control measures to
be implemented as the project advances.
The Airport West VCP Phase I RAP Shotgun Shooting Range report, dated October 11,
2023, conducted by Stantec was provided by the owner. The report provided XRF results
of the soil scraped for lead impacts in Phase I Area associated with the former shotgun
shooting range. Approximately 36 acres were scraped and placed near the Bonneville
Landfill repository.
Based on the known soil and groundwater impacts to the site and surrounding area, and
the ongoing remedial actions, the Airport West VCP facility represents a REC to the site.
Bonneville Center Landfill VCP/CERCLA UTD0009772106/VCP C010
The Bonneville Center Landfill, also known as the NTL-E, was an approximately 208-acre
landfill located immediately east of the site, that operated from the early 1950s until
1959. Site investigations suggest that the NTL-E was a dry landfill with one to four feet
of landfill waste material deposited in cells above the water table. The combined
NTL/NTL-E site was bisected by the Little Goggin Drain, which in general forms the
boundary of the site between the NTL and the NTL-E site.
As part of the site’s evaluation under CERCLA, both the NTL and the NTL-E were
evaluated under a single Preliminary Assessment (PA) in 1987. Following the PA, a site
investigation was conducted by the Utah Department of Health, Bureau of Solid and
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Hazardous Waste in 1988 (Analytical Results Report, 1988). Due to the low priority of
the site, the owner of the property, Zions Securities, removed the landfill debris from
the NTL-E site and stockpiled it on the adjacent NTL site, under the oversight of the Salt
Lake City/County Health Department. Following the relocation of the wastes and prior to
the redevelopment of the site, Zions Securities entered the site into Utah’s VCP
identifying the site as the Bonneville Center. The Bonneville Center VCP site was closed
in 2013.
In March, 2000, the Bonneville Center received a Certificate of Completion from the
DEQ, and in July 2000, the EPA archived the NTL-E site from the CERCLIS list. Although
the Certificate of Completion was in place, the Site Management Plan required ongoing
groundwater monitoring. As part of this monitoring, a plume of arsenic-impacted
groundwater was identified on the north side of the landfill (approximately 1,300 feet
north of the site), and low concentrations of chlorinated solvents were seen in a single
monitoring well along the north edge of the landfill. The well closest to the NTL (NTL-
GW-08) had low concentrations of arsenic that were slightly above MCLs. Following an
extended monitoring period, the plume was determined to be stable, and the UDEQ
provided a Second Amended and Restated Certificate of Completion dated August 29,
2013, removing the requirement for further groundwater monitoring.
The Restated Certificate of Completion acknowledged that a dissolved arsenic plume was
present that exceeded groundwater standards and that it did not represent a threat, as
long as the use of the remediated site complied with the Site Management Plan (SMP).
This SMP allows light commercial or industrial land use and prohibits the use of the
groundwater. According to Mr. Bill Rees, successful completion of the VCP resulted in a
portion of the site being issued a No Further Remedial Action Planned (NFRAP) status as
of March 22, 2000 with land use and water use restrictions remaining in place. According
to the UDEQ, the solid waste material, leachate, and lead contamination from a nearby
shooting range were the primary contaminants of concern. Remedial activity included
soil excavation and groundwater monitoring, as well as management under a site
management plan.
Based on the regulatory status of the facility, the Bonneville Center listing does not
represent a REC to the site.
Amazon.com Services LLC—SUT1/Amazon.com Services LLC—SLC9
The Amazon.com Services LLC—SUT1, a north-adjoining facilities were identified on the
RCRA-SQG and TIER 2 databases. Universal waste and D waste codes were listed as
generated on the property. There are no violations reported for the facility. Based on the
new development of the facility, types of waste generated, and gradient, the listing does
not represent a REC.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 21
Amazon.com Services LLC— SLC3
The Amazon.com Services LLC— SLC3, an east-adjoining facility, was identified on the
RCRA-SQG and TIER 2 databases. Universal waste and D waste codes were listed as
generated on the property. There are no violations reported for the facility. Based on the
new development of the facility, type of waste generated, and gradient, the listing does
not represent a REC.
Valspar (Quality Distribution)
This east-adjoining facility was identified on the RCRA NonGen and PFAS IND databases.
A letter dated November 1, 2006, from the EPA, acknowledges the notification of
regulated waste activity, as a small quantity generator with D001 (ignitable waste) and
D035 (methyl-ethyl ketone). There was also a notice of closure dated March 2008. The
UDEQ Division of Waste Management and Radiation Control was contacted for additional
information on the facility. According to the UDEQ, prior to 2009 US GreenFiber was
listed as the facility address occupant. Quality Distribution applied for a Tier 2
identification number in 2009; however as of July 28, 2023, they had not submitted any
reports. According to the EPA on July 21, 2023, the site is currently an active Universal
Waste generator. A violation or “undetermined” record was identified by ERIS for the
facility in April 2023; however, no other details were identified for the potential
violation. Based on the short duration of operations of hazardous waste, and the type of
waste this facility generated, the RCRA listing does not represent a REC. PFAS IND listed
facilities potentially handle PFAS based on their industrial profile, but are unconfirmed by
the EPA. Based on the PFAS sampling conducted as part of the VCP program on the site,
it's unlikely that PFAS, if used at the facility, is impacting the site, and is not considered
a REC.
Kennecott Operable Unit 22 (North Zone)
The Kennecott (North Zone) was identified by ERIS on the proposed NPL, NPL, SEMS,
CERCLIS and Superfund ROD databases. The facility is an industrial area at the north
end of the Oquirrh Mountains and at the south shore of the Great Salt Lake, west of Salt
Lake City, Utah. The closest operable unit to the site is the Great Salt Lake Wetlands
(OU22), approximately 600 feet south, southwest of the site. According to the EPA
Kennecott North Superfund Site 5-year review, since 1906 the Kennecott North Zone has
been used to process copper, lead, zinc, molybdenum, arsenic, gold, and silver-bearing
ores. The wastes produced contain hazardous substances, including heavy metals.
Sludge and soils were/are contaminated, as were/are surface and groundwater that
affect wetlands located between the smelting and refining operations and the south
shoreline of the Great Salt Lake. The main contaminant of concern in OU22 is selenium,
and arsenic. Based on distance and gradient, and ongoing site investigations, the
impacts from the Kennecott North Zone are not considered a REC to the site.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 22
The remaining facilities listed in the database report do not appear to represent RECs to
the site at this time based upon regulatory status, apparent topographic gradient,
and/or distance from the site.
Unmapped facilities are those that do not contain sufficient address or location
information to evaluate the facility listing locations relative to the site. The report listed
two facilities in the unmapped section. One of which is a SPILLS listing for an incident on
I-80 at about 7200 West (mile marker 110) which is potentially adjoining the site. The
report is from December 2012 when a truck crashed and spilled 20-25 gallons of diesel
fuel in the median. Environmental Remediation was dispatched for the spill and no
surface water was impacted. The other listing was not identified as the site or adjacent
properties.
4.2 Local Agency Inquiries
Agency Contacted/
Contact Method Response
Salt Lake County Health
Department/
https://saltlakecountyut.
nextrequest.com/requests/new
Terracon submitted an online written request for
records of environmental incidents and/or
hazardous materials identified for the site on
November 19, 2024. A response was received by
the Health Department on November 20, 2024.
Records of complaints and spills in the vicinity
were identified; however, the records are not
considered a REC to the site.
Salt Lake City Fire
Department/https://slcut.mycusthe
lp.com/
Terracon submitted an online written request for
records of environmental incidents and/or
hazardous materials identified for the site on
November 19, 2024. The fire department
responded on December 4, 2024 stating no
records were found for the site addresses.
Utah Department of Environmental
Quality (UDEQ), Utah
Environmental Interactive
Map/https://enviro.deq.utah.gov/
The Utah Department of Environmental Quality
maintains an online interactive map database of
regulatory facilities in the state. As of November
19, 2024, the site is listed on the website as the
Airport West, NTL, and the Bonneville Center
(NTL-E) VCP sites. Several Enforceable Written
Assurances (EWAs) were issued within the site
vicinity that included reasonable steps for
evaluation of vapor intrusion pathways and
mitigation of vapor intrusion pathways as
appropriate, due to possible impacts from the
NTL. The site listings are further discussed in
Section 4.1.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 23
Agency Contacted/
Contact Method Response
Salt Lake County
Assessor/https://slco.org/assessor/
The County maintains an online interactive map
database of parcel records. According to the
map, as of November 19, 2024, the site address
was identified as Salt Lake County Parcel ID 07-
35-100-020-0000 and consists of 765.06 acres.
Based on review of the parcel map, the acreage
discrepancy for the site parcel appears to be due
to the establishment of a roadway easement in
the southeastern portion of the site. For
purposes of this ESA, the easement was not
excluded from the site boundary.
5.0 SITE RECONNAISSANCE
5.1 General Site Information
Information contained in this section is based on a visual reconnaissance conducted
while walking through the site and the accessible interior areas of structures, if any,
located on the site. The site and adjoining properties are depicted on the Site Diagram,
which is included in Exhibit 2 of Appendix A. Photo documentation of the site at the time
of the visual reconnaissance is provided in Appendix B. Credentials of the individuals
planning and conducting the site visit are included in Appendix E.
General Site Information
Site Reconnaissance
Field Personnel Tina Cheney and Ellie Roubal
Reconnaissance Date November 20, 2024
Weather Conditions Sunny, 40 degrees Fahrenheit
Site Contact/Title Gary McEntee/Principal at Ninigret Construction (Owner
representative)
5.2 Overview of Current Site Occupants and Site Operations
The site is a former landfill. At the time of reconnaissance, no operations were
conducted.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 24
5.3 Site Observations
The following table summarizes site observations and interviews. Affirmative responses
(designated by an “X”) are discussed in more detail following the table.
Site Characteristics
Category Item or Feature
Observed
or
Identified
Site Operations,
Processes, and
Equipment
Emergency generators
Elevators
Air compressors
Hydraulic lifts
Dry cleaning
Photo processing
Ventilation hoods and/or incinerators
Waste treatment systems and/or water treatment
systems
Heating and/or cooling systems
Paint booths
Sub-grade mechanic pits
Wash-down areas or carwashes
Pesticide/herbicide production or storage
Printing operations
Metal finishing (electroplating, chrome plating,
galvanizing, etc.)
Salvage operations
Oil, gas, or mineral production
Other processes or equipment
Aboveground
Chemical or Waste
Storage
Aboveground storage tanks
Drums, barrels, and/or containers  5 gallons X
MSDS or SDS
Underground
Chemical or Waste
Underground storage tanks or ancillary UST
equipment
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 25
Category Item or Feature
Observed
or
Identified
Storage, Drainage
or Collection
Systems
Sumps, cisterns, French drains, catch basins, and/or
dry wells
Grease traps
Septic tanks and/or leach fields
Oil/water separators, clarifiers, sand traps, triple
traps, interceptors
Pipeline markers
Interior floor drains
Electrical
Transformers/PCBs
Transformers and/or capacitors
Other equipment
Releases or
Potential Releases
Stressed vegetation X
Stained soil
Stained pavement or similar surface
Leachate and/or waste seeps
Trash, debris, and/or other waste materials
Dumping or disposal areas X
Construction/demolition debris and/or dumped fill
dirt
Surface water discoloration, odor, sheen, and/or
free-floating product
Strong, pungent, or noxious odors
Exterior pipe discharges and/or other effluent
discharges
Other Notable Site
Features
Surface water bodies X
Quarries or pits
Wastewater lagoons
Wells X
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 26
Aboveground Chemical or Waste Storage
Drums, barrels, and/or containers  5 gallons
About a dozen 55-gallon drums that appeared to be in good condition were observed
during site reconnaissance. These were located near the office trailer in the southeastern
portion of the site. They were labeled as hazardous waste. Mr. McEntee reported these
drums contain granulated activated carbon media that were utilized as part of the
Leachate Treatment Pilot Study. No staining was observed within the vicinity of the
drums. Based on the observations made during the reconnaissance, the drums do not
represent a REC to the site.
Releases or Potential Releases
Stressed Vegetation
Around the center of the site, Terracon observed portions of thistle coverage that were
dark brown or black in color and seemingly dead. The site contact thought it was from a
possible brush fire; however, they were unaware of a reported fire.
Dumping or disposal areas
The site is a former landfill, as evidenced by hummocky terrain, the Bonneville Pile
berm, and the abundance of debris and fill material observed. Stockpiled soils
throughout the western and central portion of the site and piles of vegetation debris
north of the canal in the central portion of the site were also observed. Hazardous
substances were not observed at the surface of the stockpiled fill and vegetation debris
material. The former landfill is considered a REC to the site and is further discussed in
Section 4.1.
Other Notable Site Features
Surface water bodies
The West Branch Brighton Canal was observed transecting the site from southeast to
northwest. The canal was overgrown with vegetation and was bordered to the south by a
gravel access road, no water was observed in the canal. Hazardous materials were not
observed within the vicinity of the canal. The presence of the canal does not represent a
REC.
Wells
Several monitoring wells were observed across the site associated with the on-going VCP
investigations. The presence of the monitoring wells does not represent a REC; however,
the ongoing VCP investigation at the site is considered a REC. The regulatory status of
the site is further discussed in Section 4.1.
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Phase I Environmental Site Assessment
North Temple Landfill | Salt Lake City, Utah
December 5, 2024 | Terracon Project No. 61247234
Facilities | Environmental | Geotechnical | Materials 27
6.0 ADJOINING PROPERTY RECONNAISSANCE
Visual observations of adjoining properties (from site boundaries) are summarized
below.
Adjoining Properties
Direction Description
North 700 North followed by vacant land, substation, commercial
warehouses, Amazon warehouse
East Easton Archery, railroad lines, Bureau of Land Management West
Desert District, Quality Distribution/Global Xoom, Amazon warehouse
South North Temple Frontage Road followed by I-80 and vacant land
West Vacant land followed by Dura-Line
RECs were not observed with the adjoining properties.
7.0 ADDITIONAL SERVICES
Per the agreed scope of services specified in the proposal, additional services (asbestos
sampling, lead-based paint sampling, wetlands evaluation, lead in drinking water
testing, radon testing, vapor encroachment screening, etc.) were not conducted.
8.0 DECLARATION
I, Tina Cheney, declare that, to the best of my professional knowledge and belief, I meet
the definition of Environmental Professional as defined in Section 312.10 of 40 CFR 312;
and I have the specific qualifications based on education, training, and experience to
assess a property of the nature, history, and setting of the site. I have developed and
performed the All Appropriate Inquiries in conformance with the standards and practices
set forth in 40 CFR Part 312.
__________________________
Tina Cheney
ESA Group Manager
APPENDIX A
EXHIBIT 1: TOPOGRAPHIC MAP
EXHIBIT 2: SITE DIAGRAM

TOPOGRAPHIC MAP IMAGE COURTESY OF
THE U.S. GEOLOGICAL SURVEY
QUADRANGLES INCLUDE: BAILEYS LAKE, UT
(1/1/1997).
TOPOGRAPHIC MAP
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, UT
6952 S High Tech Dr Ste B
Midvale, UT 84047-3707

61247234
DIAGRAM IS FOR GENERAL LOCATION ONLY,
AND IS NOT INTENDED FOR CONSTRUCTION
PURPOSES
Project Manager:
Drawn by:
Checked by:
Approved by:
ER
TC
TC
TC
Ex. 1
Nov. 2024
Project No.
File Name:
Date:
1
Exhibit
1”=2,000’ Scale:
APPROXIMATE
SITE BOUNDARY

SITE DIAGRAM
6952 S High Tech Dr Ste B
Midvale, UT 84047-3707

61247234 AERIAL PHOTOGRAPHY PROVIDED BY
MICROSOFT BING MAPS
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, UT DIAGRAM IS FOR GENERAL LOCATION ONLY,
AND IS NOT INTENDED FOR CONSTRUCTION
PURPOSES
Project Manager:
Drawn by:
Checked by:
Approved by:
ER
TC
TC
TC
Ex. 2
Nov. 2024
Scale:
Project No.
File Name:
Date:
AS SHOWN 2
Exhibit
APPROXIMATE
SITE BOUNDARY Warehouse/
office
6792 W 700 N
Dura-Line
7591 W 700 N
Vacant
Amazon SLC3
355 John Glen
Eaton Archery
575 N. John Glen
Quality
Distribution
421 John Glen
Former
Bonneville
Landfill
Bonneville
Landfill
waste
74
0
0

W
e
s
t

400 North
700 North
North Temple Frontage 66
0
0

W
e
s
t

72
0
0

W
e
s
t

72
0
0

W
e
s
t

68
8
0

W
e
s
t

67
1
5

W
e
s
t

65
5
0

W
e
s
t

Rail spur
BLM Field Office
491 John Glenn
Rail spur
West Branch
Brighton Canal
City Creek
concrete
Wood
Debris
Lead
scraping
pile
Western Peaks,
Haines Jones &
Cadbury, SLC-GLC
6628 W 700 N
Amazon
SLC9
808 N.
6550 W.
Amazon
VUT1
6338 W.
700 N.
Drums

City Creek
materials
City Creek
materials
APPENDIX B
SITE PHOTOGRAPHS
Site Photographs
North Temple Landfill | Salt Lake City, Utah
Date Photos were taken: November 20, 2024 | Terracon Project No. 61247234

Facilities | Environmental | Geotechnical | Materials

Photo #1 View of the east entrance (6600
West), looking north.
Photo #2 View of the trailer near the eastern
entrance.

Photo #3 View of sandbags and 55-gallon
drums containing an ion-exchange media
associated with the leachate treatment.
Photo #4 View of fill pile, associated with the
lead scrape in Phase I Area.

Photo #5 View of the west entrance (7200
West), looking north.
Photo #6 Water spigot and trailer near the
west entrance.
Site Photographs
North Temple Landfill | Salt Lake City, Utah
Date Photos were taken: November 20, 2024 | Terracon Project No. 61247234

Facilities | Environmental | Geotechnical | Materials

Photo #7 View of City Creek debris materials
on the west side of the site.
Photo #8 View of additional City Creek
materials with clay material, that may have
impacts.

Photo #9 View of the concrete rubble from City
Creek on the southwest portion of the site.
Photo #10 View across the site, piles from the
leachate treatment observed.

Photo #11 View of Bonneville repository area,
and debris.
Photo #12 View of stressed vegetation, north of
the Bonneville repository area (in
the background).
Site Photographs
North Temple Landfill | Salt Lake City, Utah
Date Photos were taken: November 20, 2024 | Terracon Project No. 61247234

Facilities | Environmental | Geotechnical | Materials

Photo #13 Northwest corner of the site, looking
southeast.
Photo #14 View of north adjoining 700 North
and distribution warehouses.

Photo #15 View near the northeast corner,
looking south.
Photo #16 View of south adjoining frontage
road, following by Interstate 80.

Photo #17 View of west adjoining vacant land,
near the southwest corner of the site, looking
north.
Photo #18 View of west adjoining Dura-Line
facility, near the northwest corner of the site,
looking west.

APPENDIX C
HISTORICAL DOCUMENTATION AND USER
QUESTIONNAIRE
ASTM E1527-21 User Questionnaire
Facilities |Environmental | Geotechnical | Materials
Date Completed November 19, 2024
Person Completing Questionnaire Name:Mona Smith
Company:Utah Inland Port Authority (UIPA)
Phone:[phone]
Email:[e-mail]
Site Name North Temple Landfill
Site Address 6780 North Temple Frontage, Salt Lake City, Utah 84116
Point of Contact for Access Name:Gary McEntee
Company:Ninigret
Phone:[phone]
Email:[e-mail]
Access Restrictions or Special Site
Requirements?
___No _X_Yes (If yes, please explain)Please contact site owner and POC for Access.
Confidentiality Requirements?__No _X_Yes (If yes, please explain)Please refer to the related agreement.
Current Site Owner Name:Kyle Pasley
Company:School and Institutional Trust Lands
Administration (SITLA)
Phone:[phone]
Email:[e-mail]
Current Site Operator Name:Gary McEntee
Company:Ninigret
Phone:[phone]
Email:[e-mail]
Reasons for ESA (e.g.,financing, acquisition,
lease, etc.)
Acquisition
Anticipated Future Site Use Commercial/industrial
Relevant Documents?Please provide Terracon copies of prior Phase I or II ESAs, Asbestos Surveys, Environmental Permits
or Audit documents,Underground Storage Tank documents, Geotechnical Investigations, Site Surveys,
Diagrams or Maps, or other relevant reports or documents.
ASTM User Questionnaire
To qualify for one of the Landowner Liability Protections (LLPs)offered by the Small Business Liability Relief and Brownfields Revitalization Act of 2001 (the
“Brownfields Amendments”), the user must respond to the following inquiries required by 40 C.F.R. §§ 312.25, 312.28, 312.29, 312.30, and 312.31. These inquiries
must also be conducted by EPA Brownfield Assessment and Characterization grantees. The user should provide the following information to the environmental
professional. Failure to conduct these inquiries could result in a determination that “all appropriate inquiries” is not complete.
1) Did a search of land title records (or judicial records where appropriate) identify any environmental liens filed or recorded against the site under federal,
tribal, state, or local law (40 CFR 312.25)?
___No ___Yes (If yes, explain below and send Terracon a copy of the title records or judicial records reviewed.)
2) Did a search of land title records (or judicial records where appropriate) identify any activity and use limitations (AULs), such as engineering controls,
land use restrictions, or institutional controls that are in place at the site and/or have been filed or recorded against the site under federal, tribal, state, or
local law (40 CFR 312.26)?
___No ___Yes (If yes, explain below and send Terracon a copy of the title records or judicial records reviewed.)
3) Do you have any specialized knowledge or experience related to the site or nearby properties? For example, are you involved in the same line of
business as the current or former occupants of the site or an adjoining property so that you would have specialized knowledge of the chemicals and
processes used by this type of business (40 CFR 312-28)?
_X_No ___Yes (If yes, explain below)
4)Do you have actual knowledge of a lower purchase price because contamination is known or believed to be present at the site (40 CFR
312.29)?___No ___ Yes __X_ Not Applicable
5) Are you aware of commonly known or reasonably ascertainable information about the site that would help the environmental professional to identify
conditions indicative of releases or threatened releases (40 CFR 312.30)? For example, (a.) Do you know the past uses of the site? (b.) Do you know of
specific chemicals that are present or once were present at the site? (c.) Do you know of spills or other chemical releases that have taken place at the
site? (d.) Do you know of any environmental cleanups that have taken place at the site?
_X_No ___Yes (If yes, explain below)
6) Based on your knowledge and experience related to the site, are there any obvious indicators that point to the presence or likely presence of releases
at the site (40 CFR 312.31)?
_X__No ___Yes (If yes, explain below)
Comments or explanations:
Only knowledge regarding the site is based on publicly available information. As per publicly available records, the site has known impacts, and the price appropriately
reflects the property’s value. The Utah Inland Port Authority has no independent knowledge or experience regarding the site.
DATE:11-19-2024
TINA CHENEY
TERRACON
6952 S. HIGH TECH DRIVE, SUITE 100
MIDVALE, UT 84047
61247234 TASK 1
TEXAS ENVIRONMENTAL RESEARCH
126 SCEPTRE DRIVE TEL: (972) 772-4283
ROCKWALL, TEXAS 75032 FAX: (972) 772-4283
ENVIRONMENTAL AND OTHER ACTIVITY AND USE LIMITATION
(AUL) SEARCH
THE ATTACHED REPORT IS BEING PROVIDED TO APPLICANT SOLELY FOR THE
PURPOSE OF FACILITATING LANDOWNER OR PURCHASE DEFENSES WHICH MAY
BE AVAILABLE UNDER THE LIABILITY ACT OF 1980, AS AMENDED. IT IS
PROVIDED FOR THE SOLE USE AND BENEFIT OF APPLICANT AND MAY NOT BE
USED OR RELIED UPON BY ANY OTHER PARTY FOR ANY REASON.
NOTE: THIS SEARCH REPRESENTS SURFACE CONVEYANCES ONLY.
TOTAL LIABILITY OF TEXAS ENVIRONMENTAL RESEARCH COMPANY
IS LIMITED TO THE AMOUNT PAID FOR THIS REPORT.
THIS REPORT WAS PREPARED FOR THE PURPOSE OF ASSISTING IN AN
ENVIRONMENTAL HAZARD INSPECTION OF THE FOLLOWING DESCRIBED
PROPERTY.
LEGAL DESCRIPTION:PARCEL:07351000200000, NORTH TEMPLE LANDFILL,
6780 NORTHTEMPLE FRONTAGE STREET, SALT LAKE CITY, SALT LAKE COUNTY,
UTAH.
CURRENT OWNER:SCHOOL AND INSTITUTIONAL TRUST LAND ADMINISTRATION.
DATE : MARCH 1, 2018
INSTRUMENT: WARRANTY DEED
GRANTOR : SUBURBAN LAND RESERVE INCORPORATED
GRANTEE : SCHOOL AND INSTITUTIONAL TRUST LAND ADMINISTRATION
FILE NO. : 12725786
DATE :MARCH 5, 2013
INSTRUMENT: WARRANTY DEED
GRANTOR :SUBURBAN LAND RESERVE L.L.C.
GRANTEE :SUBURBAN LAND RESERVE INCORPORATED
FILE NO.:11589876
DATE :AUGUST 1, 2007
INSTRUMENT: WARRANTY DEED
GRANTOR :ZIONS SECURITIES CORPORATION
GRANTEE :SUBURBAN LAND RESERVE L.L.C.
FILE NO. :10180374
61247234 TASK 1 (1)
DATE : JULY 19, 1999
INSTRUMENT: WARRANTY DEED
GRANTOR :PROPERTY RESERVE INCORPORATED
GRANTEE :ZIONS SECURITIES CORPORATION
FILE NO.:7415986
DATE :DECEMBER 18, 1972
INSTRUMENT: WARRANTY DEED
GRANTOR :CORPORATE LATTER DAY SAINTS INCORPORATED
GRANTEE :PROPERTY RESERVE INCORPORATED
FILE NO.:3928439
DATE :MAY 23, 1970
INSTRUMENT: WARRANTY DEED
GRANTOR :LATTER DAY SAINTS
GRANTEE :CORPORATE LATTER DAY SAINTS INCORPORATED
FILE NO.:6149725
DATE : JANUARY 18, 1956
INSTRUMENT: WARRANTY DEED
GRANTOR :DOUGLAS H. BURMIESTER, ET AL
GRANTEE :LATTER DAY SAINTS
FILE NO.:2531614
61247234 TASK 1 (2)
DATE :OCTOBER 24, 1945
INSTRUMENT: WARRANTY DEED
GRANTOR :BRANN D. LEHMAN AND SPOUSE, JANET LEHMAN
GRANTEE :DOUGLAS H. BURMIESTER, ET AL
FILE NO.:9417283
DATE :JUNE 23, 1939
INSTRUMENT: WARRANTY DEED
GRANTOR :JAMES L. SULLBERGER AND SPOUSE, KAREN SULLBERGER
GRANTEE :BRANN D. LEHMAN AND SPOUSE, JANET LEHMAN
FILE NO.:7386148
EASEMENTS : UTILITY EASEMENT.
Prepared by Texas Environmental Research on 11-19-2024.
NOTE: 7-19-1999, WATER RIGHTS WERE ASSIGNED TO ZIONS SECURITIES CORPORATION
7415988.
61247234 TASK 1 (3)
ENVIRONMENTAL LIEN AND OTHER ACTIVITY AND USE
LIMITATIONS SEARCH
AFTER COMPLETING AN ENVIRONMENTAL LIEN AND OTHER
ACTIVITY AND USE LIMITATIONS SEARCH A FINDING THAT NO
ENVIRONMENTAL LIENS OR AUL’S HAVE BEEN FILED OF PUBLIC
RECORD AND THAT IT HAS BEEN DETERMINED THAT THE
PROPERTY RESEARCHED IN THIS REPORT COMPLIES WITH ASTM E
1527-21-SEC.8.3.4.9 AND SECTION 6.2
THIS REPORT MEETS OR EXCEEDS A.S.T.M. E 1527-21.
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
Project Property:
Project No:
Requested By:
Order No:
Date Completed:
North Temple Landfill
6780 North Temple Frontage
Salt Lake City UT 84116
61237231
Terracon
23071100100
July 11, 2023
Topographic Map Symbology for the maps may be available in the following documents:
Pre-1947
1947-2009
2009-present
Topographic Maps included in this report are produced by the USGS and are to be used for research purposes including a phase I report.
Maps are not to be resold as commercial property.
No warranty of Accuracy or Liability for ERIS: The information contained in this report has been produced by ERIS Information Inc.(in the US)
and ERIS Information Limited Partnership (in Canada), both doing business as 'ERIS', using Topographic Maps produced by the USGS.
This maps contained herein does not purport to be and does not constitute a guarantee of the accuracy of the information contained herein.
Although ERIS has endeavored to present you with information that is accurate, ERIS disclaims, any and all liability for any errors, omissions,
or inaccuracies in such information and data, whether attributable to inadvertence, negligence or otherwise, and for any consequences
arising therefrom. Liability on the part of ERIS is limited to the monetary value paid for this report.
Page 223 of 1918 Topographic Instructions
Page 130 of 1928 Topographic Instructions
Topographic Map Symbols
US Topo Map Symbols
We have searched USGS collections of current topographic maps and historical topographic
maps for the project property. Below is a list of maps found for the project property and
adjacent area. Maps are from 7.5 and 15 minute topographic map series, if available.
Year Map Series

1951 7.5
1972 7.5
1997 7.5
2017 7.5
2020 7.5
QU ADRAN GLES INCLUDE: Saltair, UT(1-1951), (7.5 Min Series, 1951).
TOPOGRAPHIC MAP IMAGE COURTESY OF THE U.S. GEOLOGIC SURVEY
Project Manager:
Drawn By:
Checked By:
Approved By:
Project No:
Scale:
File Name:
Date:
TOPOGRAPHIC MAP (1951)61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
QU ADRAN GLES INCLUDE: Saltair, UT(1-1972), (7.5 Min Series, 1972).
TOPOGRAPHIC MAP IMAGE COURTESY OF THE U.S. GEOLOGIC SURVEY
Project Manager:
Drawn By:
Checked By:
Approved By:
Project No:
Scale:
File Name:
Date:
TOPOGRAPHIC MAP (1972)61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
QU ADRAN GLES INCLUDE: Baileys Lake, U T(1-1997), (7.5 Min Series, 1997).
TOPOGRAPHIC MAP IMAGE COURTESY OF THE U.S. GEOLOGIC SURVEY
Project Manager:
Drawn By:
Checked By:
Approved By:
Project No:
Scale:
File Name:
Date:
TOPOGRAPHIC MAP (1997)61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
QU ADRAN GLES INCLUDE: Baileys Lake, U T, (7.5 Min Series, 2017).
TOPOGRAPHIC MAP IMAGE COURTESY OF THE U.S. GEOLOGIC SURVEY
Project Manager:
Drawn By:
Checked By:
Approved By:
Project No:
Scale:
File Name:
Date:
TOPOGRAPHIC MAP (2017)61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
QU ADRAN GLES INCLUDE: Baileys Lake, U T, (7.5 Min Series, 2020).
TOPOGRAPHIC MAP IMAGE COURTESY OF THE U.S. GEOLOGIC SURVEY
Project Manager:
Drawn By:
Checked By:
Approved By:
Project No:
Scale:
File Name:
Date:
TOPOGRAPHIC MAP (2020)61237231
1" = 1300'
23071100100
2023-07-12
6949 S High Tech Dr Suite 100
Midvale, Utah 84047-3705
North Temple Landfill
6780 North Temple Frontage
Salt Lake City, Utah 84116
Appendix
C
P ro ject P ro perty:North Te m ple Landfil l
6780 N ort h T e m pl e Frontage
Sal t Lake Ci ty,UT 84116
P ro ject No:61237231
Requ ested By:T e rracon
O rder No :23071100100
D ate C o mp leted:Jul y 14, 2023
Ju l y 1 4 , 2 0 2 3
RE: CI TY D I REC TO RY RESEARCH
6 7 8 0 No r th Temp l e Fr o nta ge
S a l t La ke Ci ty ,UT 8 4 1 1 6
Th a n k yo u fo r c on ta c ti n g ERI S fo r a n C i ty D i r ec to r y S ea r c h fo r the s i te des c r i b ed a b o v e. O ur s ta ff h a s c on d u c ted a
r ever s e l i s ti n g C i ty Di r ec to r y s ea r c h to deter mi n e p r i o r o c c u p a nts o f th e s u b j ec t s i te a n d a d j a c en t p r op er ti es . W e
h a ve pr o v i d ed the nea r es t a d d r es s es (s ) wh en a d j a c en t a d d r es s es a r e no t l i s ted . I f we h a v e s ea r c h ed a r a n ge o f
a d d r es s es , a l l a d d r es s es i n tha t r a n ge fo u n d i n th e D i r ec to r y a r e i n c l u d ed .
No te: Rever s e Li s ti n g Di r ec tor i es gen er a l l y a r e fo c u s ed o n mo r e h i ghl y d evel op ed a r ea s . Newl y d ev el o p ed a r ea s ma y
b e c o ver ed i n th e mo r e r ec en t yea r s , b u t th e o l d er d i r ec to r i es wi l l ten d to c o ver o n l y th e "c en tr a l " p a r ts of th e c i ty. To
c o mp l ete th e s ea r c h , we h a ve ei th er u ti l i zed th e ACP L, Li b r a r y o f Con gr es s , Sta te Ar c hi v es , a n d /o r a r egi o n a l l i b r a r y
o r h i s tor y c enter a s wel l a s mu l ti pl e d i gi ti zed d i r ec to r i es . Th es e d o n o t c l a i m to b e a c ompl ete c o l l ec ti on of a l l
r ever s e l i s ti n g c i ty d i r ec to r i es p r o d u c ed .
ER I S h a s ma d e ev er y effo r t to p r ovi d e a c c u r a te a n d c o mp l ete i n for ma ti o n b u t s ha l l n ot b e h el d l i a bl e for mi s s i n g,
i n c o mp l ete o r i n a c c ur a te i n for ma ti o n . To c o mp l ete th i s s ea r c h we u s ed th e gen er a l r a n ge(s ) b el o w to s ea r c h fo r
r el eva n t fi n d i n gs . I f you bel i ev e th er e a r e a d d i ti on a l a d d r es s es o r s tr eets tha t r equ i r e s ea r c h i n g p l ea s e c o n ta c t u s a t
8 6 6 -5 1 7 -5 2 0 4 .
S ear c h Cr it er ia:
Al l of John Gl enn R d
Al l of N 7200 W
Al l of N Temple Fronta g e
6330-7595 of W 700 N
S ear c h N o t es:
S earc h Resu lt s S u m mary
Dat e So u r ce Com m e n t
2022 DIGITAL BUSIN ESS DIRECTORY
2020 DIGITAL BUSIN ESS DIRECTORY
2016 DIGITAL BUSIN ESS DIRECTORY
2012 DIGITAL BUSIN ESS DIRECTORY
2008 DIGITAL BUSIN ESS DIRECTORY
2003 DIGITAL BUSIN ESS DIRECTORY
2000 DIGITAL BUSIN ESS DIRECTORY
1995-96 COLE
1991 COLE
1986 COLE
1981 COLE
1976 COLE
1973 COLE
1969-70 COLE
1965 POLKS
1959 POLKS
1955 POLKS
1949 POLKS
1944 POLKS
1940 POLKS
1935 POLKS
1931 POLKS
1925 POLKS
2 0 22 JO HN GL E N N RD
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 2 2 N 7200 W
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 3 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
346 EXEL LOGISTICS...L OGIS TICS
350 1 800 CONTACTS...C ONTA C T L E NS E S
350 EXPEDITORS INTERNATIONAL...TRU C K INGM OTOR FRE IGHT
350 EXPEDITORS INTERNATIONAL...FRE IGH T-FOR W A RD IN G
350 VICTORY PACKAGING INC...P A C K A GIN G S E RV IC E
421 CROWN PACKAGING CORP...B E V E R A GE S (W HL S )
421 QUALITY DISTRIBUTION...TRU C K ING-L IQU ID & D RY B UL K
421 QUALITY DISTRIBUTION INC...TR U CK IN G-M OTOR FR E IGHT
421 QUALITY DISTRIBUTION INC...TR U CK IN GH E A V Y HA U L IN G
491 BUREAU LAND MANAGEMENT...S TA TE GOV E R NM E NTCON S E R V A TION D E P TS
491 BUREAU LAND MANAGEMENT...GOV E R NM E NT OFFICE S -U S
575 EASTON SALT LAKE ARCHERY CTR...S P OR TS & R E CR E A TION INS TR U CTION
NO LISTING FOUND
2 0 22 N TEMP LE FRO N TA GE
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 2 2 W 700 N
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 4 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
NO LISTING FOUND NO LISTING FOUND
2 0 20 JO HN GL E N N RD
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 2 0 N 7200 W
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 5 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
346 EXEL LOGISTICS...L OGIS TICS
350 1 800 CONTACTS...C ONTA C T L E NS E S
350 EXPEDITORS INTERNATIONAL...TRU C K INGM OTOR FRE IGHT
350 EXPEDITORS INTERNATIONAL...FRE IGH T-FOR W A RD IN G
350 VICTORY PACKAGING INC...P A C K A GIN G S E RV IC E
421 CROWN PACKAGING CORP...B E V E R A GE S (W HL S )
421 QUALITY DISTRIBUTION...TRU C K INGM OTOR FRE IGHT
421 QUALITY DISTRIBUTION...TRU C K ING-L IQU ID & D RY B UL K
421 QUALITY DISTRIBUTION INC...TR U CK IN GH E A V Y HA U L IN G
421 QUALITY DISTRIBUTION INC...TR U CK IN G-M OTOR FR E IGHT
575 EASTON SALT LAKE ARCHERY CTR...S P OR TS & R E CR E A TION INS TR U CTION
NO LISTING FOUND
2 0 20 N TEMP LE FRO N TA GE
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 2 0 W 700 N
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 6 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
NO LISTING FOUND NO LISTING FOUND
2 0 16 JO HN GL E N N RD
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 1 6 N 7200 W
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 7 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
421 CROWN PACKAGING CORP...B E V E R A GE S (W HL S )
421 QUALITY DISTRIBUTION INC...TR U CK IN G-M OTOR FR E IGHT
575 EASTON SALT LAKE ARCHERY CTR...S P OR TS & R E CR E A TION INS TR U CTION
620 COMPEQ INTERNATIONAL CORP...E L E CTRIC E QUIP M E NT & S UP P L IE S -
W H OL E S A LE
NO LISTING FOUND
2 0 16 N TEMP LE FRO N TA GE
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 1 6 W 700 N
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 8 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
NO LISTING FOUND NO LISTING FOUND
2 0 12 JO HN GL E N N RD
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 1 2 N 7200 W
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 9 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
421 CROWN PACKAGING CORP...B E V E R A GE S (W HL S )
421 QUALITY DISTRIBUTION INC...TR U CK IN G-L IQU ID & DR Y B U LK
550 PAPA PITA BAKERY...B RE A D/OTHE R B A K E R Y P R OD-E X C OOK IE S
620 COMPEQ INTERNATIONAL CORP...P RIN TE D & E TC HE D CIRC U ITS -M FR S
NO LISTING FOUND
2 0 12 N TEMP LE FRO N TA GE
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 1 2 W 700 N
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 10 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
NO LISTING FOUND NO LISTING FOUND
2 0 08 JO HN GL E N N RD
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 0 8 N 7200 W
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 11 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
421 QUALITY CARRIERS INC...TR UC K IN G-L IQUID & D R Y B U LK
421 QUALITY DISTRIBUTION INC...TR U CK IN G
421 SPICERS PAPER...S TA TION E RY S TOR E S
550 PAPA PITA BAKERY...B RE A D,RE L B A K E D P DT
550 PAPA PITA BAKERY...B A K E RS -W H OL E S A L E
620 COMPEQ INTERNATIONAL CORP...M FG OF P R IN TE D CIR C UIT B OA R DS
620 COMPEQ INTERNATIONAL CORP...P RIN TE D C IR CU IT B D S
NO LISTING FOUND
2 0 08 N TEMP LE FRO N TA GE
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 0 8 W 700 N
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 12 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
NO LISTING FOUND NO LISTING FOUND
2 0 03 JO HN GL E N N RD
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 0 3 N 7200 W
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 13 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
550 PAPA PITA BAKERY...P E T FOOD S
620 COMPEQ INTERNATIONAL
NO LISTING FOUND
2 0 03 N TEMP LE FRO N TA GE
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 0 3 W 700 N
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 14 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
NO LISTING FOUND NO LISTING FOUND
2 0 00 JO HN GL E N N RD
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 0 0 N 7200 W
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 15 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
550 PAPA PITA BAKERY...P E T FOOD S
620 COMPEQ INTERNATIONAL
NO LISTING FOUND
2 0 00 N TEMP LE FRO N TA GE
SOURCE: DIGITAL BUSINESS DIRECTORY
2 0 0 0 W 700 N
SOURCE: DIGITAL BUSINESS DIRECTORY
Page: 16 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
NO LISTING FOUND NO LISTING FOUND
1 9 95 -9 6 JO HN GL E N N RD
SOURCE: COLE
1 9 9 5-96 N 7200 W
SOURCE: COLE
Page: 17 Report ID: 23071100100 - 07/14/2023
www.erisinfo.com
620 COMPEQ INTL CO LTD STREET NOT LISTED
Project Property:
Project No:
Requested By:
Order No:
Date Completed:
North Temple Landfill
6780 North Temple Frontage
Salt Lake City UT 84116
61237231
Terracon
23071100100
July 11, 2023
Please note that no information was found for your site or adjacent properties.
APPENDIX D
ENVIRONMENTAL DATABASE INFORMATION
Project Property:North Temple Landfill
6780 North Temple Frontage
Salt Lake City UT 84116
Project No:61247234
Report Type:Database Report
Order No: 24111900057
Requested by:Terracon Consultants, Inc.
Date Completed: November 20, 2024
2 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Table of Contents
Notice:IMPORTANT LIMITATIONS and YOUR LIABILITY
Reliance on information in Report:This report DOES NOT replace a full Phase I Environmental Site Assessment but is solely intended to be used as
database review of environmental records.
License for use of information in Report:No page of this report can be used without this cover page,this notice and the project property identifier.
The information in Report(s)may not be modified or re-sold.
Your Liability for misuse:Using this Service and/or its reports in a manner contrary to this Notice or your agreement will be in breach of copyright and
contract and ERIS may obtain damages for such mis-use,including damages caused to third parties,and gives ERIS the right to terminate your account,
rescind your license to any previous reports and to bar you from future use of the Service.
No warranty of Accuracy or Liability for ERIS:The information contained in this report has been produced by ERIS Information Inc.("ERIS")using
various sources of information,including information provided by Federal and State government departments.The report applies only to the address and
up to the date specified on the cover of this report,and any alterations or deviation from this description will require a new report.This report and the
data contained herein does not purport to be and does not constitute a guarantee of the accuracy of the information contained herein and does not
constitute a legal opinion nor medical advice.Although ERIS has endeavored to present you with information that is accurate,ERIS disclaims,any and
all liability for any errors,omissions,or inaccuracies in such information and data,whether attributable to inadvertence,negligence or otherwise,and for
any consequences arising therefrom.Liability on the part of ERIS is limited to the monetary value paid for this report.
Trademark and Copyright:You may not use the ERIS trademarks or attribute any work to ERIS other than as outlined above.This Service and Report
(s)are protected by copyright owned by ERIS Information Inc.Copyright in data used in the Service or Report(s)(the "Data")is owned by ERIS or its
licensors.The Service,Report(s)and Data may not be copied or reproduced in whole or in any substantial part without prior written consent of ERIS.
Table of Contents
Table of Contents...........................................................................................2
Executive Summary........................................................................................3
Executive Summary: Report Summary.......................................................................................................................4
Executive Summary: Site Report Summary - Project Property...................................................................................8
Executive Summary: Site Report Summary - Surrounding Properties........................................................................9
Executive Summary: Summary by Data Source.......................................................................................................12
Map...............................................................................................................19
Aerial.............................................................................................................22
Topographic Map..........................................................................................23
Detail Report.................................................................................................24
Unplottable Summary.................................................................................152
Unplottable Report......................................................................................153
Appendix: Database Descriptions...............................................................154
Definitions...................................................................................................169
3 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Executive Summary
Property Information:
Project Property:North Temple Landfill
6780 North Temple Frontage Salt Lake City UT 84116
Project No:61247234
Coordinates:
Latitude:40.7778563
Longitude:-112.05311744
UTM Northing:4,514,630.92
UTM Easting:411,133.77
UTM Zone:12T
Elevation:4,225 FT
Order Information:
Order No:24111900057
Date Requested:November 19, 2024
Requested by:Terracon Consultants, Inc.
Report Type:Database Report
Historicals/Products:
ERIS Xplorer ERIS Xplorer
Excel Add-On Excel Add-On
terraDOCS Report terraDOCS (Terracon)
Executive Summary
4 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Executive Summary: Report Summary
Database Searched Search
Radius
Project
Property
Within
0.12mi
0.125mi
to 0.25mi
0.25mi to
0.50mi
0.50mi to
1.00mi
Total
Standard Environmental Records
Federal
rr-NPL-aa Y 1 0 0 0 0 0 0

rr-PROPOSED NPL-aa Y 1 0 1 0 0 0 1

rr-DELETED NPL-aa Y 0.5 0 0 0 0 - 0

rr-SEMS-aa Y 0.5 1 0 0 1 - 2

rr-ODI-aa Y 0.5 0 0 0 0 - 0

rr-SEMS ARCHIVE-aa Y 0.5 1 0 0 0 - 1

rr-CERCLIS-aa Y 0.5 2 0 0 1 - 3

rr-IODI-aa Y 0.5 0 0 0 0 - 0

rr-CERCLIS NFRAP-aa Y 0.5 1 0 0 0 - 1

rr-CERCLIS LIENS-aa Y PO 0 ---- 0

rr-RCRA CORRACTS-aa Y 1 0 0 0 0 0 0

rr-RCRA TSD-aa Y 0.5 0 0 1 0 - 1

rr-RCRA LQG-aa Y 0.25 0 0 0 -- 0

rr-RCRA SQG-aa Y 0.25 0 3 2 -- 5

rr-RCRA VSQG-aa Y 0.25 0 0 0 -- 0

rr-RCRA NON GEN-aa Y 0.25 0 1 0 -- 1

rr-RCRA CONTROLS-aa Y 0.5 0 0 0 0 - 0

rr-FED ENG-aa Y 0.5 0 0 0 0 - 0

rr-FED INST-aa Y 0.5 0 0 0 0 - 0

rr-LUCIS-aa Y 0.5 0 0 0 0 - 0

rr-NPL IC-aa Y 0.5 0 0 0 0 - 0

rr-ERNS 1982 TO 1986-aa Y PO 0 ---- 0

rr-ERNS 1987 TO 1989-aa Y PO 0 ---- 0

rr-ERNS-aa Y PO 0 ---- 0

rr-FED BROWNFIELDS-aa Y 0.5 0 0 0 0 - 0

rr-FEMA UST-aa Y 0.25 0 0 0 -- 0

rr-FRP-aa Y 0.25 0 0 0 -- 0

NPL
PROPOSED NPL
DELETED NPL
SEMS
ODI
SEMS ARCHIVE
CERCLIS
IODI
CERCLIS NFRAP
CERCLIS LIENS
RCRA CORRACTS
RCRA TSD
RCRA LQG
RCRA SQG
RCRA VSQG
RCRA NON GEN
RCRA CONTROLS
FED ENG
FED INST
LUCIS
NPL IC
ERNS 1982 TO 1986
ERNS 1987 TO 1989
ERNS
FED BROWNFIELDS
FEMA UST
FRP
Executive Summary: Report Summary
5 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Database Searched Search
Radius
Project
Property
Within
0.12mi
0.125mi
to 0.25mi
0.25mi to
0.50mi
0.50mi to
1.00mi
Total
rr-DELISTED FRP-aa Y 0.25 0 0 0 -- 0

rr-HIST GAS STATIONS-aa Y 0.25 0 0 0 -- 0

rr-REFN-aa Y 0.25 0 0 0 -- 0

rr-BULK TERMINAL-aa Y 0.25 0 0 0 -- 0

rr-SEMS LIEN-aa Y PO 0 ---- 0

rr-SUPERFUND ROD-aa Y 1 0 0 0 1 0 1

rr-DOE FUSRAP-aa Y 1 0 0 0 0 0 0

State
rr-NPL UT-aa Y 1 0 0 0 1 0 1

rr-CONTAM POTENTIAL-aa Y 0.5 1 0 0 0 - 1

rr-SWF/LF-aa Y 0.5 0 0 0 0 - 0

rr-HSWF-aa Y 0.5 1 0 0 0 - 1

rr-LUST-aa Y 0.5 0 0 0 1 - 1

rr-LAST-aa Y 0.5 0 0 0 0 - 0

rr-DELISTED LST-aa Y 0.5 0 0 0 0 - 0

rr-UST-aa Y 0.25 0 0 0 -- 0

rr-AST-aa Y 0.25 0 0 0 -- 0

rr-UST LAPSE-aa Y 0.25 0 0 0 -- 0

rr-DTNK-aa Y 0.25 0 0 0 -- 0

rr-BROWNFIELDS-aa Y 0.5 0 0 0 0 - 0

rr-VCP-aa Y 0.5 1 1 0 0 - 2

rr-RESPONSE-aa Y 0.5 0 1 0 0 - 1

rr-INST-aa Y 0.5 0 0 0 0 - 0

Tribal
rr-INDIAN LUST-aa Y 0.5 0 0 0 0 - 0

rr-INDIAN UST-aa Y 0.25 0 0 0 -- 0

rr-DELISTED INDIAN LST-aa Y 0.5 0 0 0 0 - 0

rr-DELISTED INDIAN UST-aa Y 0.25 0 0 0 -- 0

County No County standard environmental record sources available for this State.
Additional Environmental Records
Federal
rr-PFAS GHG-aa Y 0.5 0 0 0 0 - 0

rr-OSC RESPONSE-aa Y 0.125 0 0 --- 0

DELISTED FRP
HIST GAS STATIONS
REFN
BULK TERMINAL
SEMS LIEN
SUPERFUND ROD
DOE FUSRAP
NPL UT
CONTAM POTENTIAL
SWF/LF
HSWF
LUST
LAST
DELISTED LST
UST
AST
UST LAPSE
DTNK
BROWNFIELDS
VCP
RESPONSE
INST
INDIAN LUST
INDIAN UST
DELISTED INDIAN LST
DELISTED INDIAN UST
PFAS GHG
OSC RESPONSE
6 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Database Searched Search
Radius
Project
Property
Within
0.12mi
0.125mi
to 0.25mi
0.25mi to
0.50mi
0.50mi to
1.00mi
Total
rr-FINDS/FRS-aa Y PO 3 ---- 3

rr-TRIS-aa Y PO 0 ---- 0

rr-PFAS NPL-aa Y 0.5 0 0 0 0 - 0

rr-PFAS FED SITES-aa Y 0.5 0 0 0 0 - 0

rr-PFAS SSEHRI-aa Y 0.5 0 0 0 0 - 0

rr-PFAS ERNS-aa Y 0.5 0 0 0 0 - 0

rr-PFAS NPDES-aa Y 0.5 0 0 0 0 - 0

rr-PFAS TRI-aa Y 0.5 0 0 0 0 - 0

rr-PFAS WATER-aa Y 0.5 0 0 0 0 - 0

rr-PFAS TSCA-aa Y 0.5 0 0 0 0 - 0

rr-PFAS E-MANIFEST-aa Y 0.5 0 0 0 0 - 0

rr-PFAS IND-aa Y 0.5 0 2 0 2 - 4

rr-HMIRS-aa Y 0.125 0 4 --- 4

rr-NCDL-aa Y 0.125 0 0 --- 0

rr-TSCA-aa Y 0.125 0 0 --- 0

rr-HIST TSCA-aa Y 0.125 0 0 --- 0

rr-FTTS ADMIN-aa Y PO 0 ---- 0

rr-FTTS INSP-aa Y PO 0 ---- 0

rr-PRP-aa Y PO 0 ---- 0

rr-SCRD DRYCLEANER-aa Y 0.5 0 0 0 0 - 0

rr-ICIS-aa Y PO 0 ---- 0

rr-FED DRYCLEANERS-aa Y 0.25 0 0 0 -- 0

rr-DELISTED FED DRY-aa Y 0.25 0 0 0 -- 0

rr-FUDS-aa Y 1 0 1 0 0 0 1

rr-FUDS MRS-aa Y 1 0 0 0 0 0 0

rr-FORMER NIKE-aa Y 1 0 0 0 0 0 0

rr-PIPELINE INCIDENT-aa Y PO 0 ---- 0

rr-MLTS-aa Y PO 0 ---- 0

rr-HIST MLTS-aa Y PO 0 ---- 0

rr-MINES-aa Y 0.25 0 0 0 -- 0

rr-SMCRA-aa Y 1 0 0 0 0 0 0

rr-MRDS-aa Y 1 0 0 0 0 0 0

rr-LM SITES-aa Y 1 0 0 0 0 0 0

rr-ALT FUELS-aa Y 0.25 0 0 0 -- 0

rr-CONSENT DECREES-aa Y 0.25 0 0 0 -- 0

FINDS/FRS
TRIS
PFAS NPL
PFAS FED SITES
PFAS SSEHRI
PFAS ERNS
PFAS NPDES
PFAS TRI
PFAS WATER
PFAS TSCA
PFAS E-MANIFEST
PFAS IND
HMIRS
NCDL
TSCA
HIST TSCA
FTTS ADMIN
FTTS INSP
PRP
SCRD DRYCLEANER
ICIS
FED DRYCLEANERS
DELISTED FED DRY
FUDS
FUDS MRS
FORMER NIKE
PIPELINE INCIDENT
MLTS
HIST MLTS
MINES
SMCRA
MRDS
LM SITES
ALT FUELS
CONSENT DECREES
7 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Database Searched Search
Radius
Project
Property
Within
0.12mi
0.125mi
to 0.25mi
0.25mi to
0.50mi
0.50mi to
1.00mi
Total
rr-AFS-aa Y PO 0 ---- 0

rr-SSTS-aa Y 0.25 0 0 0 -- 0

rr-PCBT-aa Y 0.5 0 0 0 0 - 0

rr-PCB-aa Y 0.5 0 0 0 0 - 0

rr-POWER PLANTS-aa Y 0.125 0 0 --- 0

State
rr-SPILLS-aa Y 0.125 0 9 --- 9

rr-CDL-aa Y PO 0 ---- 0

rr-DRYCLEANERS-aa Y 0.25 0 0 0 -- 0

rr-DELISTED DRYCLEANERS-aa Y 0.25 0 0 0 -- 0

rr-TIER 2-aa Y 0.125 0 5 --- 5

Tribal No Tribal additional environmental record sources available for this State.

County No County additional environmental record sources available for this State.
Total:11 28 3 7 0 49
* PO – Property Only
* 'Property and adjoining properties' database search radii are set at 0.25 miles.
AFS
SSTS
PCBT
PCB
POWER PLANTS
SPILLS
CDL
DRYCLEANERS
DELISTED DRYCLEANERS
TIER 2
8 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Executive Summary: Site Report Summary - Project Property
Map
Key
DB Company/Site Name Address Direction Distance
(mi/ft)
Elev Diff
(ft)
Page
Number
m1d dd-CERCLIS-805450944-aa NORTH TEMPLE LANDFILL 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 2 p1p-24-805450944-x1x
Site EPA ID: UTD000463489
m1d dd-CERCLIS-805460221-aa BONNEVILLE CENTER 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 2 p1p-26-805460221-x1x
Site EPA ID: UT0009772106
m1d dd-CERCLIS NFRAP-805482328-aa BONNEVILLE CENTER 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 2 p1p-28-805482328-x1x
Site EPA ID: UT0009772106
m1d dd-FINDS/FRS-817180027-aa NORTH TEMPLE LANDFILL 7200 W N TEMPLE
SALT LAKE CITY UT
841160000
N 0.00 / 0.00 2 p1p-31-817180027-x1x
Registry ID: 110002261533
m1d dd-VCP-820684259-aa NORTH TEMPLE LANDFILL Intersection of I-80 and 7200
West
SALT LAKE CITY UT 84116
N 0.00 / 0.00 2 p1p-31-820684259-x1x
m1d dd-HSWF-820790284-aa North Temple Landfill
UT
N 0.00 / 0.00 2 p1p-32-820790284-x1x
m1d dd-SEMS-828840178-aa NORTH TEMPLE LANDFILL 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 2 p1p-33-828840178-x1x
EPA ID: UTD000463489
m1d dd-SEMS ARCHIVE-828877025-aa BONNEVILLE CENTER 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 2 p1p-35-828877025-x1x
EPA ID: UT0009772106
m1d dd-FINDS/FRS-885136932-aa NORTH TEMPLE LANDFILL
- LEACHATE
330 NORTH 7200 WEST
SALT LAKE CITY UT 84116
N 0.00 / 0.00 2 p1p-36-885136932-x1x
Registry ID: 110070708541
m1d dd-CONTAM POTENTIAL-891365868-aa NORTH TEMPLE LANDFILL 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 2 p1p-37-891365868-x1x
m2d dd-FINDS/FRS-920771341-aa I-80 RECYCLE PROJECT I-80 FRONTAGE RD
WEST VALLEY CITY UT
84104
WSW 0.00 / 0.00 9 p1p-37-920771341-x1x
Registry ID: 110071437037
24
26
28
31
31
32
33
35
36
37
37
1
1
1
1
1
1
1
1
1
1
2
CERCLIS
CERCLIS
CERCLIS
NFRAP
FINDS/FRS
VCP
HSWF
SEMS
SEMS
ARCHIVE
FINDS/FRS
CONTAM
POTENTIAL
FINDS/FRS
Executive Summary: Site Report Summary - Project Property
9 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Executive Summary: Site Report Summary - Surrounding Properties
Map
Key
DB Company/Site Name Address Direction Distance
(mi/ft)
Elev Diff
(ft)
Page
Number
m3d dd-PROPOSED NPL-807277278-aa KENNECOTT (NORTH
ZONE)
12000 WEST 2100 SOUTH
MAGNA UT 84044
SW 0.01 / 35.45 -2 p1p-38-807277278-x1x
EPA ID: UTD070926811
m4d dd-FUDS-845739072-aa Salt Lake City Army Air
Base Gunnery Range

SALT LAKE CITY UT
WNW 0.01 / 64.39 0 p1p-42-845739072-x1x
FUDS Property No: J08UT0951
m5d dd-RCRA SQG-894820944-aa AMAZON.COM
SERVICES LLC - SUT1
6338 WEST 700 NORTH
SALT LAKE CITY UT 84116
NE 0.08 /
433.87
-3 p1p-43-894820944-x1x
EPA Handler ID: UTR000017020
m5d dd-TIER 2-898864137-aa Amazoncom Services LLC
- SUT1
6338 West 700 North
SALT LAKE CITY UT 84116
NE 0.08 /
433.87
-3 p1p-48-898864137-x1x
m6d dd-VCP-873400456-aa AIRPORT WEST 581 NORTH JOHN GLENN
ROAD
SALT LAKE CITY UT
E 0.10 /
547.95
-2 p1p-48-873400456-x1x
m6d dd-RESPONSE-875058995-aa AIRPORT WEST VCP-
C092
581 NORTH JOHN GLENN
ROAD SALT LAKE CITY, UT
UT
E 0.10 /
547.95
-2 p1p-48-875058995-x1x
m7d dd-RCRA NON GEN-810171127-aa VALSPAR 421 JOHN GLEN ROAD
SALT LAKE CITY UT 84116
E 0.11 /
557.37
1 p1p-49-810171127-x1x
EPA Handler ID: UTR000009316
m7d dd-HMIRS-880618017-aa 421 NORTH JOHN GLENN
SALT LAKE CITY UT
E 0.11 /
557.37
1 p1p-51-880618017-x1x
m7d dd-HMIRS-880666513-aa 421 NO JOHN GLENN
SALT LAKE CITY UT
E 0.11 /
557.37
1 p1p-53-880666513-x1x
m7d dd-TIER 2-882131438-aa Quality Distribution, Inc 421 John Glenn Rd
SALT LAKE CITY UT 84116
E 0.11 /
557.37
1 p1p-55-882131438-x1x
m7d dd-PFAS IND-918263641-aa VALSPAR
SALT LAKE CITY UT
E 0.11 /
557.37
1 p1p-55-918263641-x1x
m8d dd-SPILLS-822565742-aa Compeq 629 North John Glenn Road
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-55-822565742-x1x
DERR ID | Date Discovered: 1836 | 4/8/1996 14:50
38
42
43
48
48
48
49
51
53
55
55
55
3
4
5
5
6
6
7
7
7
7
7
8
PROPOSED
NPL
FUDS
RCRA
SQG
TIER
2
VCP
RESPONSE
RCRA
NON GEN
HMIRS
HMIRS
TIER
2
PFAS
IND
SPILLS
Executive Summary: Site Report Summary - Surrounding Properties
10 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Map
Key
DB Company/Site Name Address Direction Distance
(mi/ft)
Elev Diff
(ft)
Page
Number
m8d dd-SPILLS-822567661-aa GW International 620 North John Glenn Road
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-56-822567661-x1x
DERR ID | Date Discovered: 3556 | 08/07/2000
m8d dd-SPILLS-858111183-aa Com Tech International 620 North John Glen Road
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-56-858111183-x1x
DERR ID | Date Discovered: 1689 | 12/04/1995
m8d dd-SPILLS-858111354-aa Compeq Int'l 620 North John Glen Road
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-57-858111354-x1x
DERR ID | Date Discovered: 1948 | 06/28/1996
m8d dd-TIER 2-866531160-aa COMPEQ
INTERNATIONAL, INC
620 N. JOHN GLENN RD.
SALT LAKE CITY UT 84116
ENE 0.11 /
563.52
-2 p1p-58-866531160-x1x
m8d dd-SPILLS-866619851-aa Compeq 620 North John Glen Road
(5600 West)
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-59-866619851-x1x
DERR ID | Date Discovered: 4774 | 01/29/2003
m8d dd-SPILLS-866619876-aa Univar USA, Inc., Bob
Sollesvik
620 North John Glenn Rd
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-60-866619876-x1x
DERR ID | Date Discovered: 5444 | 09/22/2004
m8d dd-SPILLS-866620151-aa Compeq International 620 N. John Glenn Rd (6070
West)
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-60-866620151-x1x
DERR ID | Date Discovered: 5041 | 09/19/2003
m8d dd-SPILLS-866620198-aa COMPEQ
INTERNATIONAL
620 N. John Glenn Rd. (6070
West)
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-61-866620198-x1x
DERR ID | Date Discovered: 5042 | 09/19/2003
m8d dd-SPILLS-866620208-aa None 620 North John Glenn Road
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-62-866620208-x1x
DERR ID | Date Discovered: 4168 | 10/08/2001
m8d dd-HMIRS-880606948-aa 620 N JOHN GLENN DR
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-62-880606948-x1x
m8d dd-HMIRS-880656862-aa 620 N JOHN GLENN RD
SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-64-880656862-x1x
m8d dd-PFAS IND-918308715-aa PRINTED CIRCUIT
BOARD
MANUFACTURING

SALT LAKE CITY UT
ENE 0.11 /
563.52
-2 p1p-66-918308715-x1x
m9d dd-RCRA SQG-879472007-aa AMAZON.COM
SERVICES, LLC. - SLC3
355 NORTH JOHN GLENN
ROAD
SALT LAKE CITY UT 84116
ESE 0.12 /
613.88
1 p1p-67-879472007-x1x
EPA Handler ID: UTR000015404
56
56
57
58
59
60
60
61
62
62
64
66
67
8
8
8
8
8
8
8
8
8
8
8
8
9
SPILLS
SPILLS
SPILLS
TIER
2
SPILLS
SPILLS
SPILLS
SPILLS
SPILLS
HMIRS
HMIRS
PFAS
IND
RCRA
SQG
11 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Map
Key
DB Company/Site Name Address Direction Distance
(mi/ft)
Elev Diff
(ft)
Page
Number
m9d dd-TIER 2-882131574-aa Amazoncom Services, LLC
- SLC3
355 John Glenn Rd
SALT LAKE CITY UT 84116
ESE 0.12 /
613.88
1 p1p-73-882131574-x1x
m10d dd-RCRA SQG-885970234-aa AMAZON.COM
SERVICES LLC SLC9
808 N. 6550 W. SLC GLOBAL
LOGISITICS CTR BUILDING 3
SALT LAKE CITY UT 84116
NE 0.12 /
640.53
-4 p1p-74-885970234-x1x
EPA Handler ID: UTR000015859
m10d dd-TIER 2-898864125-aa Amazoncom Services LLC
- SLC9
808 N 6550 W
SALT LAKE CITY UT 84116
NE 0.12 /
640.53
-4 p1p-77-898864125-x1x
m11d dd-RCRA SQG-867211001-aa BIOMERICS LLC 6030 W HAROLD GATTY DR
SALT LAKE CITY UT 84116
ENE 0.15 /
810.58
4 p1p-77-867211001-x1x
EPA Handler ID: UTD988070215
m11d dd-RCRA TSD-873889549-aa BIOMERICS LLC 6030 W HAROLD GATTY DR
SALT LAKE CITY UT 84116
ENE 0.15 /
810.58
4 p1p-100-873889549-x1x
EPA Handler ID: UTD988070215
m12d dd-RCRA SQG-826030939-aa ALBANY ENGINEERED
COMPOSITES
5995 WEST AMELIA
EARHART DRIVE
SALT LAKE CITY UT 84116
E 0.24 /
1,269.35
3 p1p-123-826030939-x1x
EPA Handler ID: UTR000003236
m13d dd-PFAS IND-924033371-aa ALBANY ENGINEERED
COMPOSITES

SALT LAKE CITY UT
E 0.25 /
1,336.43
0 p1p-133-924033371-x1x
m14d dd-PFAS IND-923152099-aa COLDSET PRINTING
PRESSES & STAMPING

SALT LAKE CITY UT
ENE 0.32 /
1,683.28
2 p1p-134-923152099-x1x
m15d dd-CERCLIS-805418078-aa KENNECOTT (NORTH
ZONE)
12000 WEST 2100 SOUTH
MAGNA UT 84044
SW 0.49 /
2,562.68
-3 p1p-134-805418078-x1x
Site EPA ID: UTD070926811
m15d dd-SEMS-828841683-aa KENNECOTT (NORTH
ZONE)
12000 WEST 2100 SOUTH
MAGNA UT 84044
SW 0.49 /
2,562.68
-3 p1p-143-828841683-x1x
EPA ID: UTD070926811
m15d dd-SUPERFUND ROD-859641034-aa KENNECOTT (NORTH
ZONE)
12000 WEST 2100 SOUTH
MAGNA UT 8404
SW 0.49 /
2,562.68
-3 p1p-149-859641034-x1x
m15d dd-NPL UT-901572580-aa KENNECOTT NORTH
ZONE
12000 W 2100 South
MAGNA UT 84044
SW 0.49 /
2,562.68
-3 p1p-149-901572580-x1x
m16d dd-LUST-820756204-aa SLC FIRE DEPT. STA. #9 5822 W AMELIA EARHART
DR (350 N )
SALT LAKE CITY UT 84116
E 0.49 /
2,606.50
2 p1p-150-820756204-x1x
DERR ID: 4001798
Date Close: 4/11/2003, LNW | 4/11/2003
73
74
77
77
100
123
133
134
134
143
149
149
150
9
10
10
11
11
12
13
14
15
15
15
15
16
TIER
2
RCRA
SQG
TIER
2
RCRA
SQG
RCRA
TSD
RCRA
SQG
PFAS
IND
PFAS
IND
CERCLIS
SEMS
SUPERFUND
ROD
NPL
UT
LUST
12 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Executive Summary: Summary by Data Source
Standard
Federal
PROPOSED NPL - National Priority List - Proposed

A search of the PROPOSED NPL database, dated Sep 25, 2024 has found that there are 1 PROPOSED NPL site(s) within
approximately 1.00miles of the project property.

Lower Elevation Address Direction Distance (mi/ft)Map Key

KENNECOTT (NORTH ZONE) 12000 WEST 2100 SOUTH
MAGNA UT 84044
SW 0.01 / 35.45 m-3-807277278-a
EPA ID: UTD070926811
SEMS - SEMS List 8R Active Site Inventory

A search of the SEMS database, dated Jul 24, 2024 has found that there are 2 SEMS site(s) within approximately 0.50miles of the
project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

NORTH TEMPLE LANDFILL 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 m-1-828840178-a
EPA ID: UTD000463489

Lower Elevation Address Direction Distance (mi/ft)Map Key

KENNECOTT (NORTH ZONE) 12000 WEST 2100 SOUTH
MAGNA UT 84044
SW 0.49 / 2,562.68 m-15-828841683-a
EPA ID: UTD070926811
SEMS ARCHIVE - SEMS List 8R Archive Sites

A search of the SEMS ARCHIVE database, dated Jul 24, 2024 has found that there are 1 SEMS ARCHIVE site(s) within approximately
0.50miles of the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

BONNEVILLE CENTER 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 m-1-828877025-a
EPA ID: UT0009772106

CERCLIS - Comprehensive Environmental Response, Compensation and Liability Information System - CERCLIS

A search of the CERCLIS database, dated Oct 25, 2013 has found that there are 3 CERCLIS site(s) within approximately 0.50miles of
the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

NORTH TEMPLE LANDFILL 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 m-1-805450944-a
3
1
15
1
1
Executive Summary: Summary by Data Source
13 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key
Site EPA ID: UTD000463489

BONNEVILLE CENTER 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 m-1-805460221-a
Site EPA ID: UT0009772106

Lower Elevation Address Direction Distance (mi/ft)Map Key

KENNECOTT (NORTH ZONE) 12000 WEST 2100 SOUTH
MAGNA UT 84044
SW 0.49 / 2,562.68 m-15-805418078-a
Site EPA ID: UTD070926811
CERCLIS NFRAP - CERCLIS - No Further Remedial Action Planned

A search of the CERCLIS NFRAP database, dated Oct 25, 2013 has found that there are 1 CERCLIS NFRAP site(s) within
approximately 0.50miles of the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

BONNEVILLE CENTER 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 m-1-805482328-a
Site EPA ID: UT0009772106

RCRA TSD - RCRA non-CORRACTS TSD Facilities

A search of the RCRA TSD database, dated Apr 8, 2024 has found that there are 1 RCRA TSD site(s) within approximately 0.50miles
of the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

BIOMERICS LLC 6030 W HAROLD GATTY DR
SALT LAKE CITY UT 84116
ENE 0.15 / 810.58 m-11-873889549-a
EPA Handler ID: UTD988070215

RCRA SQG - RCRA Small Quantity Generators List

A search of the RCRA SQG database, dated Apr 8, 2024 has found that there are 5 RCRA SQG site(s) within approximately 0.25miles
of the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

AMAZON.COM SERVICES, LLC. -
SLC3
355 NORTH JOHN GLENN ROAD
SALT LAKE CITY UT 84116
ESE 0.12 / 613.88 m-9-879472007-a
EPA Handler ID: UTR000015404

BIOMERICS LLC 6030 W HAROLD GATTY DR
SALT LAKE CITY UT 84116
ENE 0.15 / 810.58 m-11-867211001-a
EPA Handler ID: UTD988070215

ALBANY ENGINEERED
COMPOSITES
5995 WEST AMELIA EARHART DRIVE
SALT LAKE CITY UT 84116
E 0.24 / 1,269.35 m-12-826030939-a
EPA Handler ID: UTR000003236

1
15
1
11
9
11
12
14 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Lower Elevation Address Direction Distance (mi/ft)Map Key

AMAZON.COM SERVICES LLC -
SUT1
6338 WEST 700 NORTH
SALT LAKE CITY UT 84116
NE 0.08 / 433.87 m-5-894820944-a
EPA Handler ID: UTR000017020

AMAZON.COM SERVICES LLC
SLC9
808 N. 6550 W. SLC GLOBAL
LOGISITICS CTR BUILDING 3
SALT LAKE CITY UT 84116
NE 0.12 / 640.53 m-10-885970234-a
EPA Handler ID: UTR000015859
RCRA NON GEN - RCRA Non-Generators

A search of the RCRA NON GEN database, dated Apr 8, 2024 has found that there are 1 RCRA NON GEN site(s) within approximately
0.25miles of the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

VALSPAR 421 JOHN GLEN ROAD
SALT LAKE CITY UT 84116
E 0.11 / 557.37 m-7-810171127-a
EPA Handler ID: UTR000009316

SUPERFUND ROD - Superfund Decision Documents

A search of the SUPERFUND ROD database, dated Jul 24, 2024 has found that there are 1 SUPERFUND ROD site(s) within
approximately 1.00miles of the project property.

Lower Elevation Address Direction Distance (mi/ft)Map Key

KENNECOTT (NORTH ZONE) 12000 WEST 2100 SOUTH
MAGNA UT 8404
SW 0.49 / 2,562.68 m-15-859641034-a
State
NPL UT - Utah National Priorities List

A search of the NPL UT database, dated May 6, 2024 has found that there are 1 NPL UT site(s) within approximately 1.00miles of the
project property.

Lower Elevation Address Direction Distance (mi/ft)Map Key

KENNECOTT NORTH ZONE 12000 W 2100 South
MAGNA UT 84044
SW 0.49 / 2,562.68 m-15-901572580-a
CONTAM POTENTIAL - Potential Contaminated Sites

A search of the CONTAM POTENTIAL database, dated Nov 1, 2024 has found that there are 1 CONTAM POTENTIAL site(s) within
approximately 0.50miles of the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

NORTH TEMPLE LANDFILL 7200 W N TEMPLE
SALT LAKE CITY UT 84116
N 0.00 / 0.00 m-1-891365868-a

HSWF - Historical Solid Waste and Landfill Facilities
5
10
7
15
15
1
15 erisinfo.com | Environmental Risk Information Services Order No: 24111900057

A search of the HSWF database, dated Sep 22, 2014 has found that there are 1 HSWF site(s) within approximately 0.50miles of the
project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

North Temple Landfill
UT
N 0.00 / 0.00 m-1-820790284-a

LUST - Sites With Leaking Underground Storage Tanks (LUST)

A search of the LUST database, dated Sep 23, 2024 has found that there are 1 LUST site(s) within approximately 0.50miles of the
project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

SLC FIRE DEPT. STA. #9 5822 W AMELIA EARHART DR (350 N
)
SALT LAKE CITY UT 84116
E 0.49 / 2,606.50 m-16-820756204-a
DERR ID: 4001798
Date Close: 4/11/2003, LNW | 4/11/2003

VCP - Voluntary Cleanup Site List

A search of the VCP database, dated Sep 2, 2024 has found that there are 2 VCP site(s) within approximately 0.50miles of the project
property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

NORTH TEMPLE LANDFILL Intersection of I-80 and 7200 West
SALT LAKE CITY UT 84116
N 0.00 / 0.00 m-1-820684259-a

Lower Elevation Address Direction Distance (mi/ft)Map Key

AIRPORT WEST 581 NORTH JOHN GLENN ROAD
SALT LAKE CITY UT
E 0.10 / 547.95 m-6-873400456-a
RESPONSE - Response Action Sites

A search of the RESPONSE database, dated Mar 12, 2024 has found that there are 1 RESPONSE site(s) within approximately 0.50
miles of the project property.

Lower Elevation Address Direction Distance (mi/ft)Map Key

AIRPORT WEST VCP-C092 581 NORTH JOHN GLENN ROAD
SALT LAKE CITY, UT
UT
E 0.10 / 547.95 m-6-875058995-a
Non Standard
Federal
FINDS/FRS - Facility Registry Service/Facility Index

A search of the FINDS/FRS database, dated Aug 1, 2024 has found that there are 3 FINDS/FRS site(s) within approximately 0.02miles
1
16
1
6
6
16 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
of the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

NORTH TEMPLE LANDFILL 7200 W N TEMPLE
SALT LAKE CITY UT 841160000
N 0.00 / 0.00 m-1-817180027-a
Registry ID: 110002261533

NORTH TEMPLE LANDFILL -
LEACHATE
330 NORTH 7200 WEST
SALT LAKE CITY UT 84116
N 0.00 / 0.00 m-1-885136932-a
Registry ID: 110070708541

I-80 RECYCLE PROJECT I-80 FRONTAGE RD
WEST VALLEY CITY UT 84104
WSW 0.00 / 0.00 m-2-920771341-a
Registry ID: 110071437037

PFAS IND - PFAS Industry Sectors

A search of the PFAS IND database, dated Sep 23, 2024 has found that there are 4 PFAS IND site(s) within approximately 0.50miles of
the project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

VALSPAR
SALT LAKE CITY UT
E 0.11 / 557.37 m-7-918263641-a

ALBANY ENGINEERED
COMPOSITES

SALT LAKE CITY UT
E 0.25 / 1,336.43 m-13-924033371-a

COLDSET PRINTING PRESSES
& STAMPING

SALT LAKE CITY UT
ENE 0.32 / 1,683.28 m-14-923152099-a

Lower Elevation Address Direction Distance (mi/ft)Map Key

PRINTED CIRCUIT BOARD
MANUFACTURING

SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-918308715-a
HMIRS - Hazardous Materials Information Reporting System

A search of the HMIRS database, dated May 29, 2024 has found that there are 4 HMIRS site(s) within approximately 0.12miles of the
project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

421 NO JOHN GLENN
SALT LAKE CITY UT
E 0.11 / 557.37 m-7-880666513-a

421 NORTH JOHN GLENN
SALT LAKE CITY UT
E 0.11 / 557.37 m-7-880618017-a
1
1
2
7
13
14
8
7
7
17 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

Lower Elevation Address Direction Distance (mi/ft)Map Key

620 N JOHN GLENN RD
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-880656862-a

620 N JOHN GLENN DR
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-880606948-a
FUDS - Formerly Used Defense Sites

A search of the FUDS database, dated May 15, 2023 has found that there are 1 FUDS site(s) within approximately 1.00miles of the
project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

Salt Lake City Army Air Base
Gunnery Range

SALT LAKE CITY UT
WNW 0.01 / 64.39 m-4-845739072-a
FUDS Property No: J08UT0951

State
SPILLS - Environmental Incidents

A search of the SPILLS database, dated Sep 19, 2024 has found that there are 9 SPILLS site(s) within approximately 0.12miles of the
project property.

Lower Elevation Address Direction Distance (mi/ft)Map Key

COMPEQ INTERNATIONAL 620 N. John Glenn Rd. (6070 West)
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-866620198-a
DERR ID | Date Discovered: 5042 | 09/19/2003

Compeq 620 North John Glen Road (5600 West)
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-866619851-a
DERR ID | Date Discovered: 4774 | 01/29/2003

Compeq 629 North John Glenn Road
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-822565742-a
DERR ID | Date Discovered: 1836 | 4/8/1996 14:50

GW International 620 North John Glenn Road
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-822567661-a
DERR ID | Date Discovered: 3556 | 08/07/2000

Com Tech International 620 North John Glen Road
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-858111183-a
DERR ID | Date Discovered: 1689 | 12/04/1995
8
8
4
8
8
8
8
8
18 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Lower Elevation Address Direction Distance (mi/ft)Map Key

Compeq Int'l 620 North John Glen Road
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-858111354-a
DERR ID | Date Discovered: 1948 | 06/28/1996

Compeq International 620 N. John Glenn Rd (6070 West)
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-866620151-a
DERR ID | Date Discovered: 5041 | 09/19/2003

Univar USA, Inc., Bob Sollesvik 620 North John Glenn Rd
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-866619876-a
DERR ID | Date Discovered: 5444 | 09/22/2004

None 620 North John Glenn Road
SALT LAKE CITY UT
ENE 0.11 / 563.52 m-8-866620208-a
DERR ID | Date Discovered: 4168 | 10/08/2001
TIER 2 - Tier 2 Chemical Inventory Program

A search of the TIER 2 database, dated May 6, 2024 has found that there are 5 TIER 2 site(s) within approximately 0.12miles of the
project property.
Equal/Higher Elevation Address Direction Distance (mi/ft)Map Key

Quality Distribution, Inc 421 John Glenn Rd
SALT LAKE CITY UT 84116
E 0.11 / 557.37 m-7-882131438-a

Amazoncom Services, LLC - SLC3 355 John Glenn Rd
SALT LAKE CITY UT 84116
ESE 0.12 / 613.88 m-9-882131574-a

Lower Elevation Address Direction Distance (mi/ft)Map Key

Amazoncom Services LLC - SUT1 6338 West 700 North
SALT LAKE CITY UT 84116
NE 0.08 / 433.87 m-5-898864137-a

COMPEQ INTERNATIONAL, INC 620 N. JOHN GLENN RD.
SALT LAKE CITY UT 84116
ENE 0.11 / 563.52 m-8-866531160-a

Amazoncom Services LLC - SLC9 808 N 6550 W
SALT LAKE CITY UT 84116
NE 0.12 / 640.53 m-10-898864125-a
8
8
8
8
7
9
5
8
10
#*
")
#*
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m2 c
m12c
m14c
m16cm13c
m7c(5)
m5c(2)
m6c(2)
m9c(2)
m1 5c(4 )
m1 0c(2 )
m11c(2)
m8c(13)
m1 c(10 )
m4c
m3c
112°1'W112°1'30"W112°2'W112°2'30"W112°3'W112°3'30"W112°4'W112°4'30"W112°5'W112°5'30"W
40°48'N
40°48'N
40°47'30"N
40°47'30"N
40°47'N
40°47'N
40°46'30"N
40°46'30"N
40°46'N
40°46'N
40°45'30"N
40°45'30"N
40°45'N
40°45'N
0.5 0 0.50.25 Miles
Order Number: 24111900057Map: 1.0 Mile Radius
1:33250
Ad dress: 6780 North Temple Frontage, Salt Lake City, UT
Source: © 2021 E SRI StreetMap Premium © ERIS Information Inc.

Project PropertyBuffer Outline
#*Sites with H igher Elevation
")Sites with Same Elevation
#*Sites with Lower Elevation
(Sites with U nknown Elevation
Areas with Higher Elevation
Areas with Same Elevation
Areas with Lower Elevation
Areas with Unknown Elevation
National Wetland
Indian Reserve Land
100 Year Flood Zone
500 Year Flood Zone
Freeways; Highw ays
Traffic Circle; Ramp
Major & Minor Arterial
Traffic Circle; Ramp
Local Road
Rail
Country
State FWS Special Designation Areas
National Priorities List (Active, D elisted, Proposed, Institutional C ontrol)
2
12
14
16
13
7 (5)
5 (2)
6 (2)
9 (2)
15 (4)
10 (2)
11 (2)
8 (13)
1 (10)
4
3
#*
")
#*
#*
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#*
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#*
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m2 c
m12c
m14c
m16c
m13c
m7c(5)
m5c(2)
m6c(2)
m9c(2)
m1 5c(4 )
m10c(2)
m11c(2)
m8c(13)
m1 c(10 )
m4c
m3c
112°2'W112°2'30"W112°3'W112°3'30"W112°4'W112°4'30"W
40°47'30"N
40°47'30"N
40°47'N
40°47'N
40°46'30"N
40°46'30"N
40°46'N
40°46'N
40°45'30"N
40°45'30"N
0.35 0 0.350.175 Miles
Order Number: 24111900057Map: 0.5 Mile Radius
1:23750
Ad dress: 6780 North Temple Frontage, Salt Lake City, UT
Source: © 2021 E SRI StreetMap Premium © ERIS Information Inc.

Project PropertyBuffer Outline
#*Sites with H igher Elevation
")Sites with Same Elevation
#*Sites with Lower Elevation
(Sites with U nknown Elevation
Areas with Higher Elevation
Areas with Same Elevation
Areas with Lower Elevation
Areas with Unknown Elevation
National Wetland
Indian Reserve Land
100 Year Flood Zone
500 Year Flood Zone
Freeways; Highw ays
Traffic Circle; Ramp
Major & Minor Arterial
Traffic Circle; Ramp
Local Road
Rail
Country
State FWS Special Designation Areas
National Priorities List (Active, D elisted, Proposed, Institutional C ontrol)
2
12
14
16
13
7 (5)
5 (2)
6 (2)
9 (2)
15 (4)
10 (2)
11 (2)
8 (13)
1 (10)
4
3
#*
")
#*
#*
#*
#*
#*
#*
#*
#*
#*
#*
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m2 c
m12c
m14c
m13c
m7c(5)
m5c(2)
m6c(2)
m9c(2)
m1 5c(4 )
m10c(2)
m11c(2)
m8c(13)
m1 c(10 )
m4c
m3c
112°2'W112°2'30"W112°3'W112°3'30"W112°4'W112°4'30"W
40°47'30"N
40°47'30"N
40°47'N
40°47'N
40°46'30"N
40°46'30"N
40°46'N
40°46'N
0.3 0 0.30.15 Miles
Order Number: 24111900057Map: 0.25 Mile Radius
1:19250
Ad dress: 6780 North Temple Frontage, Salt Lake City, UT
Source: © 2021 E SRI StreetMap Premium © ERIS Information Inc.

Project PropertyBuffer Outline
#*Sites with H igher Elevation
")Sites with Same Elevation
#*Sites with Lower Elevation
(Sites with U nknown Elevation
Areas with Higher Elevation
Areas with Same Elevation
Areas with Lower Elevation
Areas with Unknown Elevation
National Wetland
Indian Reserve Land
100 Year Flood Zone
500 Year Flood Zone
Freeways; Highw ays
Traffic Circle; Ramp
Major & Minor Arterial
Traffic Circle; Ramp
Local Road
Rail
Country
State FWS Special Designation Areas
National Priorities List (Active, D elisted, Proposed, Institutional C ontrol)
2
12
14
13
7 (5)
5 (2)
6 (2)
9 (2)
15 (4)
10 (2)
11 (2)
8 (13)
1 (10)
4
3
Source: Esri, Maxar, Earthstar Geographics, and the GIS User Community
112°2'W112°2'30"W112°3'W112°3'30"W112°4'W112°4'30"W
40°47'30"N
40°47'30"N
40°47'N
40°47'N
40°46'30"N
40°46'30"N
40°46'N
40°46'N
40°45'30"N
40°45'30"N0.25 0 0.250.125 Miles
Order Number: 24111900057Aerial
1:18470
Address: 6780 North Temple Frontage, Salt Lake City, UT © ERIS Info rmation Inc.
Source: ESRI World Imager y
Year: 2021
112°2'W112°2'30"W112°3'W112°3'30"W112°4'W112°4'30"W
40°48'N
40°48'N
40°47'30"N
40°47'30"N
40°47'N
40°47'N
40°46'30"N
40°46'30"N
40°46'N
40°46'N
40°45'30"N
40°45'30"N
0.35 0 0.350.175 Miles
Order Number: 24111900057Topographic Map
1:24000
Address: 6780 North Temple Frontage, UT
© ERIS Info rmation Inc.
Source: USGS Topographic Map
Quad rangle(s): Magna UT, Baileys Lake UT
Year: 2020
24 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Detail Report
Map Key Number of
Records
Direction Distance
(mi/ft)
Elev/Diff
(ft)
Site DB
m-1-805450944-b 1 of 10 N 0.00 /
0.00
4,227.43 /
2
NORTH TEMPLE LANDFILL
7200 W N TEMPLE
SALT LAKE CITY UT 84116

p1p-805450944-y1y
Site ID: 0800588 RNPL Status Code:N
Site EPA ID: UTD000463489 NPL Status:Not on the NPL
Site Street Address 2:RFED Facility Code:N
Site County Name: SALT LAKE RFED Facility Desc:Not a Federal Facility
Site FIPS Code: 49035 USGS Hydro Unit No.:16020204
Region Code: 08 Site Cong. Dist. Code:02
Site SMSA No.: 7160 ROT Desc:Other
Site Prim. Latitude: +40.773945 FR NPL Update No.:
Site Prim. Longitude: -112.057774 RFRA Code:
Lat Long Source:
RNON NPL Status Desc:Other Cleanup Activity: State-Lead Cleanup

CERCLIS Site Contact Name(s)

Person ID:13002897.00
First Name:Ryan
Last Name:Dunham
Phone No.:3033126627
Email:

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 002 Act Start Date:
RAT Code: PA Act Complete Date:4/2/1985 00:00:00
RAT Short Name: PA AGT Order No.:130
RAT Name: PRELIMINARY ASSESSMENT SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: P SH Lead:
SPA Code: 13
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:EPA Fund
Act Code ID: 001 Act Start Date:
RAT Code: DS Act Complete Date:4/1/1979 00:00:00
RAT Short Name: DISCVRY AGT Order No.:10
RAT Name: DISCOVERY SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: SH Lead:
SPA Code: 13
RAT Def:The process by which a potential hazardous waste site is brought to the attention of the EPA. The process can
1 CERCLIS
Detail Report
25 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Map Key Number of
Records
Direction Distance
(mi/ft)
Elev/Diff
(ft)
Site DB
occur through the use of several mechanisms such as a phone call or referral by another government agency.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 003 Act Start Date:
RAT Code: PA Act Complete Date:3/6/1987 00:00:00
RAT Short Name: PA AGT Order No.:130
RAT Name: PRELIMINARY ASSESSMENT SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: P SH Lead:
SPA Code: 13
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 001 Act Start Date:1/5/2008 00:00:00
RAT Code: VA Act Complete Date:
RAT Short Name: OTHERCLEAN AGT Order No.:185
RAT Name: OTHER CLEANUP ACTIVITY SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: SH Lead:
SPA Code: 13
RAT Def:Documents that another party is managing cleanup work at a non-NPL site.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 001 Act Start Date:
RAT Code: SI Act Complete Date:9/21/1990 00:00:00
RAT Short Name: SI AGT Order No.:160
RAT Name: SITE INSPECTION SH OU:00
RAT Hist. Only Flag: SH Code:SH
RAT NSI Indicator: B SH Seq:001
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:9/27/1995 00:00:00
RFBS Code: P SH Lead:State (Fund)
SPA Code: 13
RAT Def:The process of collecting site data and samples to characterize the severity of the hazard for the hazard ranking
score and/or enforcement support.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 001 Act Start Date:
RAT Code: PA Act Complete Date:5/1/1980 00:00:00
RAT Short Name: PA AGT Order No.:130
RAT Name: PRELIMINARY ASSESSMENT SH OU:
26 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Map Key Number of
Records
Direction Distance
(mi/ft)
Elev/Diff
(ft)
Site DB
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: P SH Lead:
SPA Code: 13
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:
Act Code ID: Act Start Date:
RAT Code: Act Complete Date:
RAT Short Name: AGT Order No.:0
RAT Name: SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: SH Seq:
RAT Level: SH Start Date:
RAT DEF OU: SH Complete Date:
RFBS Code: SH Lead:
SPA Code:
RAT Def:
Site Desc:The North Temple Landfill has been separated into two sites. The western most area will remain as the North
Temple Landfill and the Bonneville Center will be in the eastern most part of the facility which was called the North
Temple Landfill East or Bonn
Site Alias:CITY LDFL - INACTIVE,,,UT,;NORTH TEMPLE LANDFILL - EAST,5600 WEST NORTH TEMPLE,SALT LAKE
CITY,UT,84116;WEST NORTH TEMPLE STREET LDFL,,,UT,;
m-1-805460221-b 2 of 10 N 0.00 /
0.00
4,227.43 /
2
BONNEVILLE CENTER
7200 W N TEMPLE
SALT LAKE CITY UT 84116

p1p-805460221-y1y
Site ID: 0801790 RNPL Status Code:N
Site EPA ID: UT0009772106 NPL Status:Not on the NPL
Site Street Address 2:RFED Facility Code:N
Site County Name: SALT LAKE RFED Facility Desc:Not a Federal Facility
Site FIPS Code: 49035 USGS Hydro Unit No.:
Region Code: 08 Site Cong. Dist. Code:02
Site SMSA No.: ROT Desc:
Site Prim. Latitude: 04D04M73S FR NPL Update No.:
Site Prim. Longitude: 111D57M30S RFRA Code:
Lat Long Source:
RNON NPL Status Desc:NFRAP-Site does not qualify for the NPL based on existing information

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 001 Act Start Date:
RAT Code: SI Act Complete Date:9/21/1990 00:00:00
RAT Short Name: SI AGT Order No.:160
RAT Name: SITE INSPECTION SH OU:00
RAT Hist. Only Flag: SH Code:SH
RAT NSI Indicator: B SH Seq:001
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:9/27/1995 00:00:00
RFBS Code: P SH Lead:State (Fund)
SPA Code: 13
RAT Def:The process of collecting site data and samples to characterize the severity of the hazard for the hazard ranking
score and/or enforcement support.
Site Desc:
Site Alias:

1 CERCLIS
27 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Map Key Number of
Records
Direction Distance
(mi/ft)
Elev/Diff
(ft)
Site DB
CERCLIS Assess History

OU ID: 00 RALT Short Name:EPA Fund
Act Code ID: 001 Act Start Date:
RAT Code: DS Act Complete Date:4/1/1979 00:00:00
RAT Short Name: DISCVRY AGT Order No.:10
RAT Name: DISCOVERY SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: SH Lead:
SPA Code: 13
RAT Def:The process by which a potential hazardous waste site is brought to the attention of the EPA. The process can
occur through the use of several mechanisms such as a phone call or referral by another government agency.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 003 Act Start Date:
RAT Code: PA Act Complete Date:3/6/1987 00:00:00
RAT Short Name: PA AGT Order No.:130
RAT Name: PRELIMINARY ASSESSMENT SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: P SH Lead:
SPA Code: 13
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:EPA In-House
Act Code ID: 001 Act Start Date:
RAT Code: VS Act Complete Date:7/24/2000 00:00:00
RAT Short Name: ARCH SITE AGT Order No.:1500
RAT Name: ARCHIVE SITE SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: SH Lead:
SPA Code: 13
RAT Def:The decision is made that no further activity is planned at the site.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:
Act Code ID: Act Start Date:
RAT Code: Act Complete Date:
RAT Short Name: AGT Order No.:0
RAT Name: SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: SH Seq:
RAT Level: SH Start Date:
RAT DEF OU: SH Complete Date:
RFBS Code: SH Lead:
28 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
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SPA Code:
RAT Def:
Site Desc:The North Temple Landfill has been separated into two sites. The western most area will remain as the North
Temple Landfill and the Bonneville Center will be in the eastern most part of the facility which was called the North
Temple Landfill East or Bonn
Site Alias:CITY LDFL-INACTIVE,,,,;NORTH TEMPLE LANDFILL - EAST,5600 WEST NORTH TEMPLE,SALT LAKE CITY,
UT,84116;WEST NORTH TEMPLE STREET LDFL,,,,;

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 002 Act Start Date:
RAT Code: PA Act Complete Date:4/2/1985 00:00:00
RAT Short Name: PA AGT Order No.:130
RAT Name: PRELIMINARY ASSESSMENT SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: P SH Lead:
SPA Code: 13
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 001 Act Start Date:
RAT Code: PA Act Complete Date:5/1/1980 00:00:00
RAT Short Name: PA AGT Order No.:130
RAT Name: PRELIMINARY ASSESSMENT SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: P SH Lead:
SPA Code: 13
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID: 00 RALT Short Name:State (Fund)
Act Code ID: 001 Act Start Date:1/1/1998 00:00:00
RAT Code: OO Act Complete Date:7/24/2000 00:00:00
RAT Short Name: SITE REASS AGT Order No.:162
RAT Name: SITE REASSESSMENT SH OU:
RAT Hist. Only Flag: SH Code:
RAT NSI Indicator: B SH Seq:
RAT Level: 1 SH Start Date:
RAT DEF OU: 00 SH Complete Date:
RFBS Code: SH Lead:
SPA Code: 13
RAT Def:Superfund is expending extramural resources to determine/update the status of site assessment activities at a site
or site conditions have changed and the Region needs to update and possibly reassess a previously made
decision.
Site Desc:
Site Alias:
m-1-805482328-b 3 of 10 N 0.00 /
0.00
4,227.43 /
2
BONNEVILLE CENTER
7200 W N TEMPLE

p1p-805482328-y1y1CERCLIS
NFRAP
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SALT LAKE CITY UT 84116
Site ID: 801790 Site FIPS Code:49035
Site EPA ID: UT0009772106 Region Code:8
Site Parent ID: Site Cong. Dist. Code:2
Site County Name: SALT LAKE Federal Facility:
Parent Site Name:

CERCLIS-NFRAP Assess History

OU ID: 0 Act Start Date:
Act Code ID: 3 Act Complete Date:3/6/1987
RAT Code: PA AGT Order No.:130
RAT Short Name: PA SH OU:
RAT Name: PRELIMINARY ASSESSMENT SH Code:
RAT Hist. Only Flag: SH Seq:
RAT NSI Indicator: B SH Start Date:
RAT Level: 1 SH Complete Date:
RAT DEF OU: 00 SH Lead:
RFBS Code: P SH Qual:
SPA Code: 13 RAQ Act. Qual Short:Higher priority
RALT Short Name: State (Fund)RNPL Status Code:N
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
RNON NPL Status Desc:NFRAP-Site does not qualify for the NPL based on existing information

CERCLIS-NFRAP Assess History

OU ID: 0 Act Start Date:1/1/1998
Act Code ID: 1 Act Complete Date:7/24/2000
RAT Code: OO AGT Order No.:162
RAT Short Name: SITE REASS SH OU:
RAT Name: SITE REASSESSMENT SH Code:
RAT Hist. Only Flag: SH Seq:
RAT NSI Indicator: B SH Start Date:
RAT Level: 1 SH Complete Date:
RAT DEF OU: 00 SH Lead:
RFBS Code: SH Qual:
SPA Code: 13 RAQ Act. Qual Short:NFRAP
RALT Short Name: State (Fund)RNPL Status Code:N
RAT Def:Superfund is expending extramural resources to determine/update the status of site assessment activities at a site
or site conditions have changed and the Region needs to update and possibly reassess a previously made
decision.
RNON NPL Status Desc:NFRAP-Site does not qualify for the NPL based on existing information

CERCLIS-NFRAP Assess History

OU ID: 0 Act Start Date:
Act Code ID: 1 Act Complete Date:5/1/1980
RAT Code: PA AGT Order No.:130
RAT Short Name: PA SH OU:
RAT Name: PRELIMINARY ASSESSMENT SH Code:
RAT Hist. Only Flag: SH Seq:
RAT NSI Indicator: B SH Start Date:
RAT Level: 1 SH Complete Date:
RAT DEF OU: 00 SH Lead:
RFBS Code: P SH Qual:
SPA Code: 13 RAQ Act. Qual Short:Higher priority
RALT Short Name: State (Fund)RNPL Status Code:N
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
RNON NPL Status Desc:NFRAP-Site does not qualify for the NPL based on existing information

CERCLIS-NFRAP Assess History
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OU ID: 0 Act Start Date:
Act Code ID: 1 Act Complete Date:9/21/1990
RAT Code: SI AGT Order No.:160
RAT Short Name: SI SH OU:0
RAT Name: SITE INSPECTION SH Code:SH
RAT Hist. Only Flag: SH Seq:1
RAT NSI Indicator: B SH Start Date:
RAT Level: 1 SH Complete Date:9/27/1995 0:00
RAT DEF OU: 00 SH Lead:State (Fund)
RFBS Code: P SH Qual:
SPA Code: 13 RAQ Act. Qual Short:Higher priority
RALT Short Name: State (Fund)RNPL Status Code:N
RAT Def:The process of collecting site data and samples to characterize the severity of the hazard for the hazard ranking
score and/or enforcement support.
RNON NPL Status Desc:NFRAP-Site does not qualify for the NPL based on existing information

CERCLIS-NFRAP Assess History

OU ID: 0 Act Start Date:
Act Code ID: 1 Act Complete Date:4/1/1979
RAT Code: DS AGT Order No.:10
RAT Short Name: DISCVRY SH OU:
RAT Name: DISCOVERY SH Code:
RAT Hist. Only Flag: SH Seq:
RAT NSI Indicator: B SH Start Date:
RAT Level: 1 SH Complete Date:
RAT DEF OU: 00 SH Lead:
RFBS Code: SH Qual:
SPA Code: 13 RAQ Act. Qual Short:
RALT Short Name: EPA Fund RNPL Status Code:N
RAT Def:The process by which a potential hazardous waste site is brought to the attention of the EPA. The process can
occur through the use of several mechanisms such as a phone call or referral by another government agency.
RNON NPL Status Desc:NFRAP-Site does not qualify for the NPL based on existing information

CERCLIS-NFRAP Assess History

OU ID: 0 Act Start Date:
Act Code ID: 2 Act Complete Date:4/2/1985
RAT Code: PA AGT Order No.:130
RAT Short Name: PA SH OU:
RAT Name: PRELIMINARY ASSESSMENT SH Code:
RAT Hist. Only Flag: SH Seq:
RAT NSI Indicator: B SH Start Date:
RAT Level: 1 SH Complete Date:
RAT DEF OU: 00 SH Lead:
RFBS Code: P SH Qual:
SPA Code: 13 RAQ Act. Qual Short:Higher priority
RALT Short Name: State (Fund)RNPL Status Code:N
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
RNON NPL Status Desc:NFRAP-Site does not qualify for the NPL based on existing information

CERCLIS-NFRAP Assess History

OU ID: 0 Act Start Date:
Act Code ID: 1 Act Complete Date:7/24/2000
RAT Code: VS AGT Order No.:1500
RAT Short Name: ARCH SITE SH OU:
RAT Name: ARCHIVE SITE SH Code:
RAT Hist. Only Flag: SH Seq:
RAT NSI Indicator: B SH Start Date:
RAT Level: 1 SH Complete Date:
RAT DEF OU: 00 SH Lead:
RFBS Code: SH Qual:
SPA Code: 13 RAQ Act. Qual Short:
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RALT Short Name: EPA In-House RNPL Status Code:N
RAT Def:The decision is made that no further activity is planned at the site.
RNON NPL Status Desc:NFRAP-Site does not qualify for the NPL based on existing information
m-1-817180027-b 4 of 10 N 0.00 /
0.00
4,227.43 /
2
NORTH TEMPLE LANDFILL
7200 W N TEMPLE
SALT LAKE CITY UT 841160000

p1p-817180027-y1y
Registry ID:110002261533
FIPS Code:49035
HUC Code:16020204
Site Type Name:STATIONARY
Location Description:MULTI-PERMITTED SITE
Supplemental Location:
Create Date:01-MAR-00
Update Date:26-FEB-16
Interest Types:STATE MASTER, SUPERFUND (NON-NPL)
SIC Codes:
SIC Code Descriptions:
NAICS Codes:
NAICS Code Descriptions:
Conveyor:FRS
Federal Facility Code:
Federal Agency Name:
Tribal Land Code:
Tribal Land Name:
Congressional Dist No:01
Census Block Code:490351003062002
EPA Region Code:08
County Name:SALT LAKE
US/Mexico Border Ind:
Latitude:40.771601
Longitude:-111.949231
Reference Point:
Coord Collection Method:ADDRESS MATCHING-HOUSE NUMBER
Accuracy Value:150
Datum:NAD83
Source:
Facility Detail Rprt URL:https://ofmpub.epa.gov/frs_public2/fii_query_detail.disp_program_facility?p_registry_id=110002261533
Data Source:Facility Registry Service - Single File
Program Acronyms:

m-1-820684259-b 5 of 10 N 0.00 /
0.00
4,227.43 /
2
NORTH TEMPLE LANDFILL
Intersection of I-80 and 7200 West
SALT LAKE CITY UT 84116

p1p-820684259-y1y
DERR ID:C046
Site Name And ID No (Web):NORTH TEMPLE LANDFILL VCP-C046
Address And City (Web):INTERSECTION OF I-80 AND 7200 WEST, SALT LAKE CITY, UTAH
Status Code (Web):TAP
Status Code Desc (Web):Terminated by applicant
County (Web):SALT LAKE
Site name:NORTH TEMPLE LANDFILL
Site Address:Intersection of I-80 and 7200 West
Site City:SALT LAKE CITY
State:UT
Zip code:84116
Site County:SALT LAKE
Point Y:40.77983319775688
Point X:-112.05346986362768
Easting:411105.68
Northing:4514851.41
Data source(s):Utah VCP Site List(Web); Utah Environmental Map - Voluntary Cleanup Program

1
1
FINDS/FRS
VCP
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Utah Environmental Map - Voluntary Cleanup Program Details

Cimid:490000015233
St Key:4936
Date of Appl:01/05/2006
Date Cocis:
Contact Phone:[phone]
Curr Proj Ma:David Bird
Zip4:
Post to Net:Yes
Map Label:Voluntary Cleanup Program - C046
Proj desc:Original: The site consists of approximately 782 acres situated north of Interstate 80 from approximately 60th West
to 80th West. The site consists of a closed municipal landfill that was operated by Salt Lake City Corporation
between 1959 and 1979.A former landfill is located directly to the east of the North Temple Landfill and is known as
the North Temple Landfill East (NTL East), or Bonneville Center. It was in operation from 1953 until 1959. A
Certificate of Completion has been issued for that site through the Voluntary Cleanup Program.
Site desc:Voluntary Cleanup Program

Voluntary Cleanup Site List Details

Acres:790
Agreement Date Amended:12/11/2007
Agreement Date Original:03/21/2006
Application Date:01/05/2006
Date of Coc Amended:
Date of Coc Original:
Epa Cerclis Archive Date:
Project Manager:DAVID BIRD
Termination Date:06/04/2018
m-1-820790284-b 6 of 10 N 0.00 /
0.00
4,227.43 /
2
North Temple Landfill

UT

p1p-820790284-y1y
Facility Status Open:
Facility Status Closed:
Facility Status Will Close:
Permit Number:
Permit Date:
Operation Type:
Operation Type Desc:
Annual Tons:
Disposal Municipal Tons:
Disposal CD Tons:
Disposal Muni Cubic Yards:
Disposal Cubic Yards:
Disposal Tons Per Day:
Disposal Tons Recycled:
Other Reports Fin Assur:
Other Repo Ground Water:
Other Reports LF Gas:
Other Reports Training:
Fac Design Cap Tons:
Fac Design Cap CubicYard:
Facility Design Cap Acres:
Facility Design Cap Years:
Year Landfill Began Accept:
Report Period:
Assigned To:
County:Salt Lake County (Salt Lake City/County Health Dept.)
Area Code:
Phone Number:
Lat Long Coordinates:
TWP:1N
RG:2W
SEC:34
Q/Q:SW
1 HSWF
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Q Sec:NE
Baseline:SLBM
X:411159.2271
Y:4514534.1268
Contact Person Name:
Contact Person Title:
Contact Person Email Add:
Contact Person Name:
Contact Person Address:
Contact Person City:
Contact Person State:
Contact Person Zip:
Contact Person Area Code:
Contact Person Phone NO:
Landfill Owner Contact:
Landfill Owner Title:
Landfill Owner Email:
Landfill Owner Name:
Landfill Owner Address:
Landfill Owner City:
Landfill Owner State:
Landfill Owner Zip:
Landfill Owner Area Code:
Landfill Owner Phone NO:
Landfill Operator Contact:
Landfill Operator Title:
Landfill Operator Email:
Landfill Operator Name:
Landfill Operator Address:
Landfill Operator City:
Landfill Operator State:
Landfill Operator Zip Code:
Landfill Opr Area Code:
Landfill Operator Phone NO:
Land Owner Contact:
Land Owner Title:
Land Owner Email:
Land Owner Name:
Land Owner Address:
Land Owner City:
Land Owner State:
Land Owner Zip Code:
Land Owner Area Code:
Land Owner Phone NO:

m-1-828840178-b 7 of 10 N 0.00 /
0.00
4,227.43 /
2
NORTH TEMPLE LANDFILL
7200 W N TEMPLE
SALT LAKE CITY UT 84116

p1p-828840178-y1y
EPA ID: UTD000463489 Latitude:+40.773945
Pgm Sys ID: UTD000463489 Longitude:-112.057774
Latitude83: 40.771601 Latitude83(CalOES):40.771601
Longitude83: -111.949231 Longitude83(CalOES):-111.949231
Primary Nm (MAP):NORTH TEMPLE LANDFILL
Loc Addr (MAP):7200 W N TEMPLE
Site Name:NORTH TEMPLE LANDFILL
Street Address:7200 W N TEMPLE
Street Address 2:
City:SALT LAKE CITY
County:SALT LAKE
PGM SYS ID(CalOES):UTD000463489
Name(CalOES):NORTH TEMPLE LANDFILL
Loc Addr(CalOES):7200 W N TEMPLE
City(CalOES):SALT LAKE CITY
County(CalOES):SALT LAKE
Postal(CalOES):841160000
County Name:SALT LAKE
1 SEMS
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City Name:SALT LAKE CITY
Postal Code:841160000
State:UT
Zip:84116
Data Source:EPA Superfund Data and Reports Active Site Inventory (List 8R Active); EPA FRS Interests Map - SEMS; CalOES
EPA RCRA TSDF Map - SEMS

Site Level Information

Site ID: 0800588 Superfund Alt Agmt:No
NPL: Not on the NPL FIPS Code:49035
Federal Facility: No Cong District:02
FF Docket: No Region:08
Non NPL Status:Other Cleanup Activity: State-Lead Cleanup

Action Information

Operable Units: 00 Start Actual:1/5/2008 05:00:00 AM
Action Code: VA Finish Actual:
Action Name: OTHR CLEANUP Qual:
SEQ: 1 Curr Action Lead:St Perf
Region:08
FF Docket:No
NPL:No
Federal Facility:No

Operable Units: 00 Start Actual:
Action Code: PA Finish Actual:3/6/1987 05:00:00 AM
Action Name: PA Qual:H
SEQ: 3 Curr Action Lead:St Perf
Region:08
FF Docket:No
NPL:No
Federal Facility:No

Operable Units: 00 Start Actual:
Action Code: SI Finish Actual:9/21/1990 04:00:00 AM
Action Name: SI Qual:H
SEQ: 1 Curr Action Lead:St Perf
Region:08
FF Docket:No
NPL:No
Federal Facility:No

Operable Units: 00 Start Actual:4/1/1979 05:00:00 AM
Action Code: DS Finish Actual:4/1/1979 05:00:00 AM
Action Name: DISCVRY Qual:
SEQ: 1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:No
Federal Facility:No

Operable Units: 00 Start Actual:
Action Code: PA Finish Actual:4/2/1985 06:00:00 AM
Action Name: PA Qual:H
SEQ: 2 Curr Action Lead:St Perf
Region:08
FF Docket:No
NPL:No
Federal Facility:No

Operable Units: 00 Start Actual:
Action Code: PA Finish Actual:5/1/1980 04:00:00 AM
Action Name: PA Qual:H
SEQ: 1 Curr Action Lead:St Perf
Region:08
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FF Docket:No
NPL:No
Federal Facility:No

GIS Information

Registry ID: 110002261533 Pgm Sys Acrnm:SEMS
Active Status: NOT ON THE NPL Accuracy Value:150
Key Field: SEMSUTD000463489 HUC8 Code:16020204
Interest Type: SUPERFUND (NON-NPL)HUC 12:160202040405
Fed Agency Name: Public Ind:Yes
Fed Facility Code: Pgm Report:no data yet
Federal Land Ind: Point X:-111.94923099999994
EPA Region Code: 08 Point Y:40.77160100000003
Fips Code: 49035
Collect Mth Desc:ADDRESS MATCHING-HOUSE NUMBER
Ref Point Desc:
Fac Url:https://ofmpub.epa.gov/frs_public2/fii_query_detail.disp_program_facility?p_registry_id=110002261533
Program Url:
Pgm Report Url:no data yet

CalOES EPA RCRA TSDF - SEMS

Registry ID: 110002261533 HUC 12:160202040405
Interest Type: SUPERFUND (NON-NPL)Collect Mth Desc:ADDRESS MATCHING-HOUSE NUMBER
Active Status: NOT ON THE NPL Accuracy Value:150
Pgm Sys Acrnm: SEMS Ref Point Desc:
Federal Agency Nm: EPA Region Code:08
Federal Land Ind: Key Field:SEMSUTD000463489
Fed Facility Cd: Create Dt:10/26/2021
Public Ind: Yes Update Dt:11/24/2021
FIPS Code: 49035 Last Reported Dt:
HUC8 Code: 16020204
Pgm Report Url:no data yet
Program URL:
Fac Url:https://ofmpub.epa.gov/frs_public2/fii_query_detail.disp_program_facility?p_registry_id=110002261533
m-1-828877025-b 8 of 10 N 0.00 /
0.00
4,227.43 /
2
BONNEVILLE CENTER
7200 W N TEMPLE
SALT LAKE CITY UT 84116

p1p-828877025-y1y
Site ID: 0801790 FIPS Code:49035
EPA ID: UT0009772106 Cong District:02
Superfund Alte Agr: No Region:08
Federal Facility: No County:SALT LAKE
FF Docket: No
NPL:Not on the NPL
Non NPL Status:NFRAP-Site does not qualify for the NPL based on existing information

Action Information

Operable Units: 00 Qual:H
Action Code: PA SEQ:1
Action Name: PA FF:No
Start Actual: FF Docket:No
Finish Actual: 5/1/1980 04:00:00 AM Region:08
Curr Action Lead: St Perf
NPL:N

Operable Units: 00 Qual:H
Action Code: PA SEQ:3
Action Name: PA FF:No
Start Actual: FF Docket:No
Finish Actual: 3/6/1987 05:00:00 AM Region:08
1 SEMS
ARCHIVE
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Curr Action Lead: St Perf
NPL:N

Operable Units: 00 Qual:N
Action Code: OO SEQ:1
Action Name: SITE REASS FF:No
Start Actual: 1/1/1998 05:00:00 AM FF Docket:No
Finish Actual: 7/24/2000 04:00:00 AM Region:08
Curr Action Lead: St Perf
NPL:N

Operable Units: 00 Qual:H
Action Code: SI SEQ:1
Action Name: SI FF:No
Start Actual: FF Docket:No
Finish Actual: 9/21/1990 04:00:00 AM Region:08
Curr Action Lead: St Perf
NPL:N

Operable Units: 00 Qual:H
Action Code: PA SEQ:2
Action Name: PA FF:No
Start Actual: FF Docket:No
Finish Actual: 4/2/1985 06:00:00 AM Region:08
Curr Action Lead: St Perf
NPL:N

Operable Units: 00 Qual:
Action Code: DS SEQ:1
Action Name: DISCVRY FF:No
Start Actual: 4/1/1979 05:00:00 AM FF Docket:No
Finish Actual: 4/1/1979 05:00:00 AM Region:08
Curr Action Lead: EPA Perf
NPL:N

Operable Units: 00 Qual:
Action Code: VS SEQ:1
Action Name: ARCH SITE FF:No
Start Actual: FF Docket:No
Finish Actual: 7/24/2000 04:00:00 AM Region:08
Curr Action Lead: EPA Perf In-Hse
NPL:N
m-1-885136932-b 9 of 10 N 0.00 /
0.00
4,227.43 /
2
NORTH TEMPLE LANDFILL -
LEACHATE
330 NORTH 7200 WEST
SALT LAKE CITY UT 84116

p1p-885136932-y1y
Registry ID:110070708541
FIPS Code:49035
HUC Code:16020204
Site Type Name:STATIONARY
Location Description:
Supplemental Location:
Create Date:06-APR-20
Update Date:
Interest Types:ICIS-NPDES NON-MAJOR, STORM WATER CONSTRUCTION
SIC Codes:
SIC Code Descriptions:
NAICS Codes:
NAICS Code Descriptions:
Conveyor:FRS-GEOCODE
Federal Facility Code:
Federal Agency Name:
Tribal Land Code:
Tribal Land Name:
Congressional Dist No:01
Census Block Code:490351139061108
1 FINDS/FRS
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(ft)
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EPA Region Code:08
County Name:SALT LAKE COUNTY
US/Mexico Border Ind:
Latitude:40.762447
Longitude:-112.062897
Reference Point:ENTRANCE POINT OF A FACILITY OR STATION
Coord Collection Method:ADDRESS MATCHING-HOUSE NUMBER
Accuracy Value:50
Datum:NAD83
Source:
Facility Detail Rprt URL:https://ofmpub.epa.gov/frs_public2/fii_query_detail.disp_program_facility?p_registry_id=110070708541
Data Source:Facility Registry Service - Single File
Program Acronyms:

m-1-891365868-b 10 of 10 N 0.00 /
0.00
4,227.43 /
2
NORTH TEMPLE LANDFILL
7200 W N TEMPLE
SALT LAKE CITY UT 84116

p1p-891365868-y1y
DERR ID: UTD000463489 Contact Phone No:3853918120
CIM ID: 490000015233 Emerg Resp Branch:No
Site Description: CERCLA Site Assessment Map Label:CERCLA Site Assessment - UTD000463489
NPL: No County:SALT LAKE
Proposed for NPL: No Northing:4514201.4815
Arch for CERCLIS: No Easting:410735.51528
Point Y: 40.77393913184249 Project Manager:<Multiple>
Point X: -112.05776308927092
Project Description:Original: State has merged this site with North Temple Landfill East. EPA has chose to keep the sites separate for
now. Possible merge later. **Note: data in the [Project Description] field for some records is truncated from the
source.

m-2-920771341-b 1 of 1 WSW 0.00 /
0.00
4,234.35 /
9
I-80 RECYCLE PROJECT
I-80 FRONTAGE RD
WEST VALLEY CITY UT 84104

p1p-920771341-y1y
Registry ID:110071437037
FIPS Code:49035
HUC Code:16020204
Site Type Name:STATIONARY
Location Description:
Supplemental Location:
Create Date:07-JUL-23
Update Date:
Interest Types:ICIS-NPDES NON-MAJOR
SIC Codes:
SIC Code Descriptions:
NAICS Codes:
NAICS Code Descriptions:
Conveyor:ICIS
Federal Facility Code:
Federal Agency Name:
Tribal Land Code:
Tribal Land Name:
Congressional Dist No:01
Census Block Code:490351139061079
EPA Region Code:08
County Name:SALT LAKE COUNTY
US/Mexico Border Ind:
Latitude:40.774408
Longitude:-112.065058
Reference Point:CENTER OF A FACILITY OR STATION
Coord Collection Method:
Accuracy Value:
Datum:NAD83
Source:
1
2
CONTAM
POTENTIAL
FINDS/FRS
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Facility Detail Rprt URL:https://ofmpub.epa.gov/frs_public2/fii_query_detail.disp_program_facility?p_registry_id=110071437037
Data Source:Facility Registry Service - Single File
Program Acronyms:

m-3-807277278-b 1 of1 SW 0.01 /
35.45
4,223.63 /
-2
KENNECOTT (NORTH ZONE)
12000 WEST 2100 SOUTH
MAGNA UT 84044

p1p-807277278-y1y
EPA ID:UTD070926811
Data Source:U.S. EPA Superfund Program. Source: SEMS Superfund Public User Database. FOIA3 All Proposed NPL Sites.
Retrieved on 25 Sept 2024; U.S. EPA Site Boundaries Shapefile Download; U.S. EPA OU Boundaries Shapefile
Download; Superfund NPR Sites with Status Information

NPL (FOIA-003 All Proposed NPL Sites)

NPL Status Dt:01/18/94 Region:08
Federal Facility:No County:SALT LAKE
SAA (Superfund Alt):No Latitude:+40.734036
NAI:No Longitude:-112.141040
NA Entity (NAI Status):
Site Name:KENNECOTT (NORTH ZONE)
Address:12000 WEST 2100 SOUTH
City:MAGNA
Zip:84044
State:UT

NPL (Superfund Sites List)

SEMS ID:800636 Partial Deletion:No
SITS ID:1422 Constr Complete No:
Site Score:59.18 Constr Complete Dt:
Status:Proposed NPL Site Region:8
Proposed Date:1/18/1994 State:Utah
Listing Date:County:Salt Lake
NOID Date:Latitude:40.75
Deletion Date:Longitude:-112.125
Site Name:Kennecott (North Zone)
City:Magna
Site Listing Narrative:<a href="https://semspub.epa.gov/src/document/08/100000176" target="_blank">UTD070926811 (PDF)</a>
Site Progress Profile:<a href="https://cumulis.epa.gov/supercpad/cursites/csitinfo.cfm?id=0800636" target="_blank">Kennecott (North
Zone)</a>
Proposed Fr Notice:<a href="https://semspub.epa.gov/src/document/11/189657" target="_blank">01/18/1994 (PDF)</a>
Final Fr Notice:
NOID Fr Notice:
Deletion Fr Notice:
Restoration Fr Notice:
Notice of Data Availability:

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:14746.03003095
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
Site Feature 1:Operable Unit Boundary
Site Feature 2:Mills and Tailings Pond
Site Feature 3:2002 North End ROD. The Magna Tailings Pond Operable Unit (OU 15) includes the first step ofthe mineral
beneficiation process including the grinding of the ore and the separation of the minerals from the ground ore via
3 PROPOSED
NPL
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gravity and flotation. It also includes the waste areas associated with the grinding and concentrating operations. It
includes the major facilities, the Bonneville Crusher, the Magna Mill, the historic Arthur Mill, and the South and
North Tailings Impoundments.
Site Feature 4:Mills and Tailings Pond
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:33670.03055616
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:EPA SEMS documents
Site Feature:5
Site Feature 1:Total Site Polygon/OU Aggregation
Site Feature 2:Kennecott N Zone OUs 8-9, 13-15, 19, 22-25
Site Feature 3:The North-Zone generally consists of the process/tailings pipeline from the Copperton Mill of the open-pit mining
operations leading to the tailings ponds and repositories, the smelter, refinery, and associated wetlands near the
facilities and along the Great Salt Lake.
Site Feature 4:Kennecott N Zone OUs 8-9, 13-15, 19, 22-25
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:The noted address is not a mailing address. The selected street locator is an approximate address for the
Kennecott North Zone which is expansive.
URL Alias:https://www.epa.gov/superfund/kennecott-north

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:3183.14500125
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
Site Feature 1:Operable Unit Boundary
Site Feature 2:Magna Soils
Site Feature 3:2002 North End ROD.
Site Feature 4:Magna Soils
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
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Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:33.1870292
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
Site Feature 1:Operable Unit Boundary
Site Feature 2:Historic Facilities
Site Feature 3:
Site Feature 4:Historic Facilities
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:1826.9645354
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
Site Feature 1:Operable Unit Boundary
Site Feature 2:North End Groundwater
Site Feature 3:2002 North End ROD.
Site Feature 4:North End Groundwater
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:248.11791372
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
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Site Feature 1:Operable Unit Boundary
Site Feature 2:Refinery
Site Feature 3:2002 North End ROD.
Site Feature 4:Refinery
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:640.85429075
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
Site Feature 1:Operable Unit Boundary
Site Feature 2:Smelter and Acid Plants
Site Feature 3:2002 North End ROD.
Site Feature 4:Smelter and Acid Plants
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:6640.26825281
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
Site Feature 1:Operable Unit Boundary
Site Feature 2:Great Salt Lake Wetlands
Site Feature 3:2002 North End ROD.
Site Feature 4:Great Salt Lake Wetlands
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north

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NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:75.82304834
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
Site Feature 1:Operable Unit Boundary
Site Feature 2:Waste Water Treatment Plant and Sludge Ponds
Site Feature 3:2002 North End ROD.
Site Feature 4:Waste Water Treatment Plant and Sludge Ponds
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north

NPL (EPA Boundaries)

EPA Program:Superfund Remedial GIS Area:8906.71164704
NPL Status:P GIS Area Unit:Acres
Fed Facility:No Primary Telephone:[phone]
Region:8
Site Contact:Douglas Bacon
Site Contact 1:[e-mail]
Feature In:
Feature 1:
Site Feature:4
Site Feature 1:Operable Unit Boundary
Site Feature 2:Smelter Fallout
Site Feature 3:2002 North End ROD.
Site Feature 4:Smelter Fallout
Projection:WGS84
SF Geospat:The Agency is providing this geospatial information as a public service and does not vouch for the accuracy,
completeness, or currency of data. Data provided by external parties is not independently verified by EPA. This
data is made available to the public strictly for informational purposes. Data does not represent EPA's official
position, viewpoint, or opinion, express or implied. This information is not intended for use in establishing liability or
calculating Cost Recovery Statutes of Limitations and cannot be relied upon to create any rights, substantive or
procedural, enforceable by any party in litigation with the United States or third parties. EPA reserves the right to
change these data at any time without public notice.
Addr Comment:
URL Alias:https://www.epa.gov/superfund/kennecott-north
m-4-845739072-b 1 of1 WNW 0.01 /
64.39
4,224.80 /
0
Salt Lake City Army Air Base
Gunnery Range

SALT LAKE CITY UT

p1p-845739072-y1y
FUDS Property No:J08UT0951
EMS Map Link:https://fudsportal.usace.army.mil/ems/inventory/map?id=57790
FUDS INST ID:UT89799F503700
Status:Properties with all projects at site closeout
SDS ID:
NPL Status Code:Not Listed
Eligibility:Eligible
Site Eligib:Eligible
Current Owner:Other Federal Government; Private Sector
4 FUDS
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Has Project:Yes
DOD FUDS Pro:
Project Required:
No Further Action:
Congressional District:02
Congressional Dist 117:02
Media ID:
Metadata ID:
Feature Desc:
EPA Region:08
County:SALT LAKE
Latitude:40.80583333
Longitude:-112.08388889
Fiscal year:2020
USACE Division:spd
USACE District:spk
Centroid Lat:
Centroid Long:
Se Anno Cad Data:
Shape Length:0.228590774644174
Shape Area:0.00269052142072664
Shape Len:.22859077
X:
Y:
Data Source:U.S. Army Corps of Engineers Geospatial Open Data
Property History:
The Salt Lake City Army Air Base Gunnery Range consisted of 40.0 acres acquired by transfer from the Department of Interior, 6212.57 acres by lease,
and 24.24 acres easement by donation. The Air Force used the property as a gunnery range. 40.0 acres of public lands were relinquished to the DoI, a
lease of 6,212 acres was terminated, and the 24.24 easement acres were quitclaimed to the original owners.
Feature Description:
The Salt Lake City Army Air Base Gunnery Range consisted of 40.0 acres acquired by transfer from the Department of Interior, 6212.57 acres by lease,
and 24.24 acres easement by donation. The Air Force used the property as a gunnery range. 40.0 acres of public lands were relinquished to the DoI, a
lease of 6,212 acres was terminated, and the 24.24 easement acres were quitclaimed to the original owners.

m-5-894820944-b 1 of2 NE 0.08 /
433.87
4,222.24 /
-3
AMAZON.COM SERVICES LLC -
SUT1
6338 WEST 700 NORTH
SALT LAKE CITY UT 84116

p1p-894820944-y1y
EPA Handler ID:UTR000017020
Gen Status Universe:Small Quantity Generator
Contact Name:PAUL WILSON
Contact Address:NA ENVIRONMENTAL DEPARTMENT-AMAZON.COM , PO BOX 80842 , SEATTLE , WA, 98108 , US
Contact Phone No and Ext:800-575-0171
Contact Email:[e-mail]
Contact Country:US
County Name:SALT LAKE
EPA Region:08
Land Type:Private
Receive Date:20231222
Location Latitude:40.78376
Location Longitude:-112.03629

Violation/Evaluation Summary

Note:NO RECORDS: As of Apr 2024, there are no Compliance Monitoring and Enforcement (violation) records
associated with this facility (EPA ID).

Handler Summary

Importer Activity:No
5 RCRA SQG
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Mixed Waste Generator:No
Transporter Activity:No
Transfer Facility:No
Onsite Burner Exemption:No
Furnace Exemption:No
Underground Injection Activity:No
Commercial TSD:No
Used Oil Transporter:No
Used Oil Transfer Facility:No
Used Oil Processor:No
Used Oil Refiner:No
Used Oil Burner:No
Used Oil Market Burner:No
Used Oil Spec Marketer:No

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20210822
Handler Name:AMAZON.COM SERVICES LLC - SUT1
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D016
Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE
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Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20230214
Handler Name:AMAZON.COM SERVICES LLC - SUT1
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D016
Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

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Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Hazardous Waste Handler Details

Sequence No:3
Receive Date:20231222
Handler Name:AMAZON.COM SERVICES LLC - SUT1
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D016
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Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Owner/Operator Details

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:PO BOX 80842
Name:AMAZON.COM SERVICES LLC Street 2:
Date Became Current:20210822 City:SEATTLE
Date Ended Current:State:WA
Phone:[phone] Country:US
Source Type:Notification Zip Code:98108

Owner/Operator Ind:Current Owner Street No:166
Type:Private Street 1:EAST 14000 SOUTH
Name:PHASE 1 GLC 2, LLC Street 2:SUITE 210
Date Became Current:20210626 City:DRAPER
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84020

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:NA ENVIRONMENTAL DEPARTMENT-
AMAZON.COM
Name:AMAZON.COM SERVICES LLC Street 2:PO BOX 80842
Date Became Current:20210822 City:SEATTLE
Date Ended Current:State:WA
Phone:[phone] Country:US
Source Type:Notification Zip Code:98108

Historical Handler Details

Receive Dt:20230214
Generator Code Description:Small Quantity Generator
Handler Name:AMAZON.COM SERVICES LLC - SUT1

Receive Dt:20210822
Generator Code Description:Small Quantity Generator
Handler Name:AMAZON.COM SERVICES LLC - SUT1
48 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
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Elev/Diff
(ft)
Site DB
m-5-898864137-b 2 of2 NE 0.08 /
433.87
4,222.24 /
-3
Amazoncom Services LLC - SUT1
6338 West 700 North
SALT LAKE CITY UT 84116

p1p-898864137-y1y
Site Program ID:UT010612 Fac County:SALT LAKE
Department ID:New10410 UTM Easting:412055.25323
Program Descriptn:Tier2 Facilities UTM Northing:4515383.32029
m-6-873400456-b 1 of2 E 0.10 /
547.95
4,222.99 /
-2
AIRPORT WEST
581 NORTH JOHN GLENN ROAD
SALT LAKE CITY UT

p1p-873400456-y1y
DERR ID:C092
Site Name And ID No (Web):AIRPORT WEST VCP-C092
Address And City (Web):581 NORTH JOHN GLENN ROAD, SALT LAKE CITY, UTAH
Status Code (Web):ACT/RA
Status Code Desc (Web):Active remedial action phase
County (Web):SALT LAKE
Site name:Airport West
Site Address:581 North John Glenn Road
Site City:SALT LAKE CITY
State:UT
Zip code:84116
Site County:SALT LAKE
Point Y:40.777752587168735
Point X:-112.05303028688915
Easting:411140
Northing:4514620
Data source(s):Utah VCP Site List(Web); Utah Environmental Map - Voluntary Cleanup Program

Utah Environmental Map - Voluntary Cleanup Program Details

Cimid:490000015233
St Key:9654
Date of Appl:04/10/2018
Date Cocis:
Contact Phone:[phone]
Curr Proj Ma:David Bird
Zip4:
Post to Net:Yes
Map Label:Voluntary Cleanup Program - C092
Proj desc:
Site desc:Voluntary Cleanup Program

Voluntary Cleanup Site List Details

Acres:769.85
Agreement Date Amended:
Agreement Date Original:07/12/2018
Application Date:04/10/2018
Date of Coc Amended:
Date of Coc Original:
Epa Cerclis Archive Date:
Project Manager:DAVID BIRD
Termination Date:
m-6-875058995-b 2 of2 E 0.10 /
547.95
4,222.99 /
-2
AIRPORT WEST VCP-C092
581 NORTH JOHN GLENN ROAD
SALT LAKE CITY, UT
UT

p1p-875058995-y1y
Type of Site:Vacant - Former Landfill
Assessment or Cleanup:Assessment
and Cleanup
5
6
6
TIER 2
VCP
RESPONSE
49 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
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Nature of Contamination:Solvents, Metals,
Petroleum, PFAS
Unrestricted Land Use:Cleanup not complete
Site Size:769.9
RESP Plan Date:Spring 2023
RESP Complete Date:Cleanup not
started
Owner Name:SITLA
Latitude Longitude:40°46'40"N
112°3'11"W
Land Use Control:Proposed but not outlined in this table until the
response action as specified in the Remedial Action Plan(s) is verified complete and a Certificate of Completion is
issued. Site characterization on-going and a Remedial Action Plan was accepted in December 2022 for Phase I.

m-7-810171127-b 1 of5 E 0.11 /
557.37
4,226.79 /
1
VALSPAR
421 JOHN GLEN ROAD
SALT LAKE CITY UT 84116

p1p-810171127-y1y
EPA Handler ID:UTR000009316
Gen Status Universe:No Report
Contact Name:STEVE DOUGLAS
Contact Address:P.O. BOX 729 , , BENTON , AR, 72018 , US
Contact Phone No and Ext:800-377-4692
Contact Email:[e-mail]
Contact Country:US
County Name:SALT LAKE
EPA Region:08
Land Type:Private
Receive Date:20100526
Location Latitude:40.779945
Location Longitude:-112.036212

Violation/Evaluation Summary

Note:VIOLATION or UNDETERMINED: There are VIOLATION or UNDETERMINED details or records associated with
this facility (EPA ID) in the Compliance Monitoring and Enforcement table dated Apr, 2024.

Evaluation Details

Evaluation Start Date:20100526
Evaluation Type Description:COMPLIANCE ASSISTANCE VISIT
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:20080325
Evaluation Type Description:COMPLIANCE ASSISTANCE VISIT
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Handler Summary

Importer Activity:No
Mixed Waste Generator:No
Transporter Activity:No
Transfer Facility:No
Onsite Burner Exemption:No
Furnace Exemption:No
Underground Injection Activity:No
Commercial TSD:No
Used Oil Transporter:No
Used Oil Transfer Facility:No
Used Oil Processor:No
7 RCRA
NON GEN
50 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
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Used Oil Refiner:No
Used Oil Burner:No
Used Oil Market Burner:No
Used Oil Spec Marketer:No

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20061017
Handler Name:VALSPAR
Source Type:Notification
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20080325
Handler Name:VALSPAR
Source Type:Implementer
Federal Waste Generator Code:N
Generator Code Description:Not a Generator, Verified

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20100526
Handler Name:VALSPAR
Source Type:Implementer
Federal Waste Generator Code:N
Generator Code Description:Not a Generator, Verified

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Owner/Operator Details

Owner/Operator Ind:Current Owner Street No:421
Type:Private Street 1:JOHN GLEN ROAD
Name:QUALITY DIST. WAREHOUSE Street 2:
Date Became Current:19960209 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:901 WEST
Type:Private Street 1:UNION STREET
Name:VALSPAR Street 2:
Date Became Current:20051121 City:MONTEBELLO
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Date Ended Current:State:CA
Phone:[phone] Country:US
Source Type:Notification Zip Code:90640

Owner/Operator Ind:Current Operator Street No:901 WEST
Type:Private Street 1:UNION STREET
Name:VALSPAR Street 2:
Date Became Current:20051121 City:MONTEBELLO
Date Ended Current:State:CA
Phone:[phone] Country:US
Source Type:Implementer Zip Code:90640

Owner/Operator Ind:Current Owner Street No:421
Type:Private Street 1:JOHN GLEN ROAD
Name:QUALITY DIST. WAREHOUSE Street 2:
Date Became Current:19960209 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Implementer Zip Code:84116

Historical Handler Details

Receive Dt:20080325
Generator Code Description:Not a Generator, Verified
Handler Name:VALSPAR

Receive Dt:20061017
Generator Code Description:Small Quantity Generator
Handler Name:VALSPAR
m-7-880618017-b 2 of5 E 0.11 /
557.37
4,226.79 /
1

421 NORTH JOHN GLENN
SALT LAKE CITY UT

p1p-880618017-y1y
Incident County:SALT LAKE

HMIR Historical Reports

Report No:I-2011030261 Fed DOT Agency Nm:
Report Type:A hazardous material incident Fed DOT Report No:
Date of Incident:2011-02-11 Report Submit Src:Paper
Time of Incident:0900 Inc Multiple Rows:No
Haz Class Code:Inc Non US State:
Hazardous Class:3 Mode Transport:Highway
Commodity Short Nm:PAINT INCLUDING PAINT, L Transport Phase:Unloading
Commodity Long Nm:PAINT INCLUDING PAINT, LACQUER,
ENAMEL, STAIN, SHELLAC SOLUTIONS,
VARNISH, POLISH, LIQUID FILLER AND
LIQUID LACQUER BASE
Incident Occrrnce:
Trade Name:Mat Ship Approval?:No
ID No:UN1263 Mat Ship Approv No:
Haz Waste Ind:No Undecl Hazmat Ship?:No
Haz Waste EPA No:Packaging Type:Non-Bulk
HMIS Tox Inhalation?:No Packing Group:II
TIH Hazard Zone:Carrier Reporter:REDDAWAY
Qty Released:0.25 CR Street Name:16277 SE 130TH AVENUE
Unit of Measure:Liquid - Gallon CR City:Clackamas
What Failed:103 CR State:OR
What Failed Desc:Basic Material CR Postal Code:97015
How Failed Code:309 CR Non US State:
How Failed Desc:Punctured CR Fed DOT ID:62227
Failure Cause Code:517 CR Hazmat Reg ID:052909550094RT
Failure Cause Desc:Improper Preparation for Transportation CR Country:US
Ident. Markings:Shipper Name:VALSPAR
Cont1 Pkging Type:Jerrican Shipper Street Name:13535 68TH AVE S
Cont1 Const Mat:Steel Shipper City:SEATTLE
7 HMIRS
52 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
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Cont1 Head Type:Non-Removable Shipper State:WA
Cont1 Pkg Capacity:5 Shipper Postal:98178
C1 Capacity UOM:LGA Shipper Non US St:
Cont1 Pkg Amt:5 Shipper Country:US
C1 Pkg Amt UOM:LGA Shipper Waybill:5036021583
Cont1 Pkg No:3 Ship Hazmat Reg ID:
C1 Pkg NO Failed:1 Origin City:
Cont1 Pkg Mnfctr:Origin State:
Cont1 Pkg Mnfct Dt:0-00-00 00:00:00 Origin Postal:
Cont1 Pkg Serial NO:Origin Non US St:
C1 Pkg Last Test Dt:0-00-00 00:00:00 Origin Country:US
C1 Test Const Mat:Steel Destination City:SALT LAKE CITY
C1 Pkg Dsign Pres.:0 Destination State:UTAH
C1 Dsign Press UOM:Destination Postal:84116
C1 Pkg Shell Thick:0 Destination Non US:
C1 Shell Thick UOM:Destination Country:US
C1 Head Thickness:0 Cont2 Package Type:
C1 Head Thick UOM:Cont2 Const Mat:
C1 Pkg Srvc Pres.:0 Cont2 Pkg Capacity:0
C1 Srvc Press UOM:Cont2 Capacity UOM:
C1 Valve/Device Fail?:No Cont2 Pkg Amount:0
C1 Device Type:Cont2 Pkg Amt UOM:
C1 Device Mnfctr:Cont2 Pkg No:0
C1 Device Model:Cont2 Pkg No Failed:0
NRC No:

RAM Pkg Category:Haz NonHosp Public:0
RAM Pkg Cert.:FALSE Haz NonHosp Old:
RAM Pkg Cert. NBR:Tot Haz Non Hosp Inj:
RAM Nuclide S:Total Hazmat Injuries:0
RAM Transport Index:Evacuation Indicator:No
RAM UOM:Public Evacuated:0
RAM Activity Rpted:0 Employees Evac:0
RAM UOM Rpted:Total Evacuated:0
RAM Activity:0 Total Evacuation Hrs:0
RAM Activity UOM:Major Artery Closed:No
RAM Mat Safety:Mjr Artery Hrs Closed:0
Spillage Result:Yes Material Involved:No
Fire Result:No Estimated Speed:0
Explosion Result:No Weather Conditions:
Water Sewer Result:No Vehicle Overturn:No
Gas Dispersion:No Vehicle Left Roadway:No
Environment Damage:No Passenger Aircraft:No
No Release Result:No Cargo Baggage:
Fire EMS Report:No Ship Non Transport:No
Fire EMS EMS Report:Ship Air First Flight:No
Police Report:No Ship Air Subflight:No
Police Report No:Ship Init Transport:No
In House Cleanup:Yes Ship Phase Transfer:No
Other Cleanup:No Contact Name:STEVE SHINNERS
Damage > 500:No Contact Title:SR MGR INDUSTRIAL SAFETY AND ENV
Material Loss:0 Contact Business:YRC INC
Carrier Damage:0 Contact Street:10990 ROE AVENUE
Property Damage:0 Contact City:OVERLAND PARK
Response Cost:0 Contact State:KS
Remediation Cost:0 Contact Postal:66211
Damage Old Form:0 Contact Non US St:
Total Damages Amt:0 Contact Country:US
Hazmat Fatality:No Inc. Report Prepared:Carrier
Haz Fatal Employees:0 HMIS Serious Incidnt:No
Haz Fatal Respndrs:0 HMIS Serious Fatality:No
Haz Fatal Gen Public:0 HMIS Serious Injury:No
Tot Hazmat Fatalities:0 HMIS Flight Plan:No
Non Hazmat Fatality:No HMIS Serious Evacs:No
Non Hazmat Fatals:0 HMIS Major Artery:No
Hazmat Injury:No HMIS Bulk Release:No
Haz Hospital Empl:0 HMIS Marine Pollutnt:No
Haz Hospital Resp:0 HMIS Radioactive:No
Haz Hosp Gen Public:0 HMIS Gen Pkg Type:DRUM METAL
53 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
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Haz Hosp Old Form:0 HMIS Container Code:PAIL MTL
Total Haz Hosp Inj:0 HMIS Container Desc:Metal pail, open head, capacity 10 gallons or
less
Haz Non Hosp Empl:0 HMIS Bulk Incident:No
Haz Non Hosp Resp:0 Undeclared Shipment:No
Description of Events:WHILE UNLOADING AT THE CUSTOMER'S DOCK, FOUND WAS A FIVE GALLON PAIL DENTED AND
LEAKING. THE PAIL WAS REFUSED BY CONSIGNEE. THE AFFECTED MATERIALS WERE PLACED INTO A
PROPERLY MARKED AND LABELED SALVAGE DRUMS. THE DAMAGED PAIL WAS PLACED INTO A LINED
SALVAGE DRUM PENDING DISPOSITION.
Recommend Actions Taken:DRUMS AND PAILS OF CHEMICALS AND OR HAZARDOUS MATERIALS MUST BE COMPLETELY
SHROUDED AND BLOCKED, USING MTY PALLETS, PLYWOOD AND OR DUNNAGE. WHEN HANDLING AND
MOVING PAILS AND DRUMS, KNOW THE SURROUNDINGS TO ENSURE PRODUCT IS NOT EASILY
DAMAGED. RETRAINING IN WORK METHODS ON PROPER AND SAFE LOADING AND STACKING OF
HAZARDOUS MATERIALS AND CHEMICALS.
m-7-880666513-b 3 of5 E 0.11 /
557.37
4,226.79 /
1

421 NO JOHN GLENN
SALT LAKE CITY UT

p1p-880666513-y1y
Incident County:SALTLAKE

HMIR Historical Reports

Report No:I-2007090125 Fed DOT Agency Nm:
Report Type:A hazardous material incident Fed DOT Report No:
Date of Incident:2007-08-10 Report Submit Src:Paper
Time of Incident:0943 Inc Multiple Rows:No
Haz Class Code:Inc Non US State:
Hazardous Class:3 Mode Transport:Highway
Commodity Short Nm:PAINT INCLUDING PAINT, L Transport Phase:Unloading
Commodity Long Nm:PAINT INCLUDING PAINT, LACQUER,
ENAMEL, STAIN, SHELLAC SOLUTIONS,
VARNISH, POLISH, LIQUID FILLER AND
LIQUID LACQUER BASE
Incident Occrrnce:
Trade Name:PAINT Mat Ship Approval?:No
ID No:UN1263 Mat Ship Approv No:
Haz Waste Ind:No Undecl Hazmat Ship?:No
Haz Waste EPA No:Packaging Type:Non-Bulk
HMIS Tox Inhalation?:No Packing Group:II
TIH Hazard Zone:Carrier Reporter:USF REDDAWAY
Qty Released:0.007813 CR Street Name:PO BOX 1035
Unit of Measure:Liquid - Gallon CR City:CLACKAMAS
What Failed:110 CR State:OR
What Failed Desc:Cover CR Postal Code:97015
How Failed Code:308 CR Non US State:
How Failed Desc:Leaked CR Fed DOT ID:62227
Failure Cause Code:515 CR Hazmat Reg ID:050406550047OQ
Failure Cause Desc:Human Error CR Country:US
Ident. Markings:Shipper Name:VALSPAR
Cont1 Pkging Type:Jerrican Shipper Street Name:901 UNION ST
Cont1 Const Mat:Steel Shipper City:MONTEBELLO
Cont1 Head Type:Shipper State:CA
Cont1 Pkg Capacity:5 Shipper Postal:90640
C1 Capacity UOM:LGA Shipper Non US St:
Cont1 Pkg Amt:5 Shipper Country:US
C1 Pkg Amt UOM:LGA Shipper Waybill:5172481127
Cont1 Pkg No:12 Ship Hazmat Reg ID:
C1 Pkg NO Failed:1 Origin City:
Cont1 Pkg Mnfctr:Origin State:
Cont1 Pkg Mnfct Dt:0-00-00 00:00:00 Origin Postal:
Cont1 Pkg Serial NO:Origin Non US St:
C1 Pkg Last Test Dt:0-00-00 00:00:00 Origin Country:US
C1 Test Const Mat:Steel Destination City:SALT LAKE CITY
C1 Pkg Dsign Pres.:0 Destination State:UTAH
C1 Dsign Press UOM:Destination Postal:84116
C1 Pkg Shell Thick:0 Destination Non US:
C1 Shell Thick UOM:Destination Country:US
7 HMIRS
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C1 Head Thickness:0 Cont2 Package Type:
C1 Head Thick UOM:Cont2 Const Mat:
C1 Pkg Srvc Pres.:0 Cont2 Pkg Capacity:0
C1 Srvc Press UOM:Cont2 Capacity UOM:
C1 Valve/Device Fail?:No Cont2 Pkg Amount:0
C1 Device Type:Cont2 Pkg Amt UOM:
C1 Device Mnfctr:Cont2 Pkg No:0
C1 Device Model:Cont2 Pkg No Failed:0
NRC No:

RAM Pkg Category:Haz NonHosp Public:0
RAM Pkg Cert.:FALSE Haz NonHosp Old:
RAM Pkg Cert. NBR:Tot Haz Non Hosp Inj:
RAM Nuclide S:Total Hazmat Injuries:0
RAM Transport Index:Evacuation Indicator:No
RAM UOM:Public Evacuated:0
RAM Activity Rpted:0 Employees Evac:0
RAM UOM Rpted:Total Evacuated:0
RAM Activity:0 Total Evacuation Hrs:0
RAM Activity UOM:Major Artery Closed:No
RAM Mat Safety:Mjr Artery Hrs Closed:0
Spillage Result:Yes Material Involved:No
Fire Result:No Estimated Speed:0
Explosion Result:No Weather Conditions:
Water Sewer Result:No Vehicle Overturn:No
Gas Dispersion:No Vehicle Left Roadway:No
Environment Damage:No Passenger Aircraft:No
No Release Result:No Cargo Baggage:
Fire EMS Report:No Ship Non Transport:No
Fire EMS EMS Report:Ship Air First Flight:No
Police Report:No Ship Air Subflight:No
Police Report No:Ship Init Transport:No
In House Cleanup:Yes Ship Phase Transfer:No
Other Cleanup:No Contact Name:MICHAEL N WINDSOR
Damage > 500:No Contact Title:MANAGER - HAZARDOUS MATERIALS
Material Loss:0 Contact Business:YELLOW TRANSPORTATION
Carrier Damage:0 Contact Street:10990 ROE AVENUE
Property Damage:0 Contact City:OVERLAND PARK
Response Cost:0 Contact State:KS
Remediation Cost:0 Contact Postal:66211
Damage Old Form:0 Contact Non US St:
Total Damages Amt:0 Contact Country:US
Hazmat Fatality:No Inc. Report Prepared:Carrier
Haz Fatal Employees:0 HMIS Serious Incidnt:No
Haz Fatal Respndrs:0 HMIS Serious Fatality:No
Haz Fatal Gen Public:0 HMIS Serious Injury:No
Tot Hazmat Fatalities:0 HMIS Flight Plan:No
Non Hazmat Fatality:No HMIS Serious Evacs:No
Non Hazmat Fatals:0 HMIS Major Artery:No
Hazmat Injury:No HMIS Bulk Release:No
Haz Hospital Empl:0 HMIS Marine Pollutnt:No
Haz Hospital Resp:0 HMIS Radioactive:No
Haz Hosp Gen Public:0 HMIS Gen Pkg Type:DRUM METAL
Haz Hosp Old Form:0 HMIS Container Code:PAIL MTL
Total Haz Hosp Inj:0 HMIS Container Desc:Metal pail, open head, capacity 10 gallons or
less
Haz Non Hosp Empl:0 HMIS Bulk Incident:No
Haz Non Hosp Resp:0 Undeclared Shipment:No
Description of Events:DURING THE UNLOADING PROCESS AN EMPLOYEE FOUND SOME SPILLED PAINT ON THE FLOOR OF A
TRAILER AT THE BASE OF SOME PAILS. THE EMPLOYEE REMOVED THE TWO PAILS AND EXAMINED
FURTHER. THEY WERE ABLE TO DETERMINE THAT THE TWO PAILS HAD BEEN RUBBING FOR SOME
TIME UNTIL ONE OF THEM DEVELOPED A LEAK. THE AFFECTED PAIL WAS REMOVED FROM THE ORDER
OF 12 AND PLACED INTO A PROPERLY MARKED, LABELED AND LINED SALVAGE DRUM PENDING
DISPOSITION.
Recommend Actions Taken:A CONTINUED EDUCATION PROGRAM TO HELP ENSURE PROPER LOADING PRACTICES. A
REINTRODUCTION OF THE PRACTICE OF USING DUNNAGE TO BLOACK AND BRACE FREIGHT.
SUPERVISORS INVOLVEMENT DURING THE ENTIRE LOADING PROCESS TO HELP ENSURE THE
FREIGHT WILL ARRIVE AT THE DESTINATION IN A SAFE MANNER. A FOCUS ON PROPER EQUIPMENT
USAGES (FORKLIFT) SO THAT THE AWARENESS LEVEL FOR THE LOCATION AND LENGTH OF THE
55 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
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FORKLIFT BLADES IS CONSTANTLY ENFORCED.
m-7-882131438-b 4 of5 E 0.11 /
557.37
4,226.79 /
1
Quality Distribution, Inc
421 John Glenn Rd
SALT LAKE CITY UT 84116

p1p-882131438-y1y
Site Program ID:UT010109 Fac County:SALT LAKE
Department ID:New9878 UTM Easting:412487.12651
Program Descriptn:Tier2 Facilities UTM Northing:4514595.87882
m-7-918263641-b 5 of5 E 0.11 /
557.37
4,226.79 /
1
VALSPAR

SALT LAKE CITY UT

p1p-918263641-y1y
Status:Active Fac Fips Code:49035
Fac Indian Cntry Flg:No Compliance Status:No Violation Identified
Fac Derived Huc:16020204 EPA Programs:RCRA
Fac Derived Wbd:160202040404 Federal Facility:No
Fac Derived Cd113:02 Federal Agency:-
Fac Derived Cb2010:490351139061080 Fac Snc Flg:No
Fac Informal Count:0 AIR Flag:No
Last Informal Action:-NPDES Flag:No
Formal Action Count:0 SDWIS Flag:No
Last Formal Action:-RCRAFlag:Yes
Fac Total Penalties:0 TRI Flag:No
Fac Penalty Count:-GHG Flag:No
Date Last Penalty:-TRI IDs:-
Last Penalty Amt:-TRI Releases Trnsfrs:-
Fac Qtrs With Nc:0 TRI on Site Releases:-
Programs With Snc:0 TRI off Site Trnsfrs:-
Fac Percent Minority:40 TRI Reporter:-
Fac Pop Den:0.53 Fac Imp Water Flg:-
Count:1 Fac Major Flag:-
Fac County:SALT LAKE Fac Active Flag:Yes
State Other :Fac Inspection Count:0
Region:08 Date Last Inspection:-
Latitude:40.77757 Days Last Inspection:-
Longitude:-112.03621
Fac Derived Tribes:-
AIR IDs:-
CAA Permit Types:-
CAA NAICS:-
CAA SICS:-
NPDES IDs:-
CWA Permit Types:-
CWA NAICS:-
CWA SICS:-
RCRA IDs:UTR000009316
RCRA Permit Types:Other
RCRA NAICS:325211 32521
SDWA IDs:-
SDWA System Types:-
SDWA Compliance Status:-
SDWA Snc Flag:No
Fac Collection Meth:ADDRESS MATCHING-HOUSE NUMBER
EJSCREEN Flag Us:Yes
EJSCREEN Report:https://ejscreen.epa.gov/mapper/mobile/EJSCREEN_mobile.aspx?geometry=%7B%22x%22:-112.03621,%22y%
22:40.77757,%22spatialReference%22:%7B%22wkid%22:4326%7D%
7D&unit=9035&areatype=&areaid=&basemap=streets&distance=1
ECHO Facility Report:https://echo.epa.gov/detailed-facility-report?fid=110031339772

Industry:Plastics and Resins
m-8-822565742-b 1 of13 ENE 0.11 /
563.52
4,222.93 /
-2
Compeq
629 North John Glenn Road
SALT LAKE CITY UT

p1p-822565742-y1y
7
7
8
TIER 2
PFAS IND
SPILLS
56 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
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DERR ID:1836 Rpt Pty Title:Gen. Affairs Supervisor
Site Desc:Rpt Pty Ph:363-7777
Date Discovered:4/8/1996 14:50 Resp Pty Ph:363-7777
Date Time Rptd:4/10/1996 8:5 Inc Hwy:
TBL Start Date:4/8/1996 Inc Mile Maker:
TBL End Date:4/8/1996 Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Hydrochloric Acid Northing:
Rpt Taken By:Mike Zucker Easting:
Rpt Pty Name:Rick Scott
Title Event Name:Compeq
ID:
Point Y:
Point X:
Incident Summary:
Spill of Hydrochloric Acid (HCL) approximately 500 gallons (RQ=540). Exterior tank for production hose coupling came off. On-site hazmat shut off
valves, pumped waste from containment area into barrels, then treated and neutralized. They have a contractor coming in to reseal cement berm. Entire
containment area consists of cement. Had some fumes, but restricted access until cleanup performed. Rick Scott replaced the hose and placed the
clamp back onto the hose.
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GW International
620 North John Glenn Road
SALT LAKE CITY UT

p1p-822567661-y1y
DERR ID:3556 Rpt Pty Title:
Site Desc:Environmental Incidents Rpt Pty Ph:
Date Discovered:08/07/2000 Resp Pty Ph:
Date Time Rptd:Inc Hwy:
TBL Start Date:Inc Mile Maker:
TBL End Date:Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Northing:4515150
Rpt Taken By:Easting:412691
Rpt Pty Name:
Title Event Name:GW International
ID:5003d00000Bb1OtAAJ
Point Y:40.782698630538
Point X:-112.034738780476
Incident Summary:
An airline broke on a load of hydrochloric acid being delivered to Compac International. About 150 gallons of acid was spilled onto the asphalt. The spill
was burmed and the acid neutralized with soda ash by TW Company.

Chemical

Spill ID:5003d00000Bb1OtAAJ
Chemical No:3556.0
Chemical:Hydrochloric Acid
Chemical Name:None
Chemical Other:None
Amount:None
Amount Type:None
Amount Other:None
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Com Tech International
620 North John Glen Road
SALT LAKE CITY UT

p1p-858111183-y1y
DERR ID:1689 Rpt Pty Title:
Site Desc:Environmental Incidents Rpt Pty Ph:
Date Discovered:12/04/1995 Resp Pty Ph:
Date Time Rptd:Inc Hwy:
TBL Start Date:Inc Mile Maker:
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TBL End Date:Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Northing:4515150
Rpt Taken By:Easting:412691
Rpt Pty Name:
Title Event Name:Com Tech International
ID:5003d00000Bb0aZAAR
Point Y:40.782698630538
Point X:-112.034738780476
Incident Summary:
Ultratech = Ammonium hydroxide @ 40%; RQ 1,000 lbs., Ammonium Chloride @ 25%; RQ 5,000 lbs., reacted with hydrogen peroxide that was
inadvertently pumped into ultratech tanks. Elgin-Dyer is head of POTW. He was alerted the incident had created waste water that could affect the
POTW. He sent a sampling team to investigate. 2 tank capacity of 1,600 gal each. 100 gal of ultratech remained in each tank. Unknown how much
discharged from Hydrogen peroxide tanker truck. Immediate reaction and cloud emerged that set off sprinkler system's eleven sprinkler heads &
knocked down cloud. Driver shut off pumps. Water amt. was approx. 1,000 gallons from sprinklers. Squeegied floor and pumped into a tank, pH - 8.3.
Waiting on samples to determine if can discharge to POTW. In-house spill response team responded, with local fire department oversight.

Chemical

Spill ID:5003d00000Bb0aZAAR
Chemical No:1689.0
Chemical:Hydrogen Peroxide
Chemical Name:None
Chemical Other:None
Amount:None
Amount Type:None
Amount Other:None

Spill ID:5003d00000Bb0aZAAR
Chemical No:1689.0
Chemical:Ammonium Hydroxide
Chemical Name:None
Chemical Other:None
Amount:None
Amount Type:None
Amount Other:None

Spill ID:5003d00000Bb0aZAAR
Chemical No:1689.0
Chemical:Ammonium Chloride
Chemical Name:None
Chemical Other:None
Amount:None
Amount Type:None
Amount Other:None
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Compeq Int'l
620 North John Glen Road
SALT LAKE CITY UT

p1p-858111354-y1y
DERR ID:1948 Rpt Pty Title:
Site Desc:Environmental Incidents Rpt Pty Ph:
Date Discovered:06/28/1996 Resp Pty Ph:
Date Time Rptd:Inc Hwy:
TBL Start Date:Inc Mile Maker:
TBL End Date:Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Northing:4515150
Rpt Taken By:Easting:412691
Rpt Pty Name:
Title Event Name:Compeq Int'l
ID:5003d00000Bb0iXAAR
Point Y:40.782698630538
Point X:-112.034738780476
Incident Summary:
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125 Gallons Ammonia Etch spilled on soil. (Ammonium Hydroxide & Ammonium Chloride). Believes Rick Scott called in release 6/28. A valve in new
system believed to have been turned wrong way. Site has 2 large spent ammonia tanks. One was full. Error occurred when switching to the other. 85
gallons released to soil, 40 caught in secondary containment. Have engaged a clean-up contractor. Etch has a distinctive blue color and is expected to
be obvious in soil. Saw pooled Etch solution after lawn sprinklers came on. 7/2 contractor found UE-50 prod. found it's way into sleeve protect. PVC pipe
of sprinkler syst. Compeq crew decontaminated soil and pipe exposed to prod.

Impacted Media

Spill ID:5003d00000Bb0iXAAR
ID:
Land Use:None
Impacted Media:Soils
Impacted Media Oth:None
Waterway Name:None
Dist to Surface Water:
In Near Water:None

Spill ID:5003d00000Bb0iXAAR
ID:
Land Use:None
Impacted Media:Soils
Impacted Media Oth:None
Waterway Name:None
Dist to Surface Water:
In Near Water:None

Chemical

Spill ID:5003d00000Bb0iXAAR
Chemical No:1948.0
Chemical:Ammonium Hydroxide
Chemical Name:None
Chemical Other:None
Amount:None
Amount Type:None
Amount Other:None

Spill ID:5003d00000Bb0iXAAR
Chemical No:1948.0
Chemical:Ammonium Chloride
Chemical Name:None
Chemical Other:None
Amount:None
Amount Type:None
Amount Other:None
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COMPEQ INTERNATIONAL, INC
620 N. JOHN GLENN RD.
SALT LAKE CITY UT 84116

p1p-866531160-y1y
Site Program ID:UT003548 Fac County:SALT LAKE
Department ID:Pending638 UTM Easting:410268.54041
Program Descriptn:Tier2 Facilities UTM Northing:4519183.81217

Tier 2 Report Year

Report Year:1997
SIC Code:
SIC Desc:
NAICS Code:
NAICS Desc:

Report Year:2006
8 TIER 2
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SIC Code:3672
SIC Desc:Printed Circuit Boards
NAICS Code:
NAICS Desc:

Report Year:2004
SIC Code:3672
SIC Desc:Printed Circuit Boards
NAICS Code:
NAICS Desc:

Report Year:2003
SIC Code:
SIC Desc:
NAICS Code:
NAICS Desc:

Report Year:2005
SIC Code:
SIC Desc:
NAICS Code:
NAICS Desc:
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Compeq
620 North John Glen Road (5600
West)
SALT LAKE CITY UT

p1p-866619851-y1y
DERR ID:4774 Rpt Pty Title:
Site Desc:Environmental Incidents Rpt Pty Ph:
Date Discovered:01/29/2003 Resp Pty Ph:
Date Time Rptd:Inc Hwy:
TBL Start Date:Inc Mile Maker:
TBL End Date:Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Northing:4515150
Rpt Taken By:Easting:412691
Rpt Pty Name:
Title Event Name:Compeq
ID:5003d00000Bb1rFAAR
Point Y:40.782698630538
Point X:-112.034738780476
Incident Summary:
Caller reports a generator blew a filter releasing 20 gallons of oil, CAS 72623-87-1 (not on the List of Lists). The spill occurred inside the facility. All but
two gallons were recovered from the containment area or surrounding floor. Approximately two gallons entered the sewer line. The caller reported the
incident to USHW and the local water treatment facility at 1365 West 2300 North that is operated by SLC Public Utilities (Steve at 799-4041). The
responsible party is planning to reconfigure their containment structure around the generator to reduce or eliminate future releases should they occur.

Impacted Media

Spill ID:5003d00000Bb1rFAAR
ID:
Land Use:None
Impacted Media:Soils
Impacted Media Oth:None
Waterway Name:None
Dist to Surface Water:
In Near Water:None

Spill ID:5003d00000Bb1rFAAR
ID:
Land Use:None
Impacted Media:Soils
Impacted Media Oth:None
Waterway Name:None
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Dist to Surface Water:
In Near Water:None
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Univar USA, Inc., Bob Sollesvik
620 North John Glenn Rd
SALT LAKE CITY UT

p1p-866619876-y1y
DERR ID:5444 Rpt Pty Title:
Site Desc:Environmental Incidents Rpt Pty Ph:
Date Discovered:09/22/2004 Resp Pty Ph:
Date Time Rptd:Inc Hwy:
TBL Start Date:Inc Mile Maker:
TBL End Date:Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Northing:4515150
Rpt Taken By:Easting:412691
Rpt Pty Name:
Title Event Name:Univar USA, Inc., Bob Sollesvik
ID:5003d00000Bb246AAB
Point Y:40.782698630538
Point X:-112.034738780476
Incident Summary:
Via the NRC report: The responsible party was pumping material into a tanker truck and the nipple on the pump failed. Spill material, cupric chloride.
Spill quantity was 40 gallons. DERR follow up: The UDEQ/SHW was notified the morning of 9/23/04. The vendor, UNIVAR, was unloading a shipment
when the pump failed and the nipple broke. The driver reacted quickly to close the valve. The spill was on concrete. The driver for UNIVAR and
COMPEQ personnel contained the spill and cleaned it up. UNIVAR will dispose of the spill materials as a hazardous material. No one was injured. The
spill quantity was estimated at 20 to 40 gallons.

Chemical

Spill ID:5003d00000Bb246AAB
Chemical No:5444.0
Chemical:Other: (describe)
Chemical Name:None
Chemical Other:CUPRIC CHLORIDE
Amount:None
Amount Type:None
Amount Other:None
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Compeq International
620 N. John Glenn Rd (6070 West)
SALT LAKE CITY UT

p1p-866620151-y1y
DERR ID:5041 Rpt Pty Title:
Site Desc:Environmental Incidents Rpt Pty Ph:
Date Discovered:09/19/2003 Resp Pty Ph:
Date Time Rptd:Inc Hwy:
TBL Start Date:Inc Mile Maker:
TBL End Date:Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Northing:4515150
Rpt Taken By:Easting:412691
Rpt Pty Name:
Title Event Name:Compeq International
ID:5003d00000Bb1wFAAR
Point Y:40.782698630538
Point X:-112.034738780476
Incident Summary:
Caller reports (CONFIDENTIALLY) he observed a release of an unknown material (gooey, bluish colored) on the lot of facility, near rear loading dock
and back toward a dumpster area. Caller observed a man spreading something on the material for a short time, but saw no other activity or attempts to
contain the material while he was on the property. Caller waited until he got home to call in his concerns. No material reached the storm drain. The
released material was not identified as to content by the caller. SLVHD (Gordon Lund) was called by DERR and he inspected the site on the evening of
the 19th. Lund called back to report (20:00 hrs) that no attempts to clean up material was being made until he arrived on the scene and made inquiries.
The facility has a lab and these personnel told Lund the material was a process rinsate material that contained Benzophenone (CAS 119-61-9, 30-60%),
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sodium hydroxide, Ristone-R, and has a high Ph (basic) value of 12 or higher. Lund felt some of the plant employees were less than forthcoming and
uncooperative while he was there. Lund suggests that appropriate agencies might want to audit the plants chemical and waste handling procedures. For
instance, is the process water discharge within permit limits, etc.

Chemical

Spill ID:5003d00000Bb1wFAAR
Chemical No:5041.0
Chemical:Other: (describe)
Chemical Name:None
Chemical Other:RISTONE-R
Amount:None
Amount Type:None
Amount Other:None

Spill ID:5003d00000Bb1wFAAR
Chemical No:5041.0
Chemical:Sodium Hydroxide
Chemical Name:None
Chemical Other:None
Amount:None
Amount Type:None
Amount Other:None

Spill ID:5003d00000Bb1wFAAR
Chemical No:5041.0
Chemical:Other: (describe)
Chemical Name:None
Chemical Other:BENZOPHENONE (CAS 119-61-9, 30-60%
Amount:None
Amount Type:None
Amount Other:None
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COMPEQ INTERNATIONAL
620 N. John Glenn Rd. (6070 West)
SALT LAKE CITY UT

p1p-866620198-y1y
DERR ID:5042 Rpt Pty Title:
Site Desc:Environmental Incidents Rpt Pty Ph:
Date Discovered:09/19/2003 Resp Pty Ph:
Date Time Rptd:Inc Hwy:
TBL Start Date:Inc Mile Maker:
TBL End Date:Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Northing:4515150
Rpt Taken By:Easting:412691
Rpt Pty Name:
Title Event Name:COMPEQ INTERNATIONAL
ID:5003d00000Bb1wGAAR
Point Y:40.782698630538
Point X:-112.034738780476
Incident Summary:
Caller reports an approximately 50 gallon spill of "PhotoResist" waste material on to concrete surface of back loading dock area of facility. Plant
employees did not follow procedures for preventing or containing a possible release. The waste material which can have a high PH value is loaded into
bags and put into dumpster to go to a landfill. The dumpster was overfilled causing release when trash truck was attempting to off load the dumpster.
The released material is a thick, gooey sludge but dries to a hard concrete like mass. The caller reports that plant employees have cleaned up the
released material. No material reached the storm drain. The caller has, on Monday the 22nd, called Allen Moore at DSHW to report to them also, and
was directed to send a written report to Dennis Downs.
Same incident was reported earlier, see report 5041.

Chemical

Spill ID:5003d00000Bb1wGAAR
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Chemical No:5042.0
Chemical:Other: (describe)
Chemical Name:None
Chemical Other:PHOTORESIST
Amount:None
Amount Type:None
Amount Other:None
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None
620 North John Glenn Road
SALT LAKE CITY UT

p1p-866620208-y1y
DERR ID:4168 Rpt Pty Title:
Site Desc:Environmental Incidents Rpt Pty Ph:
Date Discovered:10/08/2001 Resp Pty Ph:
Date Time Rptd:Inc Hwy:
TBL Start Date:Inc Mile Maker:
TBL End Date:Inc Indian Land:
TBL Imp Media:County:SALT LAKE
TBL Chemical:Northing:4515150
Rpt Taken By:Easting:412691
Rpt Pty Name:
Title Event Name:None
ID:5003d00000Bb1cwAAB
Point Y:40.782698630538
Point X:-112.034738780476
Incident Summary:
A truck carrying copper chloride splashed about 20 gallons of copper chloride on the ground. The driver used a sorbent to clean up the spilled material
and is bringing in a contractor to do further clean up. The trucking company is the responsible party but caller did not have their name.

Chemical

Spill ID:5003d00000Bb1cwAAB
Chemical No:4168.0
Chemical:Other: (describe)
Chemical Name:None
Chemical Other:COPPER CHLORIDE
Amount:None
Amount Type:None
Amount Other:None
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620 N JOHN GLENN DR
SALT LAKE CITY UT

p1p-880606948-y1y
Incident County:SALT LAKE

HMIR Historical Reports

Report No:I-1996010930 Fed DOT Agency Nm:
Report Type:A hazardous material incident Fed DOT Report No:
Date of Incident:1995-12-04 Report Submit Src:Paper
Time of Incident:1130 Inc Multiple Rows:No
Haz Class Code:Inc Non US State:
Hazardous Class:5.1 Mode Transport:Highway
Commodity Short Nm:HYDROGEN PEROXIDE, AQUEO Transport Phase:Unloading
Commodity Long Nm:HYDROGEN PEROXIDE, AQUEOUS
SOLUTIONS WITH NOT LESS THAN 20
PERCENT BUT NOT MORE THAN 40
PERCENT HYDROGEN PEROXIDE
(STABILIZED AS NECESSARY)
Incident Occrrnce:
Trade Name:PEROXIDE Mat Ship Approval?:No
ID No:UN2014 Mat Ship Approv No:
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Haz Waste Ind:No Undecl Hazmat Ship?:No
Haz Waste EPA No:Packaging Type:Portable Tank
HMIS Tox Inhalation?:No Packing Group:
TIH Hazard Zone:Carrier Reporter:MONTGOMERY TANK LINES INC
Qty Released:30 CR Street Name:3108 CENTRAL DR
Unit of Measure:Liquid - Gallon CR City:PLANT CITY
What Failed:CR State:FL
What Failed Desc:CR Postal Code:
How Failed Code:CR Non US State:
How Failed Desc:CR Fed DOT ID:0
Failure Cause Code:CR Hazmat Reg ID:
Failure Cause Desc:CR Country:US
Ident. Markings:Shipper Name:SOLCVAY INTEROX
Cont1 Pkging Type:Shipper Street Name:
Cont1 Const Mat:Shipper City:LONGVIEW
Cont1 Head Type:Shipper State:WA
Cont1 Pkg Capacity:0 Shipper Postal:
C1 Capacity UOM:Shipper Non US St:
Cont1 Pkg Amt:0 Shipper Country:US
C1 Pkg Amt UOM:Shipper Waybill:1122308
Cont1 Pkg No:1 Ship Hazmat Reg ID:
C1 Pkg NO Failed:1 Origin City:
Cont1 Pkg Mnfctr:NOT REPORTED BY CARRIER Origin State:
Cont1 Pkg Mnfct Dt:0-00-00 00:00:00 Origin Postal:
Cont1 Pkg Serial NO:Origin Non US St:
C1 Pkg Last Test Dt:0-00-00 00:00:00 Origin Country:US
C1 Test Const Mat:Destination City:SALT LAKE CITY
C1 Pkg Dsign Pres.:0 Destination State:UTAH
C1 Dsign Press UOM:Destination Postal:
C1 Pkg Shell Thick:0 Destination Non US:
C1 Shell Thick UOM:Destination Country:US
C1 Head Thickness:0 Cont2 Package Type:
C1 Head Thick UOM:Cont2 Const Mat:
C1 Pkg Srvc Pres.:0 Cont2 Pkg Capacity:0
C1 Srvc Press UOM:Cont2 Capacity UOM:
C1 Valve/Device Fail?:No Cont2 Pkg Amount:0
C1 Device Type:Cont2 Pkg Amt UOM:
C1 Device Mnfctr:Cont2 Pkg No:0
C1 Device Model:Cont2 Pkg No Failed:0
NRC No:

RAM Pkg Category:Haz NonHosp Public:0
RAM Pkg Cert.:FALSE Haz NonHosp Old:
RAM Pkg Cert. NBR:Tot Haz Non Hosp Inj:
RAM Nuclide S:Total Hazmat Injuries:0
RAM Transport Index:Evacuation Indicator:Yes
RAM UOM:Public Evacuated:0
RAM Activity Rpted:0 Employees Evac:0
RAM UOM Rpted:Total Evacuated:50
RAM Activity:0 Total Evacuation Hrs:0
RAM Activity UOM:Major Artery Closed:No
RAM Mat Safety:Mjr Artery Hrs Closed:0
Spillage Result:Yes Material Involved:No
Fire Result:No Estimated Speed:0
Explosion Result:No Weather Conditions:
Water Sewer Result:No Vehicle Overturn:No
Gas Dispersion:No Vehicle Left Roadway:No
Environment Damage:No Passenger Aircraft:No
No Release Result:No Cargo Baggage:
Fire EMS Report:No Ship Non Transport:No
Fire EMS EMS Report:Ship Air First Flight:No
Police Report:No Ship Air Subflight:No
Police Report No:Ship Init Transport:No
In House Cleanup:No Ship Phase Transfer:No
Other Cleanup:No Contact Name:JOHN MCAVOY
Damage > 500:Yes Contact Title:INSURANCE MGR
Material Loss:5000 Contact Business:
Carrier Damage:0 Contact Street:
Property Damage:0 Contact City:
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Response Cost:0 Contact State:
Remediation Cost:5000 Contact Postal:
Damage Old Form:0 Contact Non US St:
Total Damages Amt:10000 Contact Country:US
Hazmat Fatality:No Inc. Report Prepared:
Haz Fatal Employees:0 HMIS Serious Incidnt:Yes
Haz Fatal Respndrs:0 HMIS Serious Fatality:No
Haz Fatal Gen Public:0 HMIS Serious Injury:No
Tot Hazmat Fatalities:0 HMIS Flight Plan:No
Non Hazmat Fatality:No HMIS Serious Evacs:Yes
Non Hazmat Fatals:0 HMIS Major Artery:No
Hazmat Injury:No HMIS Bulk Release:No
Haz Hospital Empl:0 HMIS Marine Pollutnt:No
Haz Hospital Resp:0 HMIS Radioactive:No
Haz Hosp Gen Public:0 HMIS Gen Pkg Type:TANK
Haz Hosp Old Form:0 HMIS Container Code:TANK TRK
Total Haz Hosp Inj:0 HMIS Container Desc:Tank truck, tank mounted on truck chassis
Haz Non Hosp Empl:0 HMIS Bulk Incident:Yes
Haz Non Hosp Resp:0 Undeclared Shipment:No
Description of Events:MTL DRIVER UNLOADED HYDROGEN PEROXIDE INTO A STORAGE TANK CONTAINING ACUGARD, A
AMMONIA BASED SOLUTION. THE 2 PRODUCTS REACTED & CREATED A BOIL OVER. APPROX. 20-30
ALLONS OF PRODUCT BOILED OVER INTO A CONTAINMENT AREA. CLEAN-UP WAS HANDLED BY
CONSIGNEE'S IN-HOUSE EMERGENCY RESPONSE TEAM. THE BUILDING & STORAGE TANK WAS
STABILIZED. NO INJURIES REPORTED. CLEAN UP WENT WITH NO FURTHER PROBLEMS. THE
REMAINING PRODUCT OF OFF-LOADED INTO THE PROPER TANK, NO PROBLEMS.
Recommend Actions Taken:
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620 N JOHN GLENN RD
SALT LAKE CITY UT

p1p-880656862-y1y
Incident County:SALT LAKE

HMIR Historical Reports

Report No:I-2004120609 Fed DOT Agency Nm:
Report Type:A hazardous material incident Fed DOT Report No:
Date of Incident:2004-09-23 Report Submit Src:Paper
Time of Incident:1600 Inc Multiple Rows:No
Haz Class Code:Inc Non US State:
Hazardous Class:8 Mode Transport:Highway
Commodity Short Nm:CORROSIVE LIQUID, ACIDIC Transport Phase:Loading
Commodity Long Nm:CORROSIVE LIQUID, ACIDIC, INORGANIC,
N.O.S.
Incident Occrrnce:
Trade Name:SPENT CUPRIC CHLORID Mat Ship Approval?:No
ID No:UN3264 Mat Ship Approv No:
Haz Waste Ind:No Undecl Hazmat Ship?:No
Haz Waste EPA No:Packaging Type:Cargo Tank Motor Vehicle (CTMV)
HMIS Tox Inhalation?:No Packing Group:
TIH Hazard Zone:Carrier Reporter:UNIVAR USA
Qty Released:40 CR Street Name:6100 CARILLON POINT
Unit of Measure:Liquid - Gallon CR City:KIRKLAND
What Failed:102; 141 CR State:WA
What Failed Desc:Auxiliary Valve; Piping or Fittings CR Postal Code:98033
How Failed Code:303;CR Non US State:
How Failed Desc:Burst or Ruptured;CR Fed DOT ID:28633
Failure Cause Code:508;CR Hazmat Reg ID:
Failure Cause Desc:Defective Component or Device;CR Country:US
Ident. Markings:Shipper Name:COMPEG INTL CORP
Cont1 Pkging Type:Shipper Street Name:620 N JOHN GLENN RD
Cont1 Const Mat:Shipper City:SALT LAKE CITY
Cont1 Head Type:Shipper State:UT
Cont1 Pkg Capacity:5000 Shipper Postal:84116
C1 Capacity UOM:LGA Shipper Non US St:
Cont1 Pkg Amt:0 Shipper Country:US
C1 Pkg Amt UOM:Shipper Waybill:
Cont1 Pkg No:1 Ship Hazmat Reg ID:
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C1 Pkg NO Failed:1 Origin City:
Cont1 Pkg Mnfctr:POLAR TANK TRAILER INC Origin State:
Cont1 Pkg Mnfct Dt:0-00-00 00:00:00 Origin Postal:
Cont1 Pkg Serial NO:L1-10287 Origin Non US St:
C1 Pkg Last Test Dt:2004-06-29 00:00:00 Origin Country:US
C1 Test Const Mat:Destination City:SALT LAKE CITY
C1 Pkg Dsign Pres.:0 Destination State:UTAH
C1 Dsign Press UOM:Destination Postal:84104
C1 Pkg Shell Thick:0 Destination Non US:
C1 Shell Thick UOM:Destination Country:US
C1 Head Thickness:0 Cont2 Package Type:
C1 Head Thick UOM:Cont2 Const Mat:
C1 Pkg Srvc Pres.:0 Cont2 Pkg Capacity:0
C1 Srvc Press UOM:Cont2 Capacity UOM:
C1 Valve/Device Fail?:No Cont2 Pkg Amount:0
C1 Device Type:Cont2 Pkg Amt UOM:
C1 Device Mnfctr:Cont2 Pkg No:0
C1 Device Model:Cont2 Pkg No Failed:0
NRC No:

RAM Pkg Category:Haz NonHosp Public:0
RAM Pkg Cert.:FALSE Haz NonHosp Old:
RAM Pkg Cert. NBR:Tot Haz Non Hosp Inj:
RAM Nuclide S:Total Hazmat Injuries:0
RAM Transport Index:Evacuation Indicator:No
RAM UOM:Public Evacuated:0
RAM Activity Rpted:0 Employees Evac:0
RAM UOM Rpted:Total Evacuated:0
RAM Activity:0 Total Evacuation Hrs:0
RAM Activity UOM:Major Artery Closed:No
RAM Mat Safety:Mjr Artery Hrs Closed:0
Spillage Result:Yes Material Involved:No
Fire Result:No Estimated Speed:0
Explosion Result:No Weather Conditions:
Water Sewer Result:No Vehicle Overturn:No
Gas Dispersion:No Vehicle Left Roadway:No
Environment Damage:No Passenger Aircraft:No
No Release Result:No Cargo Baggage:
Fire EMS Report:No Ship Non Transport:No
Fire EMS EMS Report:Ship Air First Flight:No
Police Report:No Ship Air Subflight:No
Police Report No:Ship Init Transport:No
In House Cleanup:No Ship Phase Transfer:No
Other Cleanup:No Contact Name:ROBERT SOLLESVIK
Damage > 500:No Contact Title:BRANCH OPERATIONS MANAGER
Material Loss:200 Contact Business:
Carrier Damage:50 Contact Street:
Property Damage:0 Contact City:
Response Cost:0 Contact State:
Remediation Cost:250 Contact Postal:
Damage Old Form:0 Contact Non US St:
Total Damages Amt:500 Contact Country:US
Hazmat Fatality:No Inc. Report Prepared:
Haz Fatal Employees:0 HMIS Serious Incidnt:No
Haz Fatal Respndrs:0 HMIS Serious Fatality:No
Haz Fatal Gen Public:0 HMIS Serious Injury:No
Tot Hazmat Fatalities:0 HMIS Flight Plan:No
Non Hazmat Fatality:No HMIS Serious Evacs:No
Non Hazmat Fatals:0 HMIS Major Artery:No
Hazmat Injury:No HMIS Bulk Release:No
Haz Hospital Empl:0 HMIS Marine Pollutnt:No
Haz Hospital Resp:0 HMIS Radioactive:No
Haz Hosp Gen Public:0 HMIS Gen Pkg Type:TANK
Haz Hosp Old Form:0 HMIS Container Code:MC312
Total Haz Hosp Inj:0 HMIS Container Desc:Cargo tanks
Haz Non Hosp Empl:0 HMIS Bulk Incident:Yes
Haz Non Hosp Resp:0 Undeclared Shipment:No
Description of Events:WHILE MAKING A PICK-UP OF SPENT CUPRIC CHLORIDE ON 9/22/04, THE TANKER TRAILER AIR
DIAPHRAGM PUMP HAD A FLANGE FITTING FAILURE THAT RESULTED IN A RELEASE OF PRODUCT IN
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THE LOADING BAY AT COMPEQ INTERNATIONAL, MIKE KOMIS, UNIVAR DRIVER IMMEDIATELY SHUT OFF
THE AIR AND TANKER FILL VALVES, NOTIFIED COMPEQ'S WASTEWATER TECHNICIANS AND BEGAN
CONTAINING THE SPILLED PRODUCT. HE WAS ABLE TO PREVENT ANY OFF SITE MIGRATION BY
PLACING CHEMICAL ABSORBENT SOCKS AT THE LOW SPOT WHILE THE COMPEQ TECHNICIANS
ASSISTED IN MOPPING UP THE RELEASE. THIS INCIDENT OCCURRED AT 4:00 PM, MST. MIKE NOTIFIED
ME, BOB SOLLESVIK, OF THE INCIDENT AT 4:10 PM MST. I THEN CONTACTED MY REGIONAL
OPERATIONS MANAGER, CHARLY BONNIE AND DISTRICT MANAGER, LARRY DAVIS BEFORE
PROCEEDING TO THE SPILL SITE. UPON ARRIVAL I MET TED WITTE, COMPEQ INTERNATIONAL
ADMINISTRATIVE MANAGER WHO WAS OVERSEEING THE CLEAN-UP. MOST OF THE RAW PRODUCT
HAD BEEN RECOVERED INTO THE LARGE CATCH BASIN BELOW THE CHEMICAL FILL FITTINGS. THE
COMPEQ EMPLOYEES HAD ALREADY WASHED DOWN THE TRUCK, CONCRETE RAMP AND DRIVE AND
WERE MOPPING UP AS I WAS TAKING PICTURES AND REVIEWING THE DAMAGED PUMP. THE
RECLAIMED MIXTURE OF SPENT CUPRIC CHLORIDE AND WATER, (APPROX. 80-90 GAL.), WAS
TRANSFERRED TO THE TANKER AFTER REPAIRS WERE MADE TO THE PUMP. ROOT CAUSE: THERE
ARE THREE POSSIBLE SCENARIOS THAT COULD HAVE CONTRIBUTED TO THIS INCIDENT. 1. THE
OUTLET CONNECTION ON THE T/T PUMP HAD A 1 1/2" NIPPLE BETWEEN THE FLANGE AND THE 2"
CAMLOCK FITTING. WITH EACH CONTINUOUS CAVITATION OF THE PUMP, THERE IS A TREMENDOUS
AMOUNT OF PRESSURE AND VIBRATION THAT OVER TIME CAN WEAKEN THE PVC FITTING CAUSING IT
TO SNAP. A SUPPORT FOR THE HOSE COULD ALLEVIATE THIS. 2. THE 1 1/2" NIPPLE BETWEEN THE
OUTLET FLANGE AND 2" CAMLOCK FITTING WAS BOTTOMED OUT AND GLUED TO THE FLANGE WHICH
COULD HAVE BEEN TO STOP PREVIOUS LEAKING OR LOOSENESS OF THE THREADS. 3. HAVING A 1 1/2"
PUMP BETWEEN 2" SUCTION AND DISCHARGE HOSES COULD BE CONTRIBUTING TO THE HIGH FLOW
PRESSURE ON THE DISCHARGE SIDE. A 2" PUMP COULD ALLEVIATE THIS BY HAVING A CONSISTENT
FLOW FROM THE SUPPLY TANK TO THE TANKER TRAILER. CORRECTIVE ACTION: AFTER A REVIEW OF
THE INCIDENT WITH THE UNIVAR SAFETY COMMITTEE, WE HAVE DETERMINED THE MOST
REASONABLE CAUSE FOR THE FITTING FAILURE WAS DUE TO STRESS PLACED ON THE OUTLET
CONNECTION OF THE TRANSFER HOSE. WE HAVE CONTACTED OUR HOSE SUPPLIER TO MODIFY THE
CURRENT HOSE BY SHORTENING IT TO LESSEN THE STRESS ON THE PUMP CONNECTIONS AND WILL
HAVE BRACE INSTALLED TO SUPPORT THE OUTLET FLANGE SIMILAR TO THE INLET CONNECTION. WE
WILL TEST THE PROCESS BEFORE OUR NEXT SCHEDULED PICK UP TO INSURE IT'S SAFE OPERABILITY.
SIDE NOTE: AFTER REPLACING THE EXISTING DISCHARGE HOSE WITH A SHORTER LENGTH AND
REPLACING THE OUTLET FLANGE FITTINGS, WE TESTED THE PUMP AND NOTICED A SIZEABLE
LESSENING OF PRESSURE AND TORQUE ON THE OUTLET FLANGE. WILL MOVE FORWARD ON BRACING
THE FLANGE AND CONTINUE TO MONITOR THE CHANGES.
Recommend Actions Taken:
m-8-918308715-b 13 of13 ENE 0.11 /
563.52
4,222.93 /
-2
PRINTED CIRCUIT BOARD
MANUFACTURING

SALT LAKE CITY UT

p1p-918308715-y1y
Status:Active Fac Fips Code:49035
Fac Indian Cntry Flg:No Compliance Status:No Violation Identified
Fac Derived Huc:16020204 EPA Programs:CWA; RCRA
Fac Derived Wbd:160202040404 Federal Facility:No
Fac Derived Cd113:02 Federal Agency:-
Fac Derived Cb2010:490351139061080 Fac Snc Flg:No
Fac Informal Count:0 AIR Flag:No
Last Informal Action:6/22/2004 NPDES Flag:Yes
Formal Action Count:0 SDWIS Flag:No
Last Formal Action:11/3/1998 RCRAFlag:Yes
Fac Total Penalties:0 TRI Flag:No
Fac Penalty Count:-GHG Flag:No
Date Last Penalty:11/3/1998 TRI IDs:84116CMPQN620NO
Last Penalty Amt:7000 TRI Releases Trnsfrs:-
Fac Qtrs With Nc:0 TRI on Site Releases:-
Programs With Snc:0 TRI off Site Trnsfrs:-
Fac Percent Minority:50 TRI Reporter:-
Fac Pop Den:0.44 Fac Imp Water Flg:Yes
Count:1 Fac Major Flag:-
Fac County:SALT LAKE Fac Active Flag:Yes
State Other :Fac Inspection Count:1
Region:08 Date Last Inspection:10/11/2019
Latitude:40.78265 Days Last Inspection:1807
Longitude:-112.03624
Fac Derived Tribes:-
AIR IDs:-
CAA Permit Types:-
CAA NAICS:-
8 PFAS IND
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CAA SICS:-
NPDES IDs:UTR000375
CWA Permit Types:Non-M
CWA NAICS:334412
CWA SICS:3672
RCRA IDs:UTD988070215
RCRA Permit Types:SQG
RCRA NAICS:339112 325211
SDWA IDs:-
SDWA System Types:-
SDWA Compliance Status:-
SDWA Snc Flag:No
Fac Collection Meth:ADDRESS MATCHING-HOUSE NUMBER
EJSCREEN Flag Us:Yes
EJSCREEN Report:https://ejscreen.epa.gov/mapper/mobile/EJSCREEN_mobile.aspx?geometry=%7B%22x%22:-112.03624,%22y%
22:40.78265,%22spatialReference%22:%7B%22wkid%22:4326%7D%
7D&unit=9035&areatype=&areaid=&basemap=streets&distance=1
ECHO Facility Report:https://echo.epa.gov/detailed-facility-report?fid=110022400846

Industry:Metal Machinery Mfg

Industry:Electronics Industry

Industry:Metal Coating

Industry:Plastics and Resins
m-9-879472007-b 1 of2 ESE 0.12 /
613.88
4,226.66 /
1
AMAZON.COM SERVICES, LLC. -
SLC3
355 NORTH JOHN GLENN ROAD
SALT LAKE CITY UT 84116

p1p-879472007-y1y
EPA Handler ID:UTR000015404
Gen Status Universe:Small Quantity Generator
Contact Name:PAUL WILSON
Contact Address:NA ENVIRONMENTAL DEPARTMENT-AMAZON.COM , PO BOX 80842 , SEATTLE , WA, 98108 , US
Contact Phone No and Ext:800-575-0171
Contact Email:[e-mail]
Contact Country:US
County Name:SALT LAKE
EPA Region:08
Land Type:Private
Receive Date:20231222
Location Latitude:40.779945
Location Longitude:-112.036212

Violation/Evaluation Summary

Note:NO VIOLATIONS: All of the compliance records associated with this facility (EPA ID) indicate NO VIOLATIONS;
Compliance Monitoring and Enforcement table dated Apr, 2024.

Evaluation Details

Evaluation Start Date:20191119
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Handler Summary

Importer Activity:No
Mixed Waste Generator:No
Transporter Activity:No
Transfer Facility:No
9 RCRA SQG
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Onsite Burner Exemption:No
Furnace Exemption:No
Underground Injection Activity:No
Commercial TSD:No
Used Oil Transporter:No
Used Oil Transfer Facility:No
Used Oil Processor:No
Used Oil Refiner:No
Used Oil Burner:No
Used Oil Market Burner:No
Used Oil Spec Marketer:No

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20190830
Handler Name:AMAZON.COM SERVICES INC. SLC3
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D016
Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE
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Hazardous Waste Code:P075
Waste Code Description:NICOTINE, & SALTS (OR) PYRIDINE, 3-(1-METHYL-2-PYRROLIDINYL)-,(S)-, & SALTS

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20191212
Handler Name:AMAZON.COM SERVICES, LLC. - SLC3
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Implementer

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D016
Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

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Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:P075
Waste Code Description:NICOTINE, & SALTS (OR) PYRIDINE, 3-(1-METHYL-2-PYRROLIDINYL)-,(S)-, & SALTS

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20230214
Handler Name:AMAZON.COM SERVICES, LLC. - SLC3
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
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Waste Code Description:SILVER

Hazardous Waste Code:D016
Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:P075
Waste Code Description:NICOTINE, & SALTS (OR) PYRIDINE, 3-(1-METHYL-2-PYRROLIDINYL)-,(S)-, & SALTS

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Hazardous Waste Handler Details

Sequence No:3
Receive Date:20231222
Handler Name:AMAZON.COM SERVICES, LLC. - SLC3
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD
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Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D016
Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:P075
Waste Code Description:NICOTINE, & SALTS (OR) PYRIDINE, 3-(1-METHYL-2-PYRROLIDINYL)-,(S)-, & SALTS

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Owner/Operator Details

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:NA ENVIRONMENTAL DEPARTMENT-
AMAZON.COM
Name:AMAZON.COM SERVICES, LLC Street 2:PO BOX 80842
Date Became Current:20191230 City:SEATTLE
Date Ended Current:State:WA
Phone:[phone] Country:US
Source Type:Notification Zip Code:98108

Owner/Operator Ind:Current Owner Street No:9830
Type:Private Street 1:COLONNADE BLVD SUITE 600
Name:USRLP SLC II, LLC Street 2:
Date Became Current:20170428 City:SAN ANTONIO
Date Ended Current:State:TX
Phone:[phone] Country:US
Source Type:Notification Zip Code:78230

Owner/Operator Ind:Current Owner Street No:9830
Type:Private Street 1:COLONNADE BLVD SUITE 600
Name:USRLP SLC II, LLC Street 2:
Date Became Current:20170428 City:SAN ANTONIO
Date Ended Current:State:TX
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Phone:[phone] Country:US
Source Type:Implementer Zip Code:78230

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:P.O BOX 80842
Name:AMAZON.COM Street 2:
Date Became Current:20180802 City:SEATTLE
Date Ended Current:State:WA
Phone:[phone] Country:US
Source Type:Implementer Zip Code:98108

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:AMAZON.COM SERVICES, LLC Street 2:
Date Became Current:20191230 City:
Date Ended Current:State:
Phone:Country:
Source Type:Implementer Zip Code:

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:P.O BOX 80842
Name:AMAZON.COM Street 2:
Date Became Current:20180802 City:SEATTLE
Date Ended Current:State:WA
Phone:[phone] Country:US
Source Type:Notification Zip Code:98108

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:NA ENVIRONMENTAL DEPARTMENT-
AMAZON.COM
Name:AMAZON.COM Street 2:PO BOX 80842
Date Became Current:20180802 City:SEATTLE
Date Ended Current:State:WA
Phone:[phone] Country:US
Source Type:Notification Zip Code:98108

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:PO BOX 80842
Name:AMAZON.COM SERVICES, LLC Street 2:
Date Became Current:20191230 City:SEATTLE
Date Ended Current:State:WA
Phone:Country:US
Source Type:Notification Zip Code:98108

Historical Handler Details

Receive Dt:20230214
Generator Code Description:Small Quantity Generator
Handler Name:AMAZON.COM SERVICES, LLC. - SLC3

Receive Dt:20191212
Generator Code Description:Small Quantity Generator
Handler Name:AMAZON.COM SERVICES, LLC. - SLC3

Receive Dt:20190830
Generator Code Description:Small Quantity Generator
Handler Name:AMAZON.COM SERVICES INC. SLC3
m-9-882131574-b 2 of2 ESE 0.12 /
613.88
4,226.66 /
1
Amazoncom Services, LLC - SLC3
355 John Glenn Rd
SALT LAKE CITY UT 84116

p1p-882131574-y1y
Site Program ID:UT010232 Fac County:SALT LAKE
Department ID:New10002 UTM Easting:412445.20005
Program Descriptn:Tier2 Facilities UTM Northing:4514242.80008
9 TIER 2
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m-10-885970234-b 1 of2 NE 0.12 /
640.53
4,221.67 /
-4
AMAZON.COM SERVICES LLC
SLC9
808 N. 6550 W. SLC GLOBAL
LOGISITICS CTR BUILDING 3
SALT LAKE CITY UT 84116

p1p-885970234-y1y
EPA Handler ID:UTR000015859
Gen Status Universe:Small Quantity Generator
Contact Name:NATALIE WAID
Contact Address:PO BOX 80842 , , SEATTLE , WA, 98108 , US
Contact Phone No and Ext:206-266-1036
Contact Email:[e-mail]
Contact Country:US
County Name:SALT LAKE
EPA Region:08
Land Type:Private
Receive Date:20230214
Location Latitude:40.84193
Location Longitude:-111.953211

Violation/Evaluation Summary

Note:NO RECORDS: As of Apr 2024, there are no Compliance Monitoring and Enforcement (violation) records
associated with this facility (EPA ID).

Handler Summary

Importer Activity:No
Mixed Waste Generator:No
Transporter Activity:No
Transfer Facility:No
Onsite Burner Exemption:No
Furnace Exemption:No
Underground Injection Activity:No
Commercial TSD:No
Used Oil Transporter:No
Used Oil Transfer Facility:No
Used Oil Processor:No
Used Oil Refiner:No
Used Oil Burner:No
Used Oil Market Burner:No
Used Oil Spec Marketer:No

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20201008
Handler Name:AMAZON.COM SERVICES LLC SLC9
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
10 RCRA SQG
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Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D016
Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20230214
Handler Name:AMAZON.COM SERVICES LLC SLC9
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE
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Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D009
Waste Code Description:MERCURY

Hazardous Waste Code:D010
Waste Code Description:SELENIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D016
Waste Code Description:2,4-D (2,4-DICHLOROPHENOXYACETIC ACID)

Hazardous Waste Code:D018
Waste Code Description:BENZENE

Hazardous Waste Code:D024
Waste Code Description:M-CRESOL

Hazardous Waste Code:D027
Waste Code Description:1,4-DICHLOROBENZENE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U129
Waste Code Description:CYCLOHEXANE, 1,2,3,4,5,6-HEXACHLORO-, (1ALPHA, 2ALPHA, 3BETA, 4ALPHA, 5ALPHA, 6BETA)- (OR)
LINDANE

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U205
Waste Code Description:SELENIUM SULFIDE (OR) SELENIUM SULFIDE SES2 (R,T)

Owner/Operator Details

Owner/Operator Ind:Current Owner Street No:166
Type:Private Street 1:EAST 14000 SOUTH SUITE 210
Name:PHASE I GLC 3 LLC Street 2:
Date Became Current:20200721 City:DRAPER
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84020

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:PO BOX 80842
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Name:AMAZON.COM SERVICES LLC Street 2:
Date Became Current:20200721 City:SEATTLE
Date Ended Current:State:WA
Phone:[phone] Country:US
Source Type:Notification Zip Code:98108

Historical Handler Details

Receive Dt:20201008
Generator Code Description:Small Quantity Generator
Handler Name:AMAZON.COM SERVICES LLC SLC9
m-10-898864125-b 2 of2 NE 0.12 /
640.53
4,221.67 /
-4
Amazoncom Services LLC - SLC9
808 N 6550 W
SALT LAKE CITY UT 84116

p1p-898864125-y1y
Site Program ID:UT010645 Fac County:SALT LAKE
Department ID:New10443 UTM Easting:411688.8174
Program Descriptn:Tier2 Facilities UTM Northing:4515513.59346
m-11-867211001-b 1 of2 ENE 0.15 /
810.58
4,228.84 /
4
BIOMERICS LLC
6030 W HAROLD GATTY DR
SALT LAKE CITY UT 84116

p1p-867211001-y1y
EPA Handler ID:UTD988070215
Gen Status Universe:Small Quantity Generator
Contact Name:JASON CUTLER
Contact Address:11111 , SANTA MONICA BLVD SUITE 600 , , LOS ANGELES , CA, 90025 , US
Contact Phone No and Ext:775-857-7252
Contact Email:[e-mail]
Contact Country:US
County Name:SALT LAKE
EPA Region:08
Land Type:Private
Receive Date:20210112
Location Latitude:40.781309
Location Longitude:-112.020967

Violation/Evaluation Summary

Note:VIOLATION or UNDETERMINED: There are VIOLATION or UNDETERMINED details or records associated with
this facility (EPA ID) in the Compliance Monitoring and Enforcement table dated Apr, 2024.

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20191011
Scheduled Compliance Date:
Return to Compliance:Documented
Actual Return to Compl:20191017
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:110
Enforcement Type Description:VERBAL INFORMAL
Enforcement Action Date:20191011
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
10
11
TIER 2
RCRA SQG
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Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20191011
Scheduled Compliance Date:
Return to Compliance:Documented
Actual Return to Compl:20191011
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:110
Enforcement Type Description:VERBAL INFORMAL
Enforcement Action Date:20191011
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - r315-7-11.3(C)
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20040622
Scheduled Compliance Date:20040722
Return to Compliance:Documented
Actual Return to Compl:20040628
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20040622
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - R315-7-11.3(E)
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20040622
Scheduled Compliance Date:20040722
Return to Compliance:Documented
Actual Return to Compl:20040628
Violation Responsible Agency:State
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Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20040622
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - r315-13
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - r315-5-4
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
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Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - r315-5-2
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - Pre-transport
Violation Type:262.C
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

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Enforcement Details

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - General
Violation Type:264.A
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - General Facility Standards
Violation Type:264.B
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
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Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - Preparedness and Prevention
Violation Type:264.C
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - Contingency Plan and Emergency Procedures
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Violation Type:264.D
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - Container Use and Management
Violation Type:264.I
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Evaluation Details
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Evaluation Start Date:20191011
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20191017
Evaluation Agency:State

Evaluation Start Date:20191011
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20191011
Evaluation Agency:State

Evaluation Start Date:20131120
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:20090817
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:20040107
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20040628
Evaluation Agency:State

Evaluation Start Date:19980312
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:EPA-Initiated Oversight/Observation/Training Actions

Evaluation Start Date:19980312
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - General Facility Standards
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - General
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - Preparedness and Prevention
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - Contingency Plan and Emergency Procedures
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
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Violation Short Description:Generators - Pre-transport
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - Container Use and Management
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:19940506
Evaluation Agency:State

Handler Summary

Importer Activity:No
Mixed Waste Generator:No
Transporter Activity:No
Transfer Facility:No
Onsite Burner Exemption:No
Furnace Exemption:No
Underground Injection Activity:No
Commercial TSD:No
Used Oil Transporter:No
Used Oil Transfer Facility:No
Used Oil Processor:No
Used Oil Refiner:No
Used Oil Burner:No
Used Oil Market Burner:No
Used Oil Spec Marketer:No

Hazardous Waste Handler Details

Sequence No:1
Receive Date:19910125
Handler Name:COMPEG INTERNATIONAL COMPANY
Federal Waste Generator Code:3
Generator Code Description:Very Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:1
Receive Date:19920522
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report

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Hazardous Waste Handler Details

Sequence No:2
Receive Date:19940225
Handler Name:COMPEQ INTERNATIONAL CORP.
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report

Hazardous Waste Handler Details

Sequence No:3
Receive Date:19960314
Handler Name:COMPEQ INTERNATIONAL CORP.
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report

Hazardous Waste Handler Details

Sequence No:4
Receive Date:19980803
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report

Hazardous Waste Handler Details

Sequence No:5
Receive Date:20010521
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report

Hazardous Waste Handler Details

Sequence No:6
Receive Date:20020313
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
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PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Code:F007
Waste Code Description:SPENT CYANIDE PLATING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS.

Hazardous Waste Handler Details

Sequence No:7
Receive Date:20040209
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Code:F007
Waste Code Description:SPENT CYANIDE PLATING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS.

Hazardous Waste Code:F008
Waste Code Description:PLATING BATH RESIDUES FROM THE BOTTOM OF PLATING BATHS FROM ELECTROPLATING
OPERATIONS IN WHICH CYANIDES ARE USED IN THE PROCESS.

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20040225
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE
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Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Code:F007
Waste Code Description:SPENT CYANIDE PLATING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS.

Hazardous Waste Handler Details

Sequence No:8
Receive Date:20060123
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Code:F007
Waste Code Description:SPENT CYANIDE PLATING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS.

Hazardous Waste Code:F008
Waste Code Description:PLATING BATH RESIDUES FROM THE BOTTOM OF PLATING BATHS FROM ELECTROPLATING
OPERATIONS IN WHICH CYANIDES ARE USED IN THE PROCESS.

Hazardous Waste Code:F009
Waste Code Description:SPENT STRIPPING AND CLEANING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS IN WHICH
CYANIDES ARE USED IN THE PROCESS.

Hazardous Waste Handler Details

Sequence No:9
Receive Date:20080220
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
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Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:3
Receive Date:20100329
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F006
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Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20100505
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report update with Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:4
Receive Date:20130611
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.
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Hazardous Waste Handler Details

Sequence No:1
Receive Date:20131126
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:N
Generator Code Description:Not a Generator, Verified
Source Type:Implementer

Hazardous Waste Handler Details

Sequence No:5
Receive Date:20150907
Handler Name:B.H. JOHN GLENN ROAD LLC (FORMERLY COMPEQ INTERNATIONAL)
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20160229
Handler Name:B.H. JOHN GLENN ROAD LLC (FORMERLY COMPEQ INTERNATIONAL)
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report update with Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Handler Details

Sequence No:6
Receive Date:20180430
Handler Name:BIOMERICS LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

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Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D022
Waste Code Description:CHLOROFORM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:D038
Waste Code Description:PYRIDINE

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:P024
Waste Code Description:BENZENAMINE, 4-CHLORO- (OR) P-CHLORANILINE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U003
Waste Code Description:ACETONITRILE (I,T)

Hazardous Waste Code:U034
Waste Code Description:ACETALDEHYDE, TRICHLORO- (OR) CHLORAL

Hazardous Waste Code:U044
Waste Code Description:CHLOROFORM (OR) METHANE, TRICHLORO-

Hazardous Waste Code:U056
Waste Code Description:BENZENE, HEXAHYDRO- (I) (OR) CYCLOHEXANE (I)

Hazardous Waste Code:U057
Waste Code Description:CYCLOHEXANONE (I)

Hazardous Waste Code:U123
Waste Code Description:FORMIC ACID (C,T)

Hazardous Waste Code:U134
Waste Code Description:HYDROFLUORIC ACID (C,T) (OR) HYDROGEN FLUORIDE (C,T)

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

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Hazardous Waste Code:U188
Waste Code Description:PHENOL

Hazardous Waste Code:U196
Waste Code Description:PYRIDINE

Hazardous Waste Code:U210
Waste Code Description:ETHENE, TETRACHLORO- (OR) TETRACHLOROETHYLENE

Hazardous Waste Code:U213
Waste Code Description:FURAN, TETRAHYDRO-(I) (OR) TETRAHYDROFURAN (I)

Hazardous Waste Code:U220
Waste Code Description:BENZENE, METHYL- (OR) TOLUENE

Hazardous Waste Code:U223
Waste Code Description:BENZENE, 1,3-DIISOCYANATOMETHYL- (R,T) (OR) TOLUENE DIISOCYANATE (R,T)

Hazardous Waste Handler Details

Sequence No:7
Receive Date:20181010
Handler Name:BIOMERICS LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D022
Waste Code Description:CHLOROFORM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:D038
Waste Code Description:PYRIDINE

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.
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Hazardous Waste Code:P024
Waste Code Description:BENZENAMINE, 4-CHLORO- (OR) P-CHLORANILINE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U003
Waste Code Description:ACETONITRILE (I,T)

Hazardous Waste Code:U034
Waste Code Description:ACETALDEHYDE, TRICHLORO- (OR) CHLORAL

Hazardous Waste Code:U044
Waste Code Description:CHLOROFORM (OR) METHANE, TRICHLORO-

Hazardous Waste Code:U056
Waste Code Description:BENZENE, HEXAHYDRO- (I) (OR) CYCLOHEXANE (I)

Hazardous Waste Code:U057
Waste Code Description:CYCLOHEXANONE (I)

Hazardous Waste Code:U123
Waste Code Description:FORMIC ACID (C,T)

Hazardous Waste Code:U134
Waste Code Description:HYDROFLUORIC ACID (C,T) (OR) HYDROGEN FLUORIDE (C,T)

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U188
Waste Code Description:PHENOL

Hazardous Waste Code:U196
Waste Code Description:PYRIDINE

Hazardous Waste Code:U210
Waste Code Description:ETHENE, TETRACHLORO- (OR) TETRACHLOROETHYLENE

Hazardous Waste Code:U213
Waste Code Description:FURAN, TETRAHYDRO-(I) (OR) TETRAHYDROFURAN (I)

Hazardous Waste Code:U220
Waste Code Description:BENZENE, METHYL- (OR) TOLUENE

Hazardous Waste Code:U223
Waste Code Description:BENZENE, 1,3-DIISOCYANATOMETHYL- (R,T) (OR) TOLUENE DIISOCYANATE (R,T)

Hazardous Waste Handler Details

Sequence No:8
Receive Date:20210112
Handler Name:BIOMERICS LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
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Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D022
Waste Code Description:CHLOROFORM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:D038
Waste Code Description:PYRIDINE

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:P024
Waste Code Description:BENZENAMINE, 4-CHLORO- (OR) P-CHLORANILINE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U003
Waste Code Description:ACETONITRILE (I,T)

Hazardous Waste Code:U034
Waste Code Description:ACETALDEHYDE, TRICHLORO- (OR) CHLORAL

Hazardous Waste Code:U044
Waste Code Description:CHLOROFORM (OR) METHANE, TRICHLORO-

Hazardous Waste Code:U056
Waste Code Description:BENZENE, HEXAHYDRO- (I) (OR) CYCLOHEXANE (I)

Hazardous Waste Code:U057
Waste Code Description:CYCLOHEXANONE (I)

Hazardous Waste Code:U123
Waste Code Description:FORMIC ACID (C,T)

Hazardous Waste Code:U134
Waste Code Description:HYDROFLUORIC ACID (C,T) (OR) HYDROGEN FLUORIDE (C,T)

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U188
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Waste Code Description:PHENOL

Hazardous Waste Code:U196
Waste Code Description:PYRIDINE

Hazardous Waste Code:U210
Waste Code Description:ETHENE, TETRACHLORO- (OR) TETRACHLOROETHYLENE

Hazardous Waste Code:U213
Waste Code Description:FURAN, TETRAHYDRO-(I) (OR) TETRAHYDROFURAN (I)

Hazardous Waste Code:U220
Waste Code Description:BENZENE, METHYL- (OR) TOLUENE

Hazardous Waste Code:U223
Waste Code Description:BENZENE, 1,3-DIISOCYANATOMETHYL- (R,T) (OR) TOLUENE DIISOCYANATE (R,T)

Owner/Operator Details

Owner/Operator Ind:Current Owner Street No:11111
Type:Private Street 1:SANTA MONICA BLVD SUITE 600
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:LOS ANGELES
Date Ended Current:State:CA
Phone:[phone] Country:
Source Type:Annual/Biennial Report update with Notification Zip Code:90025

Owner/Operator Ind:Current Owner Street No:91
Type:Private Street 1:LANE 814 TA-HSIN RD
Name:COMPEQ MANUFACTURING - TAIWAN Street 2:HSIN CHUANG VILLAGE
Date Became Current:19900101 City:LU-CHU HSIANG
Date Ended Current:State:
Phone:Country:TW
Source Type:Annual/Biennial Report Zip Code:00000

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:620 NORTH JOHN GLEN RD
Name:COMPEG INTERNATIONAL COMPANY Street 2:
Date Became Current:City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:620 NORTH
Name:COMPRQ MANUFACTURING - TAIWAN Street 2:JOHN GLENN ROAD
Date Became Current:19900101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Annual/Biennial Report update with Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:
Date Ended Current:State:
Phone:Country:
Source Type:Annual/Biennial Report update with Notification Zip Code:

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:620 NORTH
Name:COMPRQ MANUFACTURING - TAIWAN Street 2:JOHN GLENN ROAD
Date Became Current:19900101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Implementer Zip Code:84116

Owner/Operator Ind:Current Operator Street No:620
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Type:Private Street 1:NORTH JOHN GLENN RD
Name:WEBB CHANG Street 2:
Date Became Current:19910101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:595
Type:Private Street 1:SOUTH RIVERWOODS PARKWAY, SUITE
400
Name:BIOMEDICAL INDUSTRIAL HOLDINGS LLC Street 2:
Date Became Current:20180302 City:AXTELL
Date Ended Current:State:UT
Phone:Country:US
Source Type:Notification Zip Code:84621

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:WEBB CHANG Street 2:
Date Became Current:19910101 City:
Date Ended Current:State:
Phone:Country:US
Source Type:Annual/Biennial Report Zip Code:

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:620 NORTH
Name:SAM PIRAYESH Street 2:JOHN GLENN ROAD
Date Became Current:20050501 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:
Source Type:Annual/Biennial Report update with Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:PO BOX 9-22
Name:COMPEQ MANUFACTURING COMPANY Street 2:
Date Became Current:19910101 City:TAOYUAN
Date Ended Current:State:
Phone:Country:TW
Source Type:Annual/Biennial Report Zip Code:

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:SAM PIRAYESH Street 2:
Date Became Current:20050501 City:
Date Ended Current:State:
Phone:Country:US
Source Type:Annual/Biennial Report Zip Code:

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:620 NORTH
Name:SAM PIRAYESH Street 2:JOHN GLENN ROAD
Date Became Current:20050501 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:
Source Type:Implementer Zip Code:84116

Owner/Operator Ind:Current Owner Street No:91
Type:Private Street 1:LANE 814 TA-HSIN RD
Name:COMPEQ MANUFACTURING - TAIWAN Street 2:HSIN CHUANG VILLAGE
Date Became Current:19900101 City:LU-CHU HSIANG
Date Ended Current:State:
Phone:Country:TW
Source Type:Notification Zip Code:00000

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:620 NORTH
Name:SAM PIRAYESH Street 2:JOHN GLENN ROAD
Date Became Current:20050501 City:SALT LAKE CITY
Date Ended Current:State:UT
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Phone:Country:
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:620
Type:Private Street 1:JOHN GLENN ROAD
Name:BIOMERICS LLC Street 2:
Date Became Current:20180302 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:
Name:COMPEQ IN TAIWAN Street 2:
Date Became Current:19910101 City:
Date Ended Current:State:
Phone:Country:US
Source Type:Annual/Biennial Report Zip Code:

Owner/Operator Ind:Current Operator Street No:620 NORTH
Type:Private Street 1:JOHN GLENN RD
Name:SAM PIRAYESH Street 2:
Date Became Current:20050501 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:620 NORTH
Name:COMPRQ MANUFACTURING - TAIWAN Street 2:JOHN GLENN ROAD
Date Became Current:19900101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:11111
Type:Private Street 1:SANTA MONICA BLVD SUITE 600
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:LOS ANGELES
Date Ended Current:State:CA
Phone:[phone] Country:US
Source Type:Notification Zip Code:90025

Owner/Operator Ind:Current Owner Street No:620
Type:Private Street 1:NORTH JOHN GLENN RD
Name:COMPEQ MANUFACTURING CO.Street 2:
Date Became Current:19910101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:11111
Type:Private Street 1:SANTA MONICA BLVD SUITE 600
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:LOS ANGELES
Date Ended Current:State:CA
Phone:[phone] Country:US
Source Type:Notification Zip Code:90025

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:
Date Ended Current:State:
Phone:Country:
Source Type:Notification Zip Code:

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:NO. 91, LANE 814, TA-HSIN RD.
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Name:COMPEQ MANUFACTURING, TAIWAN Street 2:
Date Became Current:19900101 City:SHIN CHUANG VILLAGE,
Date Ended Current:State:
Phone:Country:TW
Source Type:Annual/Biennial Report Zip Code:

Historical Handler Details

Receive Dt:20181010
Generator Code Description:Small Quantity Generator
Handler Name:BIOMERICS LLC

Receive Dt:20180430
Generator Code Description:Small Quantity Generator
Handler Name:BIOMERICS LLC

Receive Dt:20160229
Generator Code Description:Large Quantity Generator
Handler Name:B.H. JOHN GLENN ROAD LLC (FORMERLY COMPEQ INTERNATIONAL)

Receive Dt:20150907
Generator Code Description:Large Quantity Generator
Handler Name:B.H. JOHN GLENN ROAD LLC (FORMERLY COMPEQ INTERNATIONAL)

Receive Dt:20131126
Generator Code Description:Not a Generator, Verified
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20130611
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20100505
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20100329
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20080220
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20060123
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20040225
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20040209
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20020313
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20010521
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:19980803
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

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Receive Dt:19960314
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL CORP.

Receive Dt:19940225
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL CORP.

Receive Dt:19920522
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:19910125
Generator Code Description:Very Small Quantity Generator
Handler Name:COMPEG INTERNATIONAL COMPANY
m-11-873889549-b 2 of2 ENE 0.15 /
810.58
4,228.84 /
4
BIOMERICS LLC
6030 W HAROLD GATTY DR
SALT LAKE CITY UT 84116

p1p-873889549-y1y
EPA Handler ID:UTD988070215
Gen Status Universe:Small Quantity Generator
Contact Name:JASON CUTLER
Contact Address:11111 , SANTA MONICA BLVD SUITE 600 , , LOS ANGELES , CA, 90025 , US
Contact Phone No and Ext:775-857-7252
Contact Email:[e-mail]
Contact Country:US
Land Type:Private
County Name:SALT LAKE
EPA Region:08
Receive Date:20210112
Location Latitude:40.781309
Location Longitude:-112.020967

Violation/Evaluation Summary

Note:VIOLATION or UNDETERMINED: There are VIOLATION or UNDETERMINED details or records associated with
this facility (EPA ID) in the Compliance Monitoring and Enforcement table dated Apr, 2024.

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20191011
Scheduled Compliance Date:
Return to Compliance:Documented
Actual Return to Compl:20191017
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:110
Enforcement Type Description:VERBAL INFORMAL
Enforcement Action Date:20191011
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

11 RCRA TSD
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Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20191011
Scheduled Compliance Date:
Return to Compliance:Documented
Actual Return to Compl:20191011
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:110
Enforcement Type Description:VERBAL INFORMAL
Enforcement Action Date:20191011
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - R315-7-11.3(E)
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20040622
Scheduled Compliance Date:20040722
Return to Compliance:Documented
Actual Return to Compl:20040628
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20040622
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - r315-7-11.3(C)
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20040622
Scheduled Compliance Date:20040722
Return to Compliance:Documented
Actual Return to Compl:20040628
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
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Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20040622
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - r315-5-2
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - r315-13
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
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Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:SR - r315-5-4
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - Pre-transport
Violation Type:262.C
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
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Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - General
Violation Type:264.A
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - General Facility Standards
Violation Type:264.B
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details
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Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - Preparedness and Prevention
Violation Type:264.C
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - Contingency Plan and Emergency Procedures
Violation Type:264.D
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
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Violation Responsible Agency:State

Enforcement Details

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:TSD - Container Use and Management
Violation Type:264.I
Violation Determined Date:19930330
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:19940506
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:210
Enforcement Type Description:INITIAL 3008(A) COMPLIANCE
Enforcement Action Date:19930330
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Enforcement Type:310
Enforcement Type Description:FINAL 3008(A) COMPLIANCE ORDER
Enforcement Action Date:19940404
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:75000
Final Amount:
Paid Amount:

Evaluation Details

Evaluation Start Date:20191011
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20191017
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Evaluation Agency:State

Evaluation Start Date:20191011
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20191011
Evaluation Agency:State

Evaluation Start Date:20131120
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:20090817
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:20040107
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20040628
Evaluation Agency:State

Evaluation Start Date:19980312
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:EPA-Initiated Oversight/Observation/Training Actions

Evaluation Start Date:19980312
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - Pre-transport
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - Preparedness and Prevention
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - General Facility Standards
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - Contingency Plan and Emergency Procedures
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - General
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
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Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:19940506
Evaluation Agency:State

Evaluation Start Date:19930204
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:TSD - Container Use and Management
Return to Compliance Date:19940506
Evaluation Agency:State

Handler Summary

Importer Activity:No
Mixed Waste Generator:No
Transporter Activity:No
Transfer Facility:No
Onsite Burner Exemption:No
Smelting, Melting and Refining:No
Underground Injection Control:No
Commercial TSD:No
Used Oil Transporter:No
Used Oil Transfer Facility:No
Used Oil Processor:No
Used Oil Refiner:No
Used Oil Burner:No
Used Oil Market Burner:No
Used Oil Spec Marketer:No

Hazardous Waste Handler Details

Sequence No:1
Receive Date:19910125
Handler Name:COMPEG INTERNATIONAL COMPANY
Federal Waste Generator Code:3
Generator Code Description:Very Small Quantity Generator
Source Type:Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:1
Receive Date:19920522
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:N

Hazardous Waste Handler Details

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Sequence No:2
Receive Date:19940225
Handler Name:COMPEQ INTERNATIONAL CORP.
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:Y

Hazardous Waste Handler Details

Sequence No:3
Receive Date:19960314
Handler Name:COMPEQ INTERNATIONAL CORP.
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:N

Hazardous Waste Handler Details

Sequence No:4
Receive Date:19980803
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:N

Hazardous Waste Handler Details

Sequence No:5
Receive Date:20010521
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:N

Hazardous Waste Handler Details

Sequence No:6
Receive Date:20020313
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
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Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Code:F007
Waste Code Description:SPENT CYANIDE PLATING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS.

Hazardous Waste Handler Details

Sequence No:7
Receive Date:20040209
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Code:F007
Waste Code Description:SPENT CYANIDE PLATING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS.

Hazardous Waste Code:F008
Waste Code Description:PLATING BATH RESIDUES FROM THE BOTTOM OF PLATING BATHS FROM ELECTROPLATING
OPERATIONS IN WHICH CYANIDES ARE USED IN THE PROCESS.

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20040225
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Notification
TSD Activity:N

Waste Code Details

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Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Code:F007
Waste Code Description:SPENT CYANIDE PLATING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS.

Hazardous Waste Handler Details

Sequence No:8
Receive Date:20060123
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Code:F007
Waste Code Description:SPENT CYANIDE PLATING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS.

Hazardous Waste Code:F008
Waste Code Description:PLATING BATH RESIDUES FROM THE BOTTOM OF PLATING BATHS FROM ELECTROPLATING
OPERATIONS IN WHICH CYANIDES ARE USED IN THE PROCESS.

Hazardous Waste Code:F009
Waste Code Description:SPENT STRIPPING AND CLEANING BATH SOLUTIONS FROM ELECTROPLATING OPERATIONS IN WHICH
CYANIDES ARE USED IN THE PROCESS.

Hazardous Waste Handler Details

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Sequence No:9
Receive Date:20080220
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:3
Receive Date:20100329
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
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METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20100505
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report update with Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:4
Receive Date:20130611
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM
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Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:F006
Waste Code Description:WASTEWATER TREATMENT SLUDGES FROM ELECTROPLATING OPERATIONS, EXCEPT FROM THE
FOLLOWING PROCESSES: (1) SULFURIC ACID ANODIZING OF ALUMINUM; (2) TIN PLATING ON CARBON
STEEL; (3) ZINC PLATING (SEGREGATED BASIS) ON CARBON STEEL; (4) ALUMINUM OR ZINC-ALUMINUM
PLATING ON CARBON STEEL; (5) CLEANING/STRIPPING ASSOCIATED WITH TIN, ZINC, AND ALUMINUM
PLATING ON CARBON STEEL; AND (6) CHEMICAL ETCHING AND MILLING OF ALUMINUM.

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20131126
Handler Name:COMPEQ INTERNATIONAL
Federal Waste Generator Code:N
Generator Code Description:Not a Generator, Verified
Source Type:Implementer
TSD Activity:N

Hazardous Waste Handler Details

Sequence No:5
Receive Date:20150907
Handler Name:B.H. JOHN GLENN ROAD LLC (FORMERLY COMPEQ INTERNATIONAL)
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20160229
Handler Name:B.H. JOHN GLENN ROAD LLC (FORMERLY COMPEQ INTERNATIONAL)
Federal Waste Generator Code:1
Generator Code Description:Large Quantity Generator
Source Type:Annual/Biennial Report update with Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Handler Details

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Sequence No:6
Receive Date:20180430
Handler Name:BIOMERICS LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D022
Waste Code Description:CHLOROFORM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:D038
Waste Code Description:PYRIDINE

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:P024
Waste Code Description:BENZENAMINE, 4-CHLORO- (OR) P-CHLORANILINE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U003
Waste Code Description:ACETONITRILE (I,T)

Hazardous Waste Code:U034
Waste Code Description:ACETALDEHYDE, TRICHLORO- (OR) CHLORAL

Hazardous Waste Code:U044
Waste Code Description:CHLOROFORM (OR) METHANE, TRICHLORO-

Hazardous Waste Code:U056
Waste Code Description:BENZENE, HEXAHYDRO- (I) (OR) CYCLOHEXANE (I)

Hazardous Waste Code:U057
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Waste Code Description:CYCLOHEXANONE (I)

Hazardous Waste Code:U123
Waste Code Description:FORMIC ACID (C,T)

Hazardous Waste Code:U134
Waste Code Description:HYDROFLUORIC ACID (C,T) (OR) HYDROGEN FLUORIDE (C,T)

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U188
Waste Code Description:PHENOL

Hazardous Waste Code:U196
Waste Code Description:PYRIDINE

Hazardous Waste Code:U210
Waste Code Description:ETHENE, TETRACHLORO- (OR) TETRACHLOROETHYLENE

Hazardous Waste Code:U213
Waste Code Description:FURAN, TETRAHYDRO-(I) (OR) TETRAHYDROFURAN (I)

Hazardous Waste Code:U220
Waste Code Description:BENZENE, METHYL- (OR) TOLUENE

Hazardous Waste Code:U223
Waste Code Description:BENZENE, 1,3-DIISOCYANATOMETHYL- (R,T) (OR) TOLUENE DIISOCYANATE (R,T)

Hazardous Waste Handler Details

Sequence No:7
Receive Date:20181010
Handler Name:BIOMERICS LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D022
Waste Code Description:CHLOROFORM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:D038
Waste Code Description:PYRIDINE

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
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BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:P024
Waste Code Description:BENZENAMINE, 4-CHLORO- (OR) P-CHLORANILINE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U003
Waste Code Description:ACETONITRILE (I,T)

Hazardous Waste Code:U034
Waste Code Description:ACETALDEHYDE, TRICHLORO- (OR) CHLORAL

Hazardous Waste Code:U044
Waste Code Description:CHLOROFORM (OR) METHANE, TRICHLORO-

Hazardous Waste Code:U056
Waste Code Description:BENZENE, HEXAHYDRO- (I) (OR) CYCLOHEXANE (I)

Hazardous Waste Code:U057
Waste Code Description:CYCLOHEXANONE (I)

Hazardous Waste Code:U123
Waste Code Description:FORMIC ACID (C,T)

Hazardous Waste Code:U134
Waste Code Description:HYDROFLUORIC ACID (C,T) (OR) HYDROGEN FLUORIDE (C,T)

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U188
Waste Code Description:PHENOL

Hazardous Waste Code:U196
Waste Code Description:PYRIDINE

Hazardous Waste Code:U210
Waste Code Description:ETHENE, TETRACHLORO- (OR) TETRACHLOROETHYLENE

Hazardous Waste Code:U213
Waste Code Description:FURAN, TETRAHYDRO-(I) (OR) TETRAHYDROFURAN (I)

Hazardous Waste Code:U220
Waste Code Description:BENZENE, METHYL- (OR) TOLUENE

Hazardous Waste Code:U223
Waste Code Description:BENZENE, 1,3-DIISOCYANATOMETHYL- (R,T) (OR) TOLUENE DIISOCYANATE (R,T)

Hazardous Waste Handler Details
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Sequence No:8
Receive Date:20210112
Handler Name:BIOMERICS LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification
TSD Activity:N

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D007
Waste Code Description:CHROMIUM

Hazardous Waste Code:D011
Waste Code Description:SILVER

Hazardous Waste Code:D022
Waste Code Description:CHLOROFORM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:D038
Waste Code Description:PYRIDINE

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:P024
Waste Code Description:BENZENAMINE, 4-CHLORO- (OR) P-CHLORANILINE

Hazardous Waste Code:U002
Waste Code Description:2-PROPANONE (I) (OR) ACETONE (I)

Hazardous Waste Code:U003
Waste Code Description:ACETONITRILE (I,T)

Hazardous Waste Code:U034
Waste Code Description:ACETALDEHYDE, TRICHLORO- (OR) CHLORAL

Hazardous Waste Code:U044
Waste Code Description:CHLOROFORM (OR) METHANE, TRICHLORO-

Hazardous Waste Code:U056
Waste Code Description:BENZENE, HEXAHYDRO- (I) (OR) CYCLOHEXANE (I)

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Hazardous Waste Code:U057
Waste Code Description:CYCLOHEXANONE (I)

Hazardous Waste Code:U123
Waste Code Description:FORMIC ACID (C,T)

Hazardous Waste Code:U134
Waste Code Description:HYDROFLUORIC ACID (C,T) (OR) HYDROGEN FLUORIDE (C,T)

Hazardous Waste Code:U154
Waste Code Description:METHANOL (I) (OR) METHYL ALCOHOL (I)

Hazardous Waste Code:U159
Waste Code Description:2-BUTANONE (I,T) (OR) METHYL ETHYL KETONE (MEK) (I,T)

Hazardous Waste Code:U188
Waste Code Description:PHENOL

Hazardous Waste Code:U196
Waste Code Description:PYRIDINE

Hazardous Waste Code:U210
Waste Code Description:ETHENE, TETRACHLORO- (OR) TETRACHLOROETHYLENE

Hazardous Waste Code:U213
Waste Code Description:FURAN, TETRAHYDRO-(I) (OR) TETRAHYDROFURAN (I)

Hazardous Waste Code:U220
Waste Code Description:BENZENE, METHYL- (OR) TOLUENE

Hazardous Waste Code:U223
Waste Code Description:BENZENE, 1,3-DIISOCYANATOMETHYL- (R,T) (OR) TOLUENE DIISOCYANATE (R,T)

Owner/Operator Details

Owner/Operator Ind:Current Owner Street No:620
Type:Private Street 1:NORTH JOHN GLENN RD
Name:COMPEQ MANUFACTURING CO.Street 2:
Date Became Current:19910101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:620 NORTH
Type:Private Street 1:JOHN GLENN RD
Name:SAM PIRAYESH Street 2:
Date Became Current:20050501 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:91
Type:Private Street 1:LANE 814 TA-HSIN RD
Name:COMPEQ MANUFACTURING - TAIWAN Street 2:HSIN CHUANG VILLAGE
Date Became Current:19900101 City:LU-CHU HSIANG
Date Ended Current:State:
Phone:Country:TW
Source Type:Notification Zip Code:00000

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:NO. 91, LANE 814, TA-HSIN RD.
Name:COMPEQ MANUFACTURING, TAIWAN Street 2:
Date Became Current:19900101 City:SHIN CHUANG VILLAGE,
Date Ended Current:State:
Phone:Country:TW
Source Type:Annual/Biennial Report Zip Code:

Owner/Operator Ind:Current Owner Street No:
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Type:Private Street 1:620 NORTH JOHN GLEN RD
Name:COMPEG INTERNATIONAL COMPANY Street 2:
Date Became Current:City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:PO BOX 9-22
Name:COMPEQ MANUFACTURING COMPANY Street 2:
Date Became Current:19910101 City:TAOYUAN
Date Ended Current:State:
Phone:Country:TW
Source Type:Annual/Biennial Report Zip Code:

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:SAM PIRAYESH Street 2:
Date Became Current:20050501 City:
Date Ended Current:State:
Phone:Country:US
Source Type:Annual/Biennial Report Zip Code:

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:
Date Ended Current:State:
Phone:Country:
Source Type:Annual/Biennial Report update with Notification Zip Code:

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:620 NORTH
Name:COMPRQ MANUFACTURING - TAIWAN Street 2:JOHN GLENN ROAD
Date Became Current:19900101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Implementer Zip Code:84116

Owner/Operator Ind:Current Owner Street No:11111
Type:Private Street 1:SANTA MONICA BLVD SUITE 600
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:LOS ANGELES
Date Ended Current:State:CA
Phone:[phone] Country:US
Source Type:Notification Zip Code:90025

Owner/Operator Ind:Current Operator Street No:620
Type:Private Street 1:JOHN GLENN ROAD
Name:BIOMERICS LLC Street 2:
Date Became Current:20180302 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:WEBB CHANG Street 2:
Date Became Current:19910101 City:
Date Ended Current:State:
Phone:Country:US
Source Type:Annual/Biennial Report Zip Code:

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:620 NORTH
Name:SAM PIRAYESH Street 2:JOHN GLENN ROAD
Date Became Current:20050501 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:
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Source Type:Annual/Biennial Report update with Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:11111
Type:Private Street 1:SANTA MONICA BLVD SUITE 600
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:LOS ANGELES
Date Ended Current:State:CA
Phone:[phone] Country:
Source Type:Annual/Biennial Report update with Notification Zip Code:90025

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:620 NORTH
Name:COMPRQ MANUFACTURING - TAIWAN Street 2:JOHN GLENN ROAD
Date Became Current:19900101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:
Date Ended Current:State:
Phone:Country:
Source Type:Notification Zip Code:

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:620 NORTH
Name:COMPRQ MANUFACTURING - TAIWAN Street 2:JOHN GLENN ROAD
Date Became Current:19900101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Annual/Biennial Report update with Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:620
Type:Private Street 1:NORTH JOHN GLENN RD
Name:WEBB CHANG Street 2:
Date Became Current:19910101 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:620 NORTH
Name:SAM PIRAYESH Street 2:JOHN GLENN ROAD
Date Became Current:20050501 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:595
Type:Private Street 1:SOUTH RIVERWOODS PARKWAY, SUITE
400
Name:BIOMEDICAL INDUSTRIAL HOLDINGS LLC Street 2:
Date Became Current:20180302 City:AXTELL
Date Ended Current:State:UT
Phone:Country:US
Source Type:Notification Zip Code:84621

Owner/Operator Ind:Current Owner Street No:91
Type:Private Street 1:LANE 814 TA-HSIN RD
Name:COMPEQ MANUFACTURING - TAIWAN Street 2:HSIN CHUANG VILLAGE
Date Became Current:19900101 City:LU-CHU HSIANG
Date Ended Current:State:
Phone:Country:TW
Source Type:Annual/Biennial Report Zip Code:00000

Owner/Operator Ind:Current Operator Street No:
Type:Private Street 1:620 NORTH
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Name:SAM PIRAYESH Street 2:JOHN GLENN ROAD
Date Became Current:20050501 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:Country:
Source Type:Implementer Zip Code:84116

Owner/Operator Ind:Current Operator Street No:11111
Type:Private Street 1:SANTA MONICA BLVD SUITE 600
Name:B.H. JOHN GLEN ROAD LLC Street 2:
Date Became Current:20150414 City:LOS ANGELES
Date Ended Current:State:CA
Phone:[phone] Country:US
Source Type:Notification Zip Code:90025

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:
Name:COMPEQ IN TAIWAN Street 2:
Date Became Current:19910101 City:
Date Ended Current:State:
Phone:Country:US
Source Type:Annual/Biennial Report Zip Code:

Historical Handler Details

Receive Dt:20181010
Generator Code Description:Small Quantity Generator
Handler Name:BIOMERICS LLC

Receive Dt:20180430
Generator Code Description:Small Quantity Generator
Handler Name:BIOMERICS LLC

Receive Dt:20160229
Generator Code Description:Large Quantity Generator
Handler Name:B.H. JOHN GLENN ROAD LLC (FORMERLY COMPEQ INTERNATIONAL)

Receive Dt:20150907
Generator Code Description:Large Quantity Generator
Handler Name:B.H. JOHN GLENN ROAD LLC (FORMERLY COMPEQ INTERNATIONAL)

Receive Dt:20131126
Generator Code Description:Not a Generator, Verified
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20130611
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20100505
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20100329
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20080220
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20060123
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20040225
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

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Receive Dt:20040209
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20020313
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:20010521
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:19980803
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:19960314
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL CORP.

Receive Dt:19940225
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL CORP.

Receive Dt:19920522
Generator Code Description:Large Quantity Generator
Handler Name:COMPEQ INTERNATIONAL

Receive Dt:19910125
Generator Code Description:Very Small Quantity Generator
Handler Name:COMPEG INTERNATIONAL COMPANY
m-12-826030939-b 1 of1 E 0.24 /
1,269.35
4,227.85 /
3
ALBANY ENGINEERED
COMPOSITES
5995 WEST AMELIA EARHART
DRIVE
SALT LAKE CITY UT 84116

p1p-826030939-y1y
EPA Handler ID:UTR000003236
Gen Status Universe:Small Quantity Generator
Contact Name:SCOTT DAVIS
Contact Address:5995 , WEST AMELIA EARHART DRIVE , , SALT LAKE CITY , UT, 84116 , US
Contact Phone No and Ext:801-505-6941
Contact Email:[e-mail]
Contact Country:US
County Name:SALT LAKE
EPA Region:08
Land Type:Private
Receive Date:20220118
Location Latitude:40.777451
Location Longitude:-112.028632

Violation/Evaluation Summary

Note:VIOLATION or UNDETERMINED: There are VIOLATION or UNDETERMINED details or records associated with
this facility (EPA ID) in the Compliance Monitoring and Enforcement table dated Apr, 2024.

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Listing - General
Violation Type:261.A
Violation Determined Date:20201023
Scheduled Compliance Date:
Return to Compliance:Documented
12 RCRA SQG
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Actual Return to Compl:20210204
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20201216
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20201023
Scheduled Compliance Date:
Return to Compliance:Documented
Actual Return to Compl:20201201
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20201216
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20201023
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:20210204
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20201216
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

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Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20201023
Scheduled Compliance Date:
Return to Compliance:Observed
Actual Return to Compl:20201023
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20201216
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Generators - General
Violation Type:262.A
Violation Determined Date:20201023
Scheduled Compliance Date:
Return to Compliance:Documented
Actual Return to Compl:20210204
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20201216
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Universal Waste - Small Quantity Handlers
Violation Type:273.B
Violation Determined Date:20201023
Scheduled Compliance Date:
Return to Compliance:Documented
Actual Return to Compl:20201208
Violation Responsible Agency:State

Enforcement Details

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Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20201216
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Violation Details

Found Violation:Yes
Citation:
Violation Short Description:Universal Waste - Small Quantity Handlers
Violation Type:273.B
Violation Determined Date:20201023
Scheduled Compliance Date:
Return to Compliance:Documented
Actual Return to Compl:20201201
Violation Responsible Agency:State

Enforcement Details

Enforcement Type:120
Enforcement Type Description:WRITTEN INFORMAL
Enforcement Action Date:20201216
Enf Disposition Status:
Disposition Status Date:
Enforcement Lead Agency:State
Proposed Penalty Amount:
Final Amount:
Paid Amount:

Evaluation Details

Evaluation Start Date:20201023
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Listing - General
Return to Compliance Date:20210204
Evaluation Agency:State

Evaluation Start Date:20201023
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Universal Waste - Small Quantity Handlers
Return to Compliance Date:20201208
Evaluation Agency:State

Evaluation Start Date:20201023
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20201201
Evaluation Agency:State

Evaluation Start Date:20201023
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Universal Waste - Small Quantity Handlers
Return to Compliance Date:20201201
Evaluation Agency:State

Evaluation Start Date:20201023
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20201023
Evaluation Agency:State
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Evaluation Start Date:20201023
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:Generators - General
Return to Compliance Date:20210204
Evaluation Agency:State

Evaluation Start Date:20160914
Evaluation Type Description:COMPLIANCE EVALUATION INSPECTION
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:20150428
Evaluation Type Description:COMPLIANCE ASSISTANCE VISIT
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Evaluation Start Date:20070831
Evaluation Type Description:COMPLIANCE ASSISTANCE VISIT
Violation Short Description:
Return to Compliance Date:
Evaluation Agency:State

Handler Summary

Importer Activity:No
Mixed Waste Generator:No
Transporter Activity:No
Transfer Facility:No
Onsite Burner Exemption:No
Furnace Exemption:No
Underground Injection Activity:No
Commercial TSD:No
Used Oil Transporter:No
Used Oil Transfer Facility:No
Used Oil Processor:No
Used Oil Refiner:No
Used Oil Burner:No
Used Oil Market Burner:No
Used Oil Spec Marketer:No

Hazardous Waste Handler Details

Sequence No:1
Receive Date:19970828
Handler Name:AMERICAN PAD & PAPER
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D006
Waste Code Description:CADMIUM

Hazardous Waste Code:D008
Waste Code Description:LEAD

Hazardous Waste Code:D018
Waste Code Description:BENZENE
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Hazardous Waste Code:D039
Waste Code Description:TETRACHLOROETHYLENE

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Handler Details

Sequence No:1
Receive Date:20070904
Handler Name:AMERICAN PAD & PAPER
Federal Waste Generator Code:N
Generator Code Description:Not a Generator, Verified
Source Type:Implementer

Hazardous Waste Handler Details

Sequence No:2
Receive Date:20150324
Handler Name:EDO CORPORATION FIBER SCIENCE
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:F001
Waste Code Description:THE FOLLOWING SPENT HALOGENATED SOLVENTS USED IN DEGREASING: TETRACHLOROETHYLENE,
TRICHLORETHYLENE, METHYLENE CHLORIDE, 1,1,1-TRICHLOROETHANE, CARBON TETRACHLORIDE
AND CHLORINATED FLUOROCARBONS; ALL SPENT SOLVENT MIXTURES/BLENDS USED IN DEGREASING
CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF
THE ABOVE HALOGENATED SOLVENTS OR THOSE SOLVENTS LISTED IN F002, F004, AND F005; AND
STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
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AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Handler Details

Sequence No:3
Receive Date:20160412
Handler Name:ALBANY AEROSTRUCTURES COMPOSITES LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:F001
Waste Code Description:THE FOLLOWING SPENT HALOGENATED SOLVENTS USED IN DEGREASING: TETRACHLOROETHYLENE,
TRICHLORETHYLENE, METHYLENE CHLORIDE, 1,1,1-TRICHLOROETHANE, CARBON TETRACHLORIDE
AND CHLORINATED FLUOROCARBONS; ALL SPENT SOLVENT MIXTURES/BLENDS USED IN DEGREASING
CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF
THE ABOVE HALOGENATED SOLVENTS OR THOSE SOLVENTS LISTED IN F002, F004, AND F005; AND
STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Handler Details

Sequence No:4
Receive Date:20171122
Handler Name:ALBANY AEROSTRUCTURES COMPOSITES LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details
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Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE

Hazardous Waste Code:F001
Waste Code Description:THE FOLLOWING SPENT HALOGENATED SOLVENTS USED IN DEGREASING: TETRACHLOROETHYLENE,
TRICHLORETHYLENE, METHYLENE CHLORIDE, 1,1,1-TRICHLOROETHANE, CARBON TETRACHLORIDE
AND CHLORINATED FLUOROCARBONS; ALL SPENT SOLVENT MIXTURES/BLENDS USED IN DEGREASING
CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF
THE ABOVE HALOGENATED SOLVENTS OR THOSE SOLVENTS LISTED IN F002, F004, AND F005; AND
STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Handler Details

Sequence No:5
Receive Date:20180712
Handler Name:ALBANY AEROSTRUCTURES COMPOSITES LLC
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:D003
Waste Code Description:REACTIVE WASTE

Hazardous Waste Code:D005
Waste Code Description:BARIUM

Hazardous Waste Code:D035
Waste Code Description:METHYL ETHYL KETONE
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Hazardous Waste Code:F001
Waste Code Description:THE FOLLOWING SPENT HALOGENATED SOLVENTS USED IN DEGREASING: TETRACHLOROETHYLENE,
TRICHLORETHYLENE, METHYLENE CHLORIDE, 1,1,1-TRICHLOROETHANE, CARBON TETRACHLORIDE
AND CHLORINATED FLUOROCARBONS; ALL SPENT SOLVENT MIXTURES/BLENDS USED IN DEGREASING
CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF
THE ABOVE HALOGENATED SOLVENTS OR THOSE SOLVENTS LISTED IN F002, F004, AND F005; AND
STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Hazardous Waste Handler Details

Sequence No:6
Receive Date:20220118
Handler Name:ALBANY ENGINEERED COMPOSITES
Federal Waste Generator Code:2
Generator Code Description:Small Quantity Generator
Source Type:Notification

Waste Code Details

Hazardous Waste Code:D001
Waste Code Description:IGNITABLE WASTE

Hazardous Waste Code:D002
Waste Code Description:CORROSIVE WASTE

Hazardous Waste Code:F003
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL ACETATE, ETHYL
BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL ALCOHOL, CYCLOHEXANONE, AND
METHANOL; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE
SPENT NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING,
BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS, AND A TOTAL OF TEN
PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004,
AND F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT
SOLVENT MIXTURES.

Hazardous Waste Code:F005
Waste Code Description:THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL KETONE, CARBON
DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT
SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY
VOLUME) OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS
LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT
SOLVENTS AND SPENT SOLVENT MIXTURES.

Owner/Operator Details

Owner/Operator Ind:Current Owner Street No:1301
Type:Private Street 1:5TH AVENUE
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Name:WASHINGTON CAPITAL MANAGEMENT Street 2:
Date Became Current:20050901 City:SEATTLE
Date Ended Current:State:WA
Phone:[phone] Country:US
Source Type:Notification Zip Code:98105

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:127 SOUTH 500 EAST STE 310
Name:BOYER COMPANY Street 2:
Date Became Current:City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:
Source Type:Notification Zip Code:84102

Owner/Operator Ind:Current Operator Street No:5995
Type:Private Street 1:WEST AMELIA EARHART DRIVE
Name:EDO CORPORATION FIBER SCIENCE Street 2:
Date Became Current:20130601 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Operator Street No:5995
Type:Private Street 1:WEST AMELIA EARHART DRIVE
Name:ALBANY AEROSTRUCTURES COMPOSITES
LLC
Street 2:
Date Became Current:20130601 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:5995
Type:Private Street 1:WEST AMELIA EARHART DRIVE
Name:ALBANY AEROSTRUCTURES COMPOSITES
LLC
Street 2:
Date Became Current:20130601 City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84116

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:127 SOUTH 500 EAST STE 310
Name:BOYER COMPANY Street 2:
Date Became Current:City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:
Source Type:Implementer Zip Code:84102

Owner/Operator Ind:Current Owner Street No:
Type:Private Street 1:127 SOUTH 500 EAST STE 310
Name:BOYER COMPANY Street 2:
Date Became Current:City:SALT LAKE CITY
Date Ended Current:State:UT
Phone:[phone] Country:US
Source Type:Notification Zip Code:84102

Historical Handler Details

Receive Dt:20180712
Generator Code Description:Small Quantity Generator
Handler Name:ALBANY AEROSTRUCTURES COMPOSITES LLC

Receive Dt:20171122
Generator Code Description:Small Quantity Generator
Handler Name:ALBANY AEROSTRUCTURES COMPOSITES LLC

Receive Dt:20160412
Generator Code Description:Small Quantity Generator
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Handler Name:ALBANY AEROSTRUCTURES COMPOSITES LLC

Receive Dt:20150324
Generator Code Description:Small Quantity Generator
Handler Name:EDO CORPORATION FIBER SCIENCE

Receive Dt:20070904
Generator Code Description:Not a Generator, Verified
Handler Name:AMERICAN PAD & PAPER

Receive Dt:19970828
Generator Code Description:Small Quantity Generator
Handler Name:AMERICAN PAD & PAPER
m-13-924033371-b 1 of1 E 0.25 /
1,336.43
4,225.09 /
0
ALBANY ENGINEERED
COMPOSITES

SALT LAKE CITY UT

p1p-924033371-y1y
Status:Active Fac Fips Code:49035
Fac Indian Cntry Flg:No Compliance Status:No Violation Identified
Fac Derived Huc:16020204 EPA Programs:CWA; RCRA
Fac Derived Wbd:160202040404 Federal Facility:No
Fac Derived Cd113:02 Federal Agency:-
Fac Derived Cb2010:490351139061080 Fac Snc Flg:No
Fac Informal Count:1 AIR Flag:No
Last Informal Action:12/16/2020 NPDES Flag:Yes
Formal Action Count:0 SDWIS Flag:No
Last Formal Action:-RCRAFlag:Yes
Fac Total Penalties:0 TRI Flag:No
Fac Penalty Count:-GHG Flag:No
Date Last Penalty:-TRI IDs:-
Last Penalty Amt:-TRI Releases Trnsfrs:-
Fac Qtrs With Nc:0 TRI on Site Releases:-
Programs With Snc:0 TRI off Site Trnsfrs:-
Fac Percent Minority:40 TRI Reporter:-
Fac Pop Den:0.55 Fac Imp Water Flg:Yes
Count:1 Fac Major Flag:-
Fac County:SALT LAKE Fac Active Flag:Yes
State Other :Fac Inspection Count:1
Region:08 Date Last Inspection:10/23/2020
Latitude:40.77879 Days Last Inspection:1429
Longitude:-112.03351
Fac Derived Tribes:-
AIR IDs:-
CAA Permit Types:-
CAA NAICS:-
CAA SICS:-
NPDES IDs:UTG071887 UTNX00582 UTR263153
CWA Permit Types:Non-M
CWA NAICS:327993 313210
CWA SICS:3296 3728 2221
RCRA IDs:UTR000003236
RCRA Permit Types:SQG
RCRA NAICS:336413 336419
SDWA IDs:-
SDWA System Types:-
SDWA Compliance Status:-
SDWA Snc Flag:No
Fac Collection Meth:ADDRESS MATCHING-HOUSE NUMBER
EJSCREEN Flag Us:Yes
EJSCREEN Report:https://ejscreen.epa.gov/mapper/mobile/EJSCREEN_mobile.aspx?geometry=%7B%22x%22:-112.03351,%22y%
22:40.77879,%22spatialReference%22:%7B%22wkid%22:4326%7D%
7D&unit=9035&areatype=&areaid=&basemap=streets&distance=1
ECHO Facility Report:https://echo.epa.gov/detailed-facility-report?fid=110005209899

Industry:Textiles and Leather
13 PFAS IND
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m-14-923152099-b 1 of1 ENE 0.32 /
1,683.28
4,227.23 /
2
COLDSET PRINTING PRESSES &
STAMPING

SALT LAKE CITY UT

p1p-923152099-y1y
Status:Unknown Fac Fips Code:49035
Fac Indian Cntry Flg:No Compliance Status:-
Fac Derived Huc:16020204 EPA Programs:-
Fac Derived Wbd:160202040404 Federal Facility:No
Fac Derived Cd113:02 Federal Agency:-
Fac Derived Cb2010:490351139061080 Fac Snc Flg:No
Fac Informal Count:0 AIR Flag:No
Last Informal Action:-NPDES Flag:No
Formal Action Count:0 SDWIS Flag:No
Last Formal Action:-RCRAFlag:No
Fac Total Penalties:0 TRI Flag:No
Fac Penalty Count:-GHG Flag:No
Date Last Penalty:-TRI IDs:-
Last Penalty Amt:-TRI Releases Trnsfrs:-
Fac Qtrs With Nc:-TRI on Site Releases:-
Programs With Snc:0 TRI off Site Trnsfrs:-
Fac Percent Minority:42.857 TRI Reporter:-
Fac Pop Den:0.5 Fac Imp Water Flg:-
Count:1 Fac Major Flag:-
Fac County:SALT LAKE Fac Active Flag:-
State Other :Fac Inspection Count:0
Region:08 Date Last Inspection:-
Latitude:40.77693 Days Last Inspection:-
Longitude:-112.04193
Fac Derived Tribes:-
AIR IDs:-
CAA Permit Types:-
CAA NAICS:-
CAA SICS:-
NPDES IDs:-
CWA Permit Types:-
CWA NAICS:-
CWA SICS:-
RCRA IDs:-
RCRA Permit Types:-
RCRA NAICS:-
SDWA IDs:-
SDWA System Types:-
SDWA Compliance Status:-
SDWA Snc Flag:No
Fac Collection Meth:UNKNOWN
EJSCREEN Flag Us:Yes
EJSCREEN Report:https://ejscreen.epa.gov/mapper/mobile/EJSCREEN_mobile.aspx?geometry=%7B%22x%22:-112.04193,%22y%
22:40.77693,%22spatialReference%22:%7B%22wkid%22:4326%7D%
7D&unit=9035&areatype=&areaid=&basemap=streets&distance=1
ECHO Facility Report:https://echo.epa.gov/detailed-facility-report?fid=110071718038

Industry:Printing
m-15-805418078-b 1 of4 SW 0.49 /
2,562.68
4,221.94 /
-3
KENNECOTT (NORTH ZONE)
12000 WEST 2100 SOUTH
MAGNA UT 84044

p1p-805418078-y1y
Site ID:0800636 RNPL Status Code:P
Site EPA ID:UTD070926811 NPL Status:Proposed for NPL
Site Street Address 2:RFED Facility Code:N
Site County Name:SALT LAKE RFED Facility Desc:Not a Federal Facility
Site FIPS Code:49035 USGS Hydro Unit No.:16020204
Region Code:08 Site Cong. Dist. Code:01,02,03
Site SMSA No.:7160 ROT Desc:Other
Site Prim. Latitude:+40.750000 FR NPL Update No.:16
Site Prim. Longitude:-112.125000 RFRA Code:P
14
15
PFAS IND
CERCLIS
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Lat Long Source:EPA HQ
RNON NPL Status Desc:

CERCLIS Site Contact Name(s)

Person ID:13000441.00
First Name:Peggy
Last Name:Linn
Phone No.:3033126622
Email:[e-mail]

CERCLIS Site Contact Name(s)

Person ID:13002908.00
First Name:Kerri
Last Name:Fiedler
Phone No.:3033126493
Email:[e-mail]

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:
RAT Code:DS Act Complete Date:8/19/1986 00:00:00
RAT Short Name:DISCVRY AGT Order No.:10
RAT Name:DISCOVERY SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:SH Lead:
SPA Code:13
RAT Def:The process by which a potential hazardous waste site is brought to the attention of the EPA. The process can
occur through the use of several mechanisms such as a phone call or referral by another government agency.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:Fed Enforce
Act Code ID:001 Act Start Date:9/13/1993 00:00:00
RAT Code:RV Act Complete Date:1/24/1995 00:00:00
RAT Short Name:RMVL AGT Order No.:70
RAT Name:REMOVAL SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:V SH Lead:
SPA Code:08
RAT Def:Response action that requires expeditious attention to reduce imminent and substantial dangers to human health,
welfare, or the environment or an emergency response required within hours or days to address acute situations
involving actual or potential threat to human health, the environment, or real or personal property due to the release
of a hazardous substance. Characterization of a removal action as removal, not immediate removal or planned
removal, started at the beginning of FY 1987. This code now takes the place of immediate removal (IR) and
planned removal (PR).
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:9/14/1993 00:00:00
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RAT Code:CO Act Complete Date:6/1/1995 00:00:00
RAT Short Name:RI/FS AGT Order No.:430
RAT Name:COMBINED REMEDIAL
INVESTIGATION/FEASIBILITY STUDY
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:The process of data collection and analyses of the site problem, identification of preliminary remedial alternatives,
and recommendation of a cost-effective remedy. There can be multiple Remedial Investigation/Feasibility Studies
(RI/FS) conducted at a site.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:9/13/1993 00:00:00
RAT Code:ED Act Complete Date:12/30/1999 00:00:00
RAT Short Name:R/H ASMT AGT Order No.:540
RAT Name:RISK/HEALTH ASSESSMENT SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:09
RAT Def:Assessment of the baseline risks posed by the site to human health.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:08 RALT Short Name:PRP Rsp Fed
Act Code ID:001 Act Start Date:11/13/2003 00:00:00
RAT Code:BE Act Complete Date:
RAT Short Name:PRP RD AGT Order No.:800
RAT Name:POTENTIALLY RESPONSIBLE PARTY
REMEDIAL DESIGN
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:Provides for oversight of Potentially Responsible Party (PRP) response action for Remedial Design (RD), including
all activities for monitoring and supervising the performance of the responsible parties to determine whether such
performance is consistent with the requirements of the administrative orders on consent, unilateral administrative
orders, consent decrees, judicial decrees, information agreements, and compliance schedules.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:08 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:3/29/2013 00:00:00
RAT Code:FE Act Complete Date:
RAT Short Name:5 YEAR AGT Order No.:1010
RAT Name:FIVE-YEAR REVIEW SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:A SH Lead:
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SPA Code:09
RAT Def:A review that is conducted at a minimum of every five years to determine if the implementation and performance of
a remedy is protective or will be protective of human health and the environment.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:003 Act Start Date:12/2/2008 00:00:00
RAT Code:TA Act Complete Date:12/2/2008 00:00:00
RAT Short Name:TECH A AGT Order No.:500
RAT Name:TECHNICAL ASSISTANCE SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:09
RAT Def:Participation in the conduct of fund-financed Remedial Investigation/Feasibility Study (RI/FS).
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:01 RALT Short Name:Fed Enforce
Act Code ID:001 Act Start Date:9/19/1991 00:00:00
RAT Code:MA Act Complete Date:6/1/1995 00:00:00
RAT Short Name:ST COOP AGT Order No.:300
RAT Name:STATE SUPPORT AGENCY COOPERATIVE
AGREEMENT
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:09
RAT Def:Federal renumeration of state administrative costs of participation in site-specific remedial planning or
implementation activities.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:08 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:5/30/1996 00:00:00
RAT Code:EE Act Complete Date:6/14/1996 00:00:00
RAT Short Name:EE/CA AGT Order No.:50
RAT Name:ENGINEERING EVALUATION/COST
ANALYSIS
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:Study to identify the objectives of a removal action and to analyze the cost effectiveness and implementability of
the various alternatives that may be used to satisfy these objectives.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:08 RALT Short Name:PRP Rsp Fed
Act Code ID:002 Act Start Date:10/2/1996 00:00:00
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RAT Code:BB Act Complete Date:3/1/2003 00:00:00
RAT Short Name:PRP RV AGT Order No.:90
RAT Name:POTENTIALLY RESPONSIBLE PARTY
REMOVAL
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:V SH Lead:
SPA Code:08
RAT Def:Provides for oversight of Potentially Responsible Party (PRP) response action for removals, including all activities
for monitoring and supervising the performance of PRPs to determine whether such performance is consistent with
the requirements of the administrative orders on consent, unilateral administrative orders, consent decrees, judicial
decrees, information agreements, and compliance schedules.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:09 RALT Short Name:EPA Fund
Act Code ID:002 Act Start Date:9/30/1993 00:00:00
RAT Code:RV Act Complete Date:1/24/1995 00:00:00
RAT Short Name:RMVL AGT Order No.:70
RAT Name:REMOVAL SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:V SH Lead:
SPA Code:08
RAT Def:Response action that requires expeditious attention to reduce imminent and substantial dangers to human health,
welfare, or the environment or an emergency response required within hours or days to address acute situations
involving actual or potential threat to human health, the environment, or real or personal property due to the release
of a hazardous substance. Characterization of a removal action as removal, not immediate removal or planned
removal, started at the beginning of FY 1987. This code now takes the place of immediate removal (IR) and
planned removal (PR).
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:
Act Code ID:Act Start Date:
RAT Code:Act Complete Date:
RAT Short Name:AGT Order No.:0
RAT Name:SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:SH Seq:
RAT Level:SH Start Date:
RAT DEF OU:SH Complete Date:
RFBS Code:SH Lead:
SPA Code:
RAT Def:
Site Desc:The Kennecott North and South Zones were proposed for the National Priorities List (NPL) in January, 1994. Final
listing was deferred in September 1995 in accordance with the terms of a three-party Memorandum of
Understanding (MOU) signed by officials at
Site Alias:KENECOTT MAGNA SOILS,23RD SOUTH ST,MAGNA ,UT,;KENNECOTT (NORTH ZONE),,MAGNA,UT,84044;
KENNECOTT (NORTH ZONE),12000 W 2100 S.,MAGNA,UT,84044;KENNECOTT - WASTEWATER
TREATMENT PLANT,,,UT,;KENNECOTT COPPER,C-7 DITCH,MAGNA,UT,84044;KENNECOTT TAILINGS,23RD
STREE

CERCLIS Assess History

OU ID:00 RALT Short Name:St PRP Only
Act Code ID:001 Act Start Date:9/30/1995 00:00:00
RAT Code:JF Act Complete Date:4/7/1997 00:00:00
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RAT Short Name:ECO RISK AGT Order No.:542
RAT Name:ECOLOGICAL RISK ASSESSMENT SH OU:
RAT Hist. Only Flag:T SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:09
RAT Def:Assessment of the baseline risks posed by the site to ecological receptors.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:1/18/1994 00:00:00
RAT Code:RS Act Complete Date:11/2/1994 00:00:00
RAT Short Name:RV ASSESS AGT Order No.:30
RAT Name:REMOVAL ASSESSMENT SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:V SH Lead:
SPA Code:08
RAT Def:Collecting site characteristics to determine whether or not a removal must be performed.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:003 Act Start Date:6/20/1994 00:00:00
RAT Code:MA Act Complete Date:
RAT Short Name:ST COOP AGT Order No.:300
RAT Name:STATE SUPPORT AGENCY COOPERATIVE
AGREEMENT
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:09
RAT Def:Federal renumeration of state administrative costs of participation in site-specific remedial planning or
implementation activities.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:State (Fund)
Act Code ID:001 Act Start Date:
RAT Code:PA Act Complete Date:10/16/1987 00:00:00
RAT Short Name:PA AGT Order No.:130
RAT Name:PRELIMINARY ASSESSMENT SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:Collection of diverse existing information about the source and nature of the site hazard. It is EPA policy to
complete the preliminary assessment within one year of site discovery.
Site Desc:
Site Alias:

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OU ID:08 RALT Short Name:Fed Enforce
Act Code ID:001 Act Start Date:
RAT Code:RO Act Complete Date:9/26/2002 00:00:00
RAT Short Name:ROD AGT Order No.:610
RAT Name:RECORD OF DECISION SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:SH Complete Date:
RFBS Code:SH Lead:
SPA Code:13
RAT Def:The final Record of Decision (ROD) is signed by the appropriate agency indicating that the agency has chosen the
remedy for site remediation. ROD signature is signified by the complete date.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:002 Act Start Date:
RAT Code:HR Act Complete Date:9/30/1993 00:00:00
RAT Short Name:HAZRANK AGT Order No.:190
RAT Name:HAZARD RANKING SYSTEM PACKAGE SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:A numeric estimate of the relative severity of a hazardous substance release or potential release based on: (1) the
relative potential of substances to cause hazardous situations; (2) the likelihood and rate at which the substances
may affect human and environmental receptors; and (3) the severity and magnitude of potential effects. The score
is computed using the hazard ranking system (HRS).
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:PRP Rsp Fed
Act Code ID:002 Act Start Date:8/16/1994 00:00:00
RAT Code:BD Act Complete Date:1/25/1995 00:00:00
RAT Short Name:PRP RI/FS AGT Order No.:470
RAT Name:POTENTIALLY RESPONSIBLE PARTY
REMEDIAL INVESTIGATION/FEASIBILITY
STUDY
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:Provides for oversight of Potentially Responsible Party (PRP) response action for Remedial Investigation/Feasibility
Study (RI/FS), including all activities for monitoring and supervising the performance of the responsible parties to
determine whether such performance is consistent with the requirements of the administrative orders on consent,
unilateral administrative orders, consent decrees, judicial decrees, information agreements, and compliance
schedules.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:State (Fund)
Act Code ID:001 Act Start Date:
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RAT Code:SI Act Complete Date:12/13/1990 00:00:00
RAT Short Name:SI AGT Order No.:160
RAT Name:SITE INSPECTION SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:The process of collecting site data and samples to characterize the severity of the hazard for the hazard ranking
score and/or enforcement support.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:
RAT Code:HR Act Complete Date:11/2/1990 00:00:00
RAT Short Name:HAZRANK AGT Order No.:190
RAT Name:HAZARD RANKING SYSTEM PACKAGE SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:A numeric estimate of the relative severity of a hazardous substance release or potential release based on: (1) the
relative potential of substances to cause hazardous situations; (2) the likelihood and rate at which the substances
may affect human and environmental receptors; and (3) the severity and magnitude of potential effects. The score
is computed using the hazard ranking system (HRS).
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:
RAT Code:NP Act Complete Date:1/18/1994 00:00:00
RAT Short Name:PROPOSED AGT Order No.:200
RAT Name:PROPOSAL TO NATIONAL PRIORITIES LIST SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:Site proposed for inclusion on the National Priority List based on the Hazard Ranking System (HRS) score for the
site.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:08 RALT Short Name:PRP Rsp Fed
Act Code ID:003 Act Start Date:6/16/1997 00:00:00
RAT Code:BD Act Complete Date:9/26/2002 00:00:00
RAT Short Name:PRP RI/FS AGT Order No.:470
RAT Name:POTENTIALLY RESPONSIBLE PARTY
REMEDIAL INVESTIGATION/FEASIBILITY
STUDY
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:SH Complete Date:
RFBS Code:P SH Lead:
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SPA Code:13
RAT Def:Provides for oversight of Potentially Responsible Party (PRP) response action for Remedial Investigation/Feasibility
Study (RI/FS), including all activities for monitoring and supervising the performance of the responsible parties to
determine whether such performance is consistent with the requirements of the administrative orders on consent,
unilateral administrative orders, consent decrees, judicial decrees, information agreements, and compliance
schedules.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:Fed Enforce
Act Code ID:004 Act Start Date:8/16/1994 00:00:00
RAT Code:AR Act Complete Date:10/1/2002 00:00:00
RAT Short Name:ADMM REC AGT Order No.:580
RAT Name:ADMINISTRATIVE RECORDS SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:SARA specifies that administrative records be compiled at Superfund sites where remedial or removal responses
are planned, or are occurring, or where EPA is issuing a unilateral order or initiating litigation to track enforcement
case budget funds used for any RP lead activity.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:01 RALT Short Name:Fed Enforce
Act Code ID:002 Act Start Date:9/14/1993 00:00:00
RAT Code:AR Act Complete Date:9/26/2002 00:00:00
RAT Short Name:ADMM REC AGT Order No.:580
RAT Name:ADMINISTRATIVE RECORDS SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:SARA specifies that administrative records be compiled at Superfund sites where remedial or removal responses
are planned, or are occurring, or where EPA is issuing a unilateral order or initiating litigation to track enforcement
case budget funds used for any RP lead activity.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:00 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:9/26/1999 00:00:00
RAT Code:TA Act Complete Date:4/10/2000 00:00:00
RAT Short Name:TECH A AGT Order No.:500
RAT Name:TECHNICAL ASSISTANCE SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:09
RAT Def:Participation in the conduct of fund-financed Remedial Investigation/Feasibility Study (RI/FS).
Site Desc:
Site Alias:

CERCLIS Assess History
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OU ID:01 RALT Short Name:EPA Fund
Act Code ID:001 Act Start Date:9/22/1993 00:00:00
RAT Code:ES Act Complete Date:9/30/1993 00:00:00
RAT Short Name:ESI AGT Order No.:170
RAT Name:EXPANDED SITE INSPECTION SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:13
RAT Def:Functions performed to collect additional data, beyond that required for Hazard Ranking System scoring, in order to
expedite the Remedial Investigation/Feasibility Study (RI/FS) project planning phase for National Priority List (NPL)
sites. The present site inspection focus on pathways and receptors has been expanded to include site and source
characterization. The information facilitates the development of RI/FS workplan and sampling and analysis plan.
Site Desc:
Site Alias:

CERCLIS Assess History

OU ID:08 RALT Short Name:EPA Fund
Act Code ID:002 Act Start Date:2/8/1994 00:00:00
RAT Code:MA Act Complete Date:
RAT Short Name:ST COOP AGT Order No.:300
RAT Name:STATE SUPPORT AGENCY COOPERATIVE
AGREEMENT
SH OU:
RAT Hist. Only Flag:SH Code:
RAT NSI Indicator:B SH Seq:
RAT Level:1 SH Start Date:
RAT DEF OU:00 SH Complete Date:
RFBS Code:P SH Lead:
SPA Code:09
RAT Def:Federal renumeration of state administrative costs of participation in site-specific remedial planning or
implementation activities.
Site Desc:
Site Alias:
m-15-828841683-b 2 of4 SW 0.49 /
2,562.68
4,221.94 /
-3
KENNECOTT (NORTH ZONE)
12000 WEST 2100 SOUTH
MAGNA UT 84044

p1p-828841683-y1y
EPA ID:UTD070926811 Latitude:+40.734036
Pgm Sys ID:UTD070926811 Longitude:-112.141040
Latitude83:40.734035999999996 Latitude83(CalOES):40.734036
Longitude83:-112.14104 Longitude83(CalOES):-112.14104
Primary Nm (MAP):KENNECOTT (NORTH ZONE)
Loc Addr (MAP):12000 WEST 2100 SOUTH
Site Name:KENNECOTT (NORTH ZONE)
Street Address:12000 WEST 2100 SOUTH
Street Address 2:
City:MAGNA
County:SALT LAKE
PGM SYS ID(CalOES):UTD070926811
Name(CalOES):KENNECOTT (NORTH ZONE)
Loc Addr(CalOES):12000 WEST 2100 SOUTH
City(CalOES):MAGNA
County(CalOES):SALT LAKE
Postal(CalOES):84044
County Name:SALT LAKE
City Name:MAGNA
Postal Code:84044
State:UT
Zip:84044
Data Source:EPA Superfund Data and Reports Active Site Inventory (List 8R Active); EPA FRS Interests Map - SEMS; CalOES
EPA RCRA TSDF Map - SEMS

15 SEMS
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Site Level Information

Site ID:0800636 Superfund Alt Agmt:No
NPL:Proposed for NPL FIPS Code:49035
Federal Facility:No Cong District:02,01,03
FF Docket:No Region:08
Non NPL Status:Remedial Activities Under EPA Enforcement

Action Information

Operable Units:00 Start Actual:3/27/2023 04:00:00 AM
Action Code:FE Finish Actual:
Action Name:5 YEAR Qual:
SEQ:3 Curr Action Lead:St Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:08 Start Actual:2/8/1994 05:00:00 AM
Action Code:MA Finish Actual:6/30/2015 04:00:00 AM
Action Name:ST COOP Qual:
SEQ:2 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:23 Start Actual:3/31/2016 05:00:00 AM
Action Code:NK Finish Actual:
Action Name:PRP FS Qual:
SEQ:1 Curr Action Lead:EPA Ovrsght
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:01 Start Actual:9/14/1993 04:00:00 AM
Action Code:AR Finish Actual:9/26/2002 04:00:00 AM
Action Name:ADMIN REC Qual:E
SEQ:2 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:11/2/1990 05:00:00 AM
Action Code:HR Finish Actual:11/2/1990 05:00:00 AM
Action Name:HAZRANK Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:01 Start Actual:8/16/1994 04:00:00 AM
Action Code:BD Finish Actual:1/25/1995 05:00:00 AM
Action Name:PRP RI/FS Qual:
SEQ:2 Curr Action Lead:EPA Ovrsght
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:08 Start Actual:6/16/1997 04:00:00 AM
Action Code:BD Finish Actual:9/26/2002 04:00:00 AM
Action Name:PRP RI/FS Qual:
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SEQ:3 Curr Action Lead:EPA Ovrsght
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:8/16/1994 04:00:00 AM
Action Code:AR Finish Actual:10/1/2002 04:00:00 AM
Action Name:ADMIN REC Qual:E
SEQ:4 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:08 Start Actual:11/13/2003 05:00:00 AM
Action Code:BE Finish Actual:
Action Name:PRP RD Qual:
SEQ:1 Curr Action Lead:EPA Ovrsght
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:6/20/1994 04:00:00 AM
Action Code:MA Finish Actual:
Action Name:ST COOP Qual:
SEQ:3 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:9/26/1999 04:00:00 AM
Action Code:TA Finish Actual:4/10/2000 04:00:00 AM
Action Name:TECH ASSIST Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:1/18/1994 05:00:00 AM
Action Code:RS Finish Actual:11/2/1994 05:00:00 AM
Action Name:RV ASSESS Qual:C
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:12/2/2008 05:00:00 AM
Action Code:TA Finish Actual:12/2/2008 05:00:00 AM
Action Name:TECH ASSIST Qual:
SEQ:3 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:10/16/1987 04:00:00 AM
Action Code:PA Finish Actual:10/16/1987 04:00:00 AM
Action Name:PA Qual:H
SEQ:1 Curr Action Lead:St Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

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Operable Units:01 Start Actual:4/1/2000 05:00:00 AM
Action Code:OM Finish Actual:
Action Name:OM Qual:
SEQ:1 Curr Action Lead:EPA Ovrsght
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:9/22/1993 04:00:00 AM
Action Code:ES Finish Actual:9/30/1993 04:00:00 AM
Action Name:ESI Qual:G
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:8/19/1986 04:00:00 AM
Action Code:DS Finish Actual:8/19/1986 04:00:00 AM
Action Name:DISCVRY Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:08 Start Actual:9/26/2002 04:00:00 AM
Action Code:RO Finish Actual:9/26/2002 04:00:00 AM
Action Name:ROD Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:01 Start Actual:9/30/1995 04:00:00 AM
Action Code:JF Finish Actual:4/7/1997 04:00:00 AM
Action Name:ECO RISK Qual:
SEQ:1 Curr Action Lead:St Ovrsght
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:5/30/2020 04:00:00 AM
Action Code:TA Finish Actual:
Action Name:TECH ASSIST Qual:
SEQ:6 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:6/23/2014 05:00:00 AM
Action Code:TA Finish Actual:10/3/2019 05:00:00 AM
Action Name:TECH ASSIST Qual:
SEQ:4 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:08 Start Actual:10/2/1996 04:00:00 AM
Action Code:BB Finish Actual:3/1/2003 05:00:00 AM
Action Name:PRP RV Qual:
SEQ:2 Curr Action Lead:EPA Ovrsght
Region:08
FF Docket:No
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NPL:P
Federal Facility:No

Operable Units:00 Start Actual:12/13/1990 05:00:00 AM
Action Code:SI Finish Actual:12/13/1990 05:00:00 AM
Action Name:SI Qual:C
SEQ:1 Curr Action Lead:St Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:01 Start Actual:9/14/1993 04:00:00 AM
Action Code:CO Finish Actual:6/1/1995 04:00:00 AM
Action Name:RI/FS Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:12/3/2014 05:00:00 AM
Action Code:TA Finish Actual:6/30/2015 04:00:00 AM
Action Name:TECH ASSIST Qual:
SEQ:5 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:01 Start Actual:9/13/1993 04:00:00 AM
Action Code:ED Finish Actual:12/30/1999 05:00:00 AM
Action Name:R/H ASMT Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:9/13/1993 04:00:00 AM
Action Code:RV Finish Actual:1/24/1995 05:00:00 AM
Action Name:RMVL Qual:C
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:3/29/2013 04:00:00 AM
Action Code:FE Finish Actual:6/17/2014 05:00:00 AM
Action Name:5 YEAR Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:9/30/1993 04:00:00 AM
Action Code:HR Finish Actual:9/30/1993 04:00:00 AM
Action Name:HAZRANK Qual:
SEQ:2 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:08 Start Actual:5/30/1996 04:00:00 AM
Action Code:EE Finish Actual:6/14/1996 04:00:00 AM
Action Name:EE/CA Qual:
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SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:09 Start Actual:9/30/1993 04:00:00 AM
Action Code:RV Finish Actual:1/24/1995 05:00:00 AM
Action Name:RMVL Qual:S
SEQ:2 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:4/19/2017 05:00:00 AM
Action Code:FE Finish Actual:8/19/2019 05:00:00 AM
Action Name:5 YEAR Qual:
SEQ:2 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:01 Start Actual:9/19/1991 04:00:00 AM
Action Code:MA Finish Actual:6/1/1995 04:00:00 AM
Action Name:ST COOP Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

Operable Units:00 Start Actual:1/18/1994 05:00:00 AM
Action Code:NP Finish Actual:1/18/1994 05:00:00 AM
Action Name:PROPOSED Qual:
SEQ:1 Curr Action Lead:EPA Perf
Region:08
FF Docket:No
NPL:P
Federal Facility:No

GIS Information

Registry ID:110009506347 Pgm Sys Acrnm:SEMS
Active Status:PROPOSED FOR NPL Accuracy Value:
Key Field:SEMSUTD070926811 HUC8 Code:16020204
Interest Type:SUPERFUND NPL HUC 12:
Fed Agency Name:Public Ind:Yes
Fed Facility Code:Pgm Report:no data yet
Federal Land Ind:Point X:-112.14103999999998
EPA Region Code:08 Point Y:40.73403600000006
Fips Code:49035
Collect Mth Desc:
Ref Point Desc:
Fac Url:https://ofmpub.epa.gov/frs_public2/fii_query_detail.disp_program_facility?p_registry_id=110009506347
Program Url:http://www.epa.gov/superfund/action/law/cercla.htm
Pgm Report Url:no data yet

CalOES EPA RCRA TSDF - SEMS

Registry ID:110009506347 HUC 12:
Interest Type:SUPERFUND NPL Collect Mth Desc:
Active Status:PROPOSED FOR NPL Accuracy Value:
Pgm Sys Acrnm:SEMS Ref Point Desc:
Federal Agency Nm:EPA Region Code:08
Federal Land Ind:Key Field:SEMSUTD070926811
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Fed Facility Cd:Create Dt:10/26/2021
Public Ind:Yes Update Dt:11/24/2021
FIPS Code:49035 Last Reported Dt:
HUC8 Code:16020204
Pgm Report Url:no data yet
Program URL:http://www.epa.gov/superfund/action/law/cercla.htm
Fac Url:https://ofmpub.epa.gov/frs_public2/fii_query_detail.disp_program_facility?p_registry_id=110009506347
m-15-859641034-b 3 of4 SW 0.49 /
2,562.68
4,221.94 /
-3
KENNECOTT (NORTH ZONE)
12000 WEST 2100 SOUTH
MAGNA UT 8404

p1p-859641034-y1y
EPA ID:UTD070926811
Site ID:0800636
NPL Status:Proposed
Non NPL Status:Remedial Activities Under EPA Enforcement
Region:08
EPA ID (Web):UTD070926811
Site Name (Web):KENNECOTT (NORTH ZONE)
State (Web):UT
Region (Web):08
Data Source(s):SEMS Superfund Public User Database; Searchable Superfund Decision Documents Database (Web)

Superfund Decision Documents Details

Doc ID:2004003
Title:RECORD OF DECISION: KENNECOTT NORTH ZONE SITE, KENNECOTT SOUTH ZONE SITE; OPERABLE
UNITS 8, 9, 13-15, 18, 19, 22-24
Date:09/26/2002
Pub No:
Description:
PDF Link:https://semspub.epa.gov/src/document/08/2004003

Completed RODs, ROD Amendments and ESDs (FOIA 2) Details

Seq ID:1
Action Name:Explanation Of Significant Differences (ESD)
Operable Unit Name:KENNECOTT (WWTP)
Actual Comp Date:08/11/2017

Seq ID:1
Action Name:Record of Decision (ROD)
Operable Unit Name:KENNECOTT (WWTP)
Actual Comp Date:09/26/2002
m-15-901572580-b 4 of4 SW 0.49 /
2,562.68
4,221.94 /
-3
KENNECOTT NORTH ZONE
12000 W 2100 South
MAGNA UT 84044

p1p-901572580-y1y
CIMID:490000015470 County:SALT LAKE
DERR ID:UTD070926811 Contact Phone No:8015364282
Northing:4508044.62552 St Key:145
Easting:405846.20972 Project Manager:Douglas Bacon
Site Description:CERCLA National Priorities List
Map Label:CERCLA National Priorities List - UTD070926811
Project Description:<b><u>Original: </u></b><br>The Kennecott-North Zone is comprised of areas on or near Kennecott Corporation
property near the south shore of the Great Salt Lake. At its Magna operations, Kennecott processes ore taken from
its pit about 15 miles south and produces copper and other metals. Ore tailings are retained in a pond near the
process facilities. Kennecott purchased the facilities in 1959. The company has continued to reduce contaminant
releases over the years by improving the facility smelter and process equipment, process methods, and waste
handling procedures.<br><br>

15
15
SUPERFUND
ROD
NPL UT
150 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Map Key Number of
Records
Direction Distance
(mi/ft)
Elev/Diff
(ft)
Site DB
m-16-820756204-b 1 of1 E 0.49 /
2,606.50
4,227.51 /
2
SLC FIRE DEPT. STA. #9
5822 W AMELIA EARHART DR
(350 N )
SALT LAKE CITY UT 84116

p1p-820756204-y1y
DERR ID:4001798 Site Desc (Map):PST
Fac ID (Map):4530 Factsheet (Map):No
Tank (Map):Yes Reg AST (Map):No
Release (Map):Yes Health Dist (Map):4
Open Release (Map):No Northing (Map):4514630.0
Open Reg AST (Map):No Easting (Map):413213.0
Open Tank (Map):Yes Forklift Hash:f6cf581328ac76ce
Facility Desc(Map):Local Government
Location Name (DERR):SLC FIRE DEPT. STA. #9
Location Address (DERR):5822 W AMELIA EARHART DR (350 N )
Location City (DERR):SALT LAKE CITY
State (DERR):UT
Zip (DERR):84116
Loc County (DERR):SALT LAKE
Owner Name (DERR):SALT LAKE PUBLIC UTILITIES
Owner Address (DERR):1530 S WEST TEMPLE
Owner City (DERR):SALT LAKE CITY
Owner State (DERR):UT
Owner Zip (DERR):84115
Location Name (Map):SLC FIRE DEPT. STA. #9
Location Address (Map):5822 W AMELIA EARHART DR (350 N )
Location City (Map):SALT LAKE CITY
Location Zip (Map):84116
Location County (Map):SALT LAKE
Owner Name (Map):SALT LAKE PUBLIC UTILITIES
Owner Address (Map):1530 S WEST TEMPLE
Owner City (Map):SALT LAKE CITY
Owner State (Map):UT
Owner Zip (Map):84115
Owner County (Map):SALT LAKE
Map Label (Map):4001798 - SLC FIRE DEPT. STA. #9
UTM Desc (Map):Orthoquad (DOQ) 1 meter Image
Hyperlink (Map):
Facility ID (Open Data):
Location Name (Open Data):
Location Street (Open Data):
Location City (Open Data):
Location State (Open Data):
Location Zip (Open Data):
Location County (Open Data):
Data Source:Leaking Underground Storage Tank (LUST) Sites in Utah (DERR); Utah Environmental Interactive Map (Map)

Historical DEQ Environmental Interactive Map LUST Details (as of June 2024)

LUST Key:4203 Project Manager:Michael Pecorelli
DERR ID:LNW Soil Treated:0
Date Close:4/11/2003 H2O Treated:0
Closure Type:< RCL/MCL PST Eligible:Eligible (100)
NFA Form:Tier 1 Worksheet PST % Eligible:100
Notification:4/9/2002 PST Deductible:10000
IC:Bluestakes:No
GW Flow Directn 1:N Envcov:No
GW Flow Directn 2:Residualco:No
Groundwater Depth:2.3 ft
Map Label:LNW - SLC FIRE DEPT. STA. #9

LUST Information

Leak ID:LNW
Project Manager:Michael Pecorelli
Notif Date:4/9/2002
Date Closed:4/11/2003
16 LUST
151 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Map Key Number of
Records
Direction Distance
(mi/ft)
Elev/Diff
(ft)
Site DB
152 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Unplottable Summary
Total: 2 Unplottable sites
DB Company Name/Site
Name
Address City Zip ERIS ID
uu-SPILLS-822566518-aa Salt Lake City Public
Utilities
I-80 SALT LAKE CITY
UT
822566518
DERR ID | Date Discovered: 6636 | 8/31/2007 5:27

uu-SPILLS-840015226-aa FedEx I-80 Westbound - Please Select UT 840015226
DERR ID | Date Discovered: 8728 | 12/24/2012 0:0 Title: Phone:

SPILLS
SPILLS
Unplottable Summary
153 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Unplottable Report
Site:Salt Lake City Public Utilities
I-80 SALT LAKE CITY UT uu-SPILLS-822566518-bb
DERR ID: 6636 Rpt Pty Title:Mngt
Site Desc: Rpt Pty Ph:[phone]
Date Discovered: 8/31/2007 5:27 Resp Pty Ph:8014836864
Date Time Rptd: 8/31/2007 5:37 Inc Hwy:I-80
TBL Start Date: 8/31/2007 Inc Mile Maker:
TBL End Date: Inc Indian Land:
TBL Imp Media: Surface Water, Surface Water County:SALT LAKE
TBL Chemical: Fluorosilicic Acid (CAS #16961-83-4 or #7732-
18-5)
Northing:
Rpt Taken By: Mike Zucker Easting:
Rpt Pty Name: Florence Reynolds
Title Event Name:Salt Lake City Public Utilities
ID:
Point Y:
Point X:
Incident Summary:
Caller is making notificaton of a release estimated over 1,000 gallons of Fluorosilicic Acid. Cause is unknown at this time but originated from a ruptured
bulk storage tank. Material overflowed secondary containment, and entered the by-pass, which eventually flows to the creek. The by-pass is dry at this
time. PRP has called Hazmat and for a backhoe to shore up/berm the zone of impact. UPDATE 06:15 - Fire Dept. is on-scene, media is also on-scene.
From NRC report (08:34) - Capacity of the tank is 10,000 gallons. Amount of release is reported as 2,000 gallons. Contractor has been secured for
cleanup. UPDATE 09:09 SLVHD reports that Incident Command team is considering at this time to flush the spill. UPDATE 14:30 A fitting on the tank
popped/failed allowing it to drain. TW Company is on site doing cleaning up. The crew is pumping out some ponded flows to contain the majority of the
material. Utilities will re-open the reservoir once a neutral pH has been re-established. Water will then be released to flush the system.
Site:FedEx
I-80 Westbound - Please Select UT uu-SPILLS-840015226-bb
DERR ID: 8728 Rpt Pty Title:
Site Desc: Rpt Pty Ph:
Date Discovered: 12/24/2012 0:0 Title: Phone:Resp Pty Ph:
Date Time Rptd: 12/24/2012 14:38 Inc Hwy:I-180
TBL Start Date: 12/24/2012 Inc Mile Maker:
TBL End Date: Inc Indian Land:
TBL Imp Media: Soils, Soils County:SALT LAKE
TBL Chemical: diesel fuel Northing:
Rpt Taken By: Taylor, Neil Easting:
Rpt Pty Name: Marlin Zechman
Title Event Name:FedEx
ID:
Point Y:
Point X:
Incident Summary:
12/24/12 at 14:38 Marlin Zechman with XL Group reported for Fed Ex Ground Transport that a truck had crashed on I-80 westbound at mile post 110 at
about 7200 West. An undetermined amount of diesel fuel was released. There are no known surface water impacts. Environmental Remediation has
been dispatched for spill remediation. XL Group reports the remedial contractor is on site, 20-25 gallons of diesel fuel was spilled in the median. No
surface water impact.
SPILLS
SPILLS
Unplottable Report
154 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Appendix: Database Descriptions
Environmental Risk Information Services (ERIS) can search the following databases. The extent of historical information varies with
each database and current information is determined by what is publicly available to ERIS at the time of update. ERIS updates
databases as set out in ASTM Standard E1527-13 and E1527-21, Section 8.1.8 Sources of Standard Source Information:
"Government information from nongovernmental sources may be considered current if the source updates the information at least every
90 days, or, for information that is updated less frequently than quarterly by the government agency, within 90 days of the date the
government agency makes the information available to the public."
Standard Environmental Record Sources
Federal
National Priority List:rr-NPL-bb
The U.S. Environmental Protection Agency (EPA)'s National Priorities List (NPL) includes the most serious uncontrolled or abandoned hazardous waste
sites identified for possible long-term remedial action under the Superfund program, based primarily on the score a site receives from EPA's Hazard
Ranking System. A site must be on the NPL to receive money from the Superfund Trust Fund for remedial action. This data includes NPL sites
represented as polygons, where available, that can be sourced from the EPA NPL Superfund Site Boundaries dataset, refreshed by the Shared
Enterprise Geodata and Services (SEGS). These site boundaries represent the footprint of a whole site, the sum of all the Operable Units (OUs) and the
current understanding of the full extent of contamination; for Federal Facility sites, the total site polygon may be the Facility boundary. As site
investigation and remediation progress, OUs may be added, modified or refined. Data provided by external parties is not independently verified by EPA.
This boundary data is made available to the public strictly for informational purposes. Where there is no polygon boundary data available for a given site,
the site is represented as a point.
Government Publication Date: Sep 25, 2024
National Priority List - Proposed:rr-PROPOSED NPL-bb
Sites proposed by the U.S. Environmental Protection Agency (EPA), the state agency, or concerned citizens for addition to the National Priorities List
(NPL) due to contamination by hazardous waste and identified by the EPA as a candidate for cleanup because it poses a risk to human health and/or
the environment. Sites represented as polygons, where available, can be sourced from the EPA NPL Superfund Site Boundaries dataset, refreshed by
the Shared Enterprise Geodata and Services (SEGS). These site boundaries represent the footprint of a whole site, the sum of all the Operable Units
(OUs) and the current understanding of the full extent of contamination; for Federal Facility sites, the total site polygon may be the Facility boundary.
Data provided by external parties is not independently verified by EPA. This boundary data is made available to the public strictly for informational
purposes. Where there is no polygon boundary data available for a given site, the site is represented as a point.
Government Publication Date: Sep 25, 2024
Deleted NPL:rr-DELETED NPL-bb
Sites deleted from the U.S. Environmental Protection Agency (EPA)'s National Priorities List (NPL). The National Oil and Hazardous Substances
Pollution Contingency Plan (NCP) establishes the criteria that the EPA uses to delete sites from the NPL. In accordance with 40 CFR 300.425.(e), sites
may be deleted from the NPL where no further response is appropriate. Sites represented as polygons, where available, can be sourced from the EPA
NPL Superfund Site Boundaries dataset, refreshed by the Shared Enterprise Geodata and Services (SEGS). These site boundaries represent the
footprint of a whole site, the sum of all the Operable Units (OUs) and the current understanding of the full extent of contamination; for Federal Facility
sites, the total site polygon may be the Facility boundary. Data provided by external parties is not independently verified by EPA. This boundary data is
made available to the public strictly for informational purposes. Where there is no polygon boundary data available for a given site, the site is
represented as a point.
Government Publication Date: Sep 25, 2024
NPL
PROPOSED NPL
DELETED NPL
Appendix: Database Descriptions
155 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
SEMS List 8R Active Site Inventory:rr-SEMS-bb
The U.S. Environmental Protection Agency's (EPA) Superfund Program has deployed the Superfund Enterprise Management System (SEMS), which
integrates multiple legacy systems into a comprehensive tracking and reporting tool. This inventory contains active sites evaluated by the Superfund
program that are either proposed to be or are on the National Priorities List (NPL) as well as sites that are in the screening and assessment phase for
possible inclusion on the NPL. The Active Site Inventory Report displays site and location information at active SEMS sites. An active site is one at
which site assessment, removal, remedial, enforcement, cost recovery, or oversight activities are being planned or conducted. This data includes SEMS
sites from the List 8R Active file as well as applicable sites from the EPA's Facility Registry Service map tool.
Government Publication Date: Jul 24, 2024
Inventory of Open Dumps, June 1985:rr-ODI-bb
The Resource Conservation and Recovery Act (RCRA) provides for publication of an inventory of open dumps. The Act defines "open dumps" as
facilities which do not comply with EPA's "Criteria for Classification of Solid Waste Disposal Facilities and Practices" (40 CFR 257).
Government Publication Date: Jun 1985
SEMS List 8R Archive Sites:rr-SEMS ARCHIVE-bb
The U.S. Environmental Protection Agency's (EPA) Superfund Enterprise Management System (SEMS) Archived Site Inventory displays site and
location information at sites archived from SEMS. An archived site is one at which EPA has determined that assessment has been completed and no
further remedial action is planned under the Superfund program at this time. This data includes sites from the List 8R Archived site file.
Government Publication Date: Jul 24, 2024
Comprehensive Environmental Response, Compensation and Liability Information System -
CERCLIS:
rr-CERCLIS-bb
Superfund is a program administered by the United States Environmental Protection Agency (EPA) to locate, investigate, and clean up the worst
hazardous waste sites throughout the United States. CERCLIS is a database of potential and confirmed hazardous waste sites at which the EPA
Superfund program has some involvement. It contains sites that are either proposed to be or are on the National Priorities List (NPL) as well as sites
that are in the screening and assessment phase for possible inclusion on the NPL. The EPA administers the Superfund program in cooperation with
individual states and tribal governments; this database is made available by the EPA.
Government Publication Date: Oct 25, 2013
EPA Report on the Status of Open Dumps on Indian Lands:rr-IODI-bb
Public Law 103-399, The Indian Lands Open Dump Cleanup Act of 1994, enacted October 22, 1994, identified congressional concerns that solid waste
open dump sites located on American Indian or Alaska Native (AI/AN) lands threaten the health and safety of residents of those lands and contiguous
areas. The purpose of the Act is to identify the location of open dumps on Indian lands, assess the relative health and environment hazards posed by
those sites, and provide financial and technical assistance to Indian tribal governments to close such dumps in compliance with Federal standards and
regulations or standards promulgated by Indian Tribal governments or Alaska Native entities.
Government Publication Date: Dec 31, 1998
CERCLIS - No Further Remedial Action Planned:rr-CERCLIS NFRAP-bb
An archived site is one at which EPA has determined that assessment has been completed and no further remedial action is planned under the
Superfund program at this time. The Archive designation means 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 this site on the National Priorities List (NPL). This 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 a potential NPL
site.
Government Publication Date: Oct 25, 2013
CERCLIS Liens:rr-CERCLIS LIENS-bb
A Federal Superfund lien exists at any property where EPA has incurred Superfund costs to address contamination ("Superfund site") and has provided
notice of liability to the property owner. A Federal CERCLA ("Superfund") lien can exist by operation of law at any site or property at which EPA has
spent Superfund monies. This database is made available by the United States Environmental Protection Agency (EPA). This database was provided by
the United States Environmental Protection Agency (EPA). Refer to SEMS LIEN as the current data source for Superfund Liens.
Government Publication Date: Jan 30, 2014
RCRA CORRACTS-Corrective Action:rr-RCRA CORRACTS-bb
RCRA Info is the U.S. Environmental Protection Agency's (EPA) comprehensive information system, providing access to data supporting the Resource
Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. At these sites, the Corrective
Action Program ensures that cleanups occur. EPA and state regulators work with facilities and communities to design remedies based on the
contamination, geology, and anticipated use unique to each site.
Government Publication Date: Apr 8, 2024
SEMS
ODI
SEMS ARCHIVE
CERCLIS
IODI
CERCLIS NFRAP
CERCLIS LIENS
RCRA CORRACTS
156 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
RCRA non-CORRACTS TSD Facilities:rr-RCRA TSD-bb
RCRA Info is the U.S. Environmental Protection Agency's (EPA) comprehensive information system, providing access to data supporting the Resource
Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. This database includes Non-
Corrective Action sites that have indicated engagement in the treatment, storage, or disposal of hazardous waste which requires a RCRA hazardous
waste permit.
Government Publication Date: Apr 8, 2024
RCRA Generator List:rr-RCRA LQG-bb
RCRA Info is the U.S. Environmental Protection Agency's (EPA) comprehensive information system, providing access to data supporting the Resource
Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. RCRA Info replaces the data
recording and reporting abilities of the Resource Conservation and Recovery Information System (RCRIS) and the Biennial Reporting System (BRS). A
hazardous waste generator is any person or site whose processes and actions create hazardous waste (see 40 CFR 260.10). Large Quantity
Generators (LQGs) generate 1,000 kilograms per month or more of hazardous waste or more than one kilogram per month of acutely hazardous waste.
Government Publication Date: Apr 8, 2024
RCRA Small Quantity Generators List:rr-RCRA SQG-bb
RCRA Info is the U.S. Environmental Protection Agency's (EPA) comprehensive information system, providing access to data supporting the Resource
Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. RCRA Info replaces the data
recording and reporting abilities of the Resource Conservation and Recovery Information System (RCRIS) and the Biennial Reporting System (BRS). A
hazardous waste generator is any person or site whose processes and actions create hazardous waste (see 40 CFR 260.10). Small Quantity
Generators (SQGs) generate more than 100 kilograms, but less than 1,000 kilograms, of hazardous waste per month.
Government Publication Date: Apr 8, 2024
RCRA Very Small Quantity Generators List:rr-RCRA VSQG-bb
RCRA Info is the U.S. Environmental Protection Agency's (EPA) comprehensive information system, providing access to data supporting the Resource
Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. A hazardous waste generator is
any person or site whose processes and actions create hazardous waste (see 40 CFR 260.10). Very Small Quantity Generators (VSQG) generate 100
kilograms or less per month of hazardous waste, or one kilogram or less per month of acutely hazardous waste. Additionally, VSQG may not
accumulate more than 1,000 kilograms of hazardous waste at any time.
Government Publication Date: Apr 8, 2024
RCRA Non-Generators:rr-RCRA NON GEN-bb
RCRA Info is the U.S. Environmental Protection Agency's (EPA) comprehensive information system, providing access to data supporting the Resource
Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. RCRA Info replaces the data
recording and reporting abilities of the Resource Conservation and Recovery Information System (RCRIS) and the Biennial Reporting System (BRS). A
hazardous waste generator is any person or site whose processes and actions create hazardous waste (see 40 CFR 260.10). Non-Generators do not
presently generate hazardous waste.
Government Publication Date: Apr 8, 2024
RCRA Sites with Controls:rr-RCRA CONTROLS-bb
List of Resource Conservation and Recovery Act (RCRA) facilities with institutional controls in place. RCRA gives the U.S. Environmental Protection
Agency (EPA) the authority to control hazardous waste from the "cradle-to-grave." This includes the generation, transportation, treatment, storage, and
disposal of hazardous waste. RCRA also set forth a framework for the management of non-hazardous solid wastes. The 1986 amendments to RCRA
enabled EPA to address environmental problems that could result from underground tanks storing petroleum and other hazardous substances.
Government Publication Date: Apr 8, 2024
Federal Engineering Controls-ECs:rr-FED ENG-bb
List of Engineering controls (ECs) made availabe by the United States Environmental Protection Agency (EPA). ECs encompass a variety of engineered
and constructed physical barriers (e.g., soil capping, sub-surface venting systems, mitigation barriers, fences) to contain and/or prevent exposure to
contamination on a property. The EC listing includes remedy component data from Superfund decision documents for applicable sites on the final or
deleted on the National Priorities List (NPL); and sites with a Superfund Alternative Approach (SAA) Agreement in place. The only sites included that are
not on the NPL; proposed for NPL; or removed from proposed NPL, are those with an SAA Agreement in place.
Government Publication Date: Sep 25, 2024
RCRA TSD
RCRA LQG
RCRA SQG
RCRA VSQG
RCRA NON GEN
RCRA CONTROLS
FED ENG
157 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Federal Institutional Controls- ICs:rr-FED INST-bb
List of Institutional controls (ICs) made available by the United States Environmental Protection Agency (EPA). ICs are non-engineered instruments,
such as administrative and legal controls, that help minimize the potential for human exposure to contamination and/or protect the integrity of the
remedy. Although it is EPA's expectation that treatment or engineering controls will be used to address principal threat wastes and that groundwater will
be returned to its beneficial use whenever practicable, ICs play an important role in site remedies because they reduce exposure to contamination by
limiting land or resource use and guide human behavior at a site. The IC listing includes remedy component data from Superfund decision documents
for applicable sites on the final or deleted on the National Priorities List (NPL); and sites with a Superfund Alternative Approach (SAA) Agreement in
place. The only sites included that are not on the NPL; proposed for NPL; or removed from proposed NPL, are those with an SAA Agreement in place.
Government Publication Date: Sep 25, 2024
Land Use Control Information System:rr-LUCIS-bb
The LUCIS database is maintained by the U.S. Department of the Navy and contains information for former Base Realignment and Closure (BRAC)
properties across the United States.
Government Publication Date: Sep 1, 2006
Institutional Control Boundaries at NPL sites:rr-NPL IC-bb
These boundaries of Institutional Control areas at sites on the U.S. Environmental Protection Agency's (EPA) National Priorities List (NPL), or as
Proposed or Deleted, are sourced from the EPA NPL Superfund Site Boundaries dataset, refreshed by the Shared Enterprise Geodata and Services
(SEGS). The EPA's NPL includes the most serious uncontrolled or abandoned hazardous waste sites identified for possible long-term remedial action
under the Superfund program. Institutional controls are non-engineered instruments such as administrative and legal controls that help minimize the
potential for human exposure to contamination and/or protect the integrity of the remedy. Data provided by external parties is not independently verified
by EPA. This boundary data is made available to the public strictly for informational purposes.
Government Publication Date: Sep 25, 2024
Emergency Response Notification System:rr-ERNS 1982 TO 1986-bb
Database of oil and hazardous substances spill reports controlled by the National Response Center. The primary function of the National Response
Center is to serve as the sole national point of contact for reporting oil, chemical, radiological, biological, and etiological discharges into the environment
anywhere in the United States and its territories.
Government Publication Date: 1982-1986
Emergency Response Notification System:rr-ERNS 1987 TO 1989-bb
Database of oil and hazardous substances spill reports controlled by the National Response Center. The primary function of the National Response
Center is to serve as the sole national point of contact for reporting oil, chemical, radiological, biological, and etiological discharges into the environment
anywhere in the United States and its territories.
Government Publication Date: 1987-1989
Emergency Response Notification System:rr-ERNS-bb
Database of oil and hazardous substances spill reports made available by the United States Coast Guard National Response Center (NRC). The NRC
fields initial reports for pollution and railroad incidents and forwards that information to appropriate federal/state agencies for response. These data
contain initial incident data that has not been validated or investigated by a federal/state response agency.
Government Publication Date: Jul 14, 2024
The Assessment, Cleanup and Redevelopment Exchange System (ACRES) Brownfield Database:rr-FED BROWNFIELDS-bb
Brownfields are real property, the expansion, redevelopment, or reuse of which may be complicated by the presence or potential presence of a
hazardous substance, pollutant, or contaminant. Cleaning up and reinvesting in these properties protects the environment, reduces blight, and takes
development pressures off greenspaces and working lands. This data is provided by the United States Environmental Protection Agency (EPA) and
includes Brownfield sites from the Cleanups in My Community (CIMC) web application.
Government Publication Date: Feb 7, 2024
FEMA Underground Storage Tank Listing:rr-FEMA UST-bb
The Federal Emergency Management Agency (FEMA) of the Department of Homeland Security maintains a list of FEMA owned underground storage
tanks.
Government Publication Date: Dec 31, 2017
FED INST
LUCIS
NPL IC
ERNS 1982 TO 1986
ERNS 1987 TO 1989
ERNS
FED BROWNFIELDS
FEMA UST
158 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Facility Response Plan:rr-FRP-bb
This listing contains facilities that have submitted Facility Response Plans (FRPs) to the U.S. Environmental Protection Agency (EPA). Facilities that
could reasonably be expected to cause "substantial harm" to the environment by discharging oil into or on navigable waters are required to prepare and
submit FRPs. Harm is determined based on total oil storage capacity, secondary containment and age of tanks, oil transfer activities, history of
discharges, proximity to a public drinking water intake or sensitive environments. This listing includes FRP facilities from an applicable EPA FOIA file
and Homeland Infrastructure Foundation-Level Data (HIFLD) data file.
Government Publication Date: Jan 9, 2024
Delisted Facility Response Plans:rr-DELISTED FRP-bb
Facilities that once appeared in - and have since been removed from - the list of facilities that have submitted Facility Response Plans (FRP) to EPA.
Facilities that could reasonably be expected to cause "substantial harm" to the environment by discharging oil into or on navigable waters are required to
prepare and submit Facility Response Plans (FRPs). Harm is determined based on total oil storage capacity, secondary containment and age of tanks,
oil transfer activities, history of discharges, proximity to a public drinking water intake or sensitive environments.
Government Publication Date: Jan 9, 2024
Historical Gas Stations:rr-HIST GAS STATIONS-bb
This historic directory of service stations is provided by the Cities Service Company. The directory includes Cities Service filling stations that were
located throughout the United States in 1930.
Government Publication Date: Jul 1, 1930
Petroleum Refineries:rr-REFN-bb
This list of petroleum refineries is sourced from the U.S. Energy Information Administration (EIA), Refinery Capacity Report. The listing includes
operating and idle petroleum refineries (including new refineries under construction) and refineries shut down during the previous year. The geographic
area the report covers is the 50 States, the District of Columbia, Puerto Rico, the U.S. Virgin Islands, Guam, and other U.S. possessions. Per the EIA,
the facility location data represents the approximate location based on research of publicly available information from sources such as Federal agencies,
company websites, and satellite images on public websites.
Government Publication Date: Jun 6, 2024
Petroleum Product and Crude Oil Rail Terminals:rr-BULK TERMINAL-bb
A list of petroleum product and crude oil rail terminals from the U.S. Energy Information Administration (EIA), as well as petroleum terminals sourced
from the Federal Communications Commission Data hosted by the Homeland Infrastructure Foundation-Level Database. Data includes operable bulk
petroleum product terminals with a total bulk shell storage capacity of 50,000 barrels or more, and/or the ability to receive volumes from tanker, barge, or
pipeline; also rail terminals handling the loading and unloading of crude oil with activity between 2017 and 2018. EIA petroleum product terminal data
comes from the EIA-815 Bulk Terminal and Blender Report, which includes working, shell in operation, and shell idle for several major product
groupings.
Government Publication Date: Jun 6, 2024
LIEN on Property:rr-SEMS LIEN-bb
The U.S. Environmental Protection Agency's (EPA) Superfund Enterprise Management System (SEMS) provides Lien details on applicable properties,
such as the Superfund lien on property activity, the lien property information, and the parties associated with the lien.
Government Publication Date: Jul 24, 2024
Superfund Decision Documents:rr-SUPERFUND ROD-bb
This database contains a list of decision documents for Superfund sites. Decision documents serve to provide the reasoning for the choice of (or)
changes to a Superfund Site cleanup plan. The decision documents include completed Records of Decision (ROD), ROD Amendments, Explanations of
Significant Differences (ESD) for active and archived sites stored in the Superfund Enterprise Management System (SEMS), along with other associated
memos and files. This information is maintained and made available by the U.S. Environmental Protection Agency.
Government Publication Date: Jul 24, 2024
Formerly Utilized Sites Remedial Action Program:rr-DOE FUSRAP-bb
The U.S. Department of Energy (DOE) established the Formerly Utilized Sites Remedial Action Program (FUSRAP) in 1974 to remediate sites where
radioactive contamination remained from the Manhattan Project and early U.S. Atomic Energy Commission (AEC) operations. The DOE Office of
Legacy Management (LM) established long-term surveillance and maintenance (LTS&M) requirements for remediated FUSRAP sites. DOE evaluates
the final site conditions of a remediated site on the basis of risk for different future uses. DOE then confirms that LTS&M requirements will maintain
protectiveness.
Government Publication Date: Mar 4, 2017
FRP
DELISTED FRP
HIST GAS STATIONS
REFN
BULK TERMINAL
SEMS LIEN
SUPERFUND ROD
DOE FUSRAP
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State
Utah National Priorities List:rr-NPL UT-bb
The National Priorities List (NPL) is maintained by the Utah Department of Environmental Quality's Division of Environmental Response and
Remediation (DERR). Before a cleanup of a hazardous waste site can take place under Superfund, it must be included on the National Priority List. The
NPL is a published list of hazardous waste sites that are eligible for extensive, long-term cleanup action under the Superfund program. When no
responsible party can be found, listing on the NPL allows EPA and the State to access the Superfund Trust fund to pay for site cleanup. The DERR
assumes no responsibility or liability for the accuracy of the location of these properties.
Government Publication Date: May 6, 2024
Potential Contaminated Sites:rr-CONTAM POTENTIAL-bb
This database of Comprehensive Environmental Response, Compensation, and Liability System sites is maintained by the Utah Department of
Environmental Quality's Division of Environmental Response and Remediation (DERR). The CERCLA Branch of the DERR performs site investigations
of potentially contaminated sites within the State of Utah to determine whether or not they pose a threat to human health and the environment and
should be included on the Federal Superfund National Priorities List. Sites are extracted from the Utah Environmental Interactive Map. The DERR
assumes no responsibility or liability for the accuracy of the location of these properties.
Government Publication Date: Nov 1, 2024
Solid Waste Facilities and Landfills:rr-SWF/LF-bb
A list of solid waste facilities provided by the Utah Department of Environmental Quality Interactive Map.
Government Publication Date: May 6, 2024
Historical Solid Waste and Landfill Facilities:rr-HSWF-bb
The Division of Solid and Hazardous Waste of the Department of Enviromental Quality (DEQ) maintains a list of historically closed landfills. Public Land
Survey System (PLSS) locations provided by the source are subject to accuracy limitations inherent to the PLSS system.
Government Publication Date: Sep 22, 2014
Sites With Leaking Underground Storage Tanks (LUST):rr-LUST-bb
A list of Leaking Underground Storage Tank (LUST) sites made available by the Underground Storage Tank Branch of the Department of Environmental
Quality (DEQ), Division of Environmental Response and Remediation (DERR). The listing Includes sites from the DEQ's LUST Sites List as well as
LUST sites from the DEQ's Environmental Interactive Map, and the Facility UST sites data layer (applicable release sites) from the Utah Open Data
Portal.
Government Publication Date: Sep 23, 2024
Sites With Leaking Aboveground Storage Tanks (LAST):rr-LAST-bb
A list of petroleum storage tank facilities with regulated above ground storage tanks where there has been a release. This listing is provided by the
Environmental Response & Remediation Division of the Utah Department of Environmental Quality (DEQ) and sourced by the DEQ's Environmental
Interactive Map.
Government Publication Date: Sep 22, 2024
Delisted Leaking Storage Tank:rr-DELISTED LST-bb
This database contains a list of closed leaking storage tank sites that were removed from the Utah State Underground Storage Tank program of the
Department of Environmental Quality (DEQ).
Government Publication Date: Sep 22, 2024
Sites With Underground Storage Tanks (UST):rr-UST-bb
A list of Underground Storage Tank (UST) sites made available by the Underground Storage Tank Branch of the Department of Environmental Quality
(DEQ), Division of Environmental Response and Remediation (DERR). The listing Includes sites from the DEQ's UST Sites list as well as UST sites
from the DEQ's Environmental Interactive Map, and the Facility UST sites data layer from the Utah Open Data Portal.
Government Publication Date: Sep 23, 2024
Sites With Aboveground Storage Tanks (AST):rr-AST-bb
A list of state regulated aboveground petroleum storage tanks from the Utah Environmental Interactive Map, provided by the Utah Department of
Environmental Quality.
Government Publication Date: Sep 22, 2024
Tanks Lapse List:rr-UST LAPSE-bb
NPL UT
CONTAM POTENTIAL
SWF/LF
HSWF
LUST
LAST
DELISTED LST
UST
AST
UST LAPSE
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A list of tank facilities that do not have an active Certificate of Compliance due to lapsing, revocation, or installation in process. The listed USTs at these
facilities are ineligible to receive deliveries of fuel. Made available by the Underground Storage Tanks Compliance Branch of the Utah Department of
Environmental Quality.
Government Publication Date: Aug 29, 2024
Delisted Storage Tanks:rr-DTNK-bb
This database contains a list of closed storage tank sites that were removed from the Utah State Underground Storage Tank program of the Department
of Environmental Quality (DEQ).
Government Publication Date: Sep 22, 2024
List of Targeted and Non-targeted Brownfields:rr-BROWNFIELDS-bb
List of Brownfields Projects, either targeted or not targeted for cleanup, made available by the Department of Environmental Quality (DEQ) Division of
Environmental Response and Remediation (DERR). The DERR conducts Brownfields activities under authorities of the Voluntary Release Cleanup Act,
Hazardous Substances Mitigation Act and the Small Business Liability Relief Brownfields Revitalization Act. These statutes provide mechanisms by
which the DERR oversees the assessment and cleanup of Brownfields.
Government Publication Date: Oct 11, 2022
Voluntary Cleanup Site List:rr-VCP-bb
The Voluntary Cleanup Program (VCP) of the Utah Department of Environmental Quality (DEQ) was created to promote the voluntary cleanup of
contaminated sites. The VCP is intended to encourage redevelopment of Brownfields and other impacted sites by providing a streamlined cleanup
program. This data is compiled from the DEQ's Division of Environmental Response & Remediation (DERR) VCP/Brownfields Section Site List and the
DERR VCP Map Data from the Utah Environmental Interactive Map tool.
Government Publication Date: Sep 2, 2024
Response Action Sites:rr-RESPONSE-bb
The Voluntary Cleanup Program/Brownfields Section of the Department of Environmental Quality (DEQ) maintains a list of sites at which Response
Actions are planned or have been completed.
Government Publication Date: Mar 12, 2024
Sites with Institutional Controls:rr-INST-bb
Sites included in the Voluntary Cleanup Program (VCP), Superfund and Underground Storage Tank Facilities list that have environmental convenants
and institutional controls in place.
Government Publication Date: Sep 20, 2023
Tribal
Leaking Underground Storage Tanks on Tribal/Indian Lands:rr-INDIAN LUST-bb
This list of leaking underground storage tanks (LUSTs) on Tribal/Indian Lands in Region 8, which includes Utah, is made available by the United States
Environmental Protection Agency (EPA).
Government Publication Date: May 7, 2024
Underground Storage Tanks on Tribal/Indian Lands:rr-INDIAN UST-bb
This list of underground storage tanks (USTs) on Tribal/Indian Lands in Region 8, which includes Utah, is made available by the United States
Environmental Protection Agency (EPA).
Government Publication Date: May 7, 2024
Delisted Tribal Leaking Storage Tanks:rr-DELISTED INDIAN LST-bb
Leaking Underground Storage Tank (LUST) facilities which once appeared on - and have since been removed from - the Regional Tribal/Indian LUST
lists made available by the United States Environmental Protection Agency (EPA).
Government Publication Date: May 7, 2024
Delisted Tribal Underground Storage Tanks:rr-DELISTED INDIAN UST-bb
Underground Storage Tank (UST) facilities which once appeared on - and have since been removed from - the Regional Tribal/Indian UST lists made
available by the United States Environmental Protection Agency (EPA).
Government Publication Date: May 7, 2024
DTNK
BROWNFIELDS
VCP
RESPONSE
INST
INDIAN LUST
INDIAN UST
DELISTED INDIAN LST
DELISTED INDIAN UST
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County
No County standard environmental record sources available for this State.
Additional Environmental Record Sources
Federal
PFAS Greenhouse Gas Emissions Data:rr-PFAS GHG-bb
The U.S. Environmental Protection Agency's Greenhouse Gas Reporting Program (GHGRP) collects Greenhouse Gas (GHG) data from large emitting
facilities (25,000 metric tons of carbon dioxide equivalent (CO2e) per year), and suppliers of fossil fuels and industrial gases that results in GHG
emissions when used. Includes GHG emissions data for facilities that emit or have emitted since 2010 chemicals identified in EPA's CompTox
Chemicals Dashboard list of PFAS without explicit structures and list of PFAS structures by DSSTox. PFAS emissions data has been identified for
facilities engaged in the following industrial processes: Aluminum Production (GHGRP Subpart F), HCFC-22 Production and HFC-23 Destruction
(Subpart O), Electronics Manufacturing (Subpart I), Fluorinated Gas Production (Subpart L), Magnesium Production (Subpart T), Electrical Transmission
and Distribution Equipment Use (Subpart DD), and Manufacture of Electric Transmission and Distribution Equipment (Subpart SS). Over time, other
industrial processes with required GHGRP reporting may include PFAS emissions data and the list of reportable gases may change over time.
Government Publication Date: Aug 5, 2024
On-Scene Coordinator Response Sites:rr-OSC RESPONSE-bb
This list of On-Scene Coordinator (OSC) Response Sites is provided by the U.S. Environmental Protection Agency (EPA). OSCs are the federal officials
responsible for monitoring or directing responses to all oil spills and hazardous substance releases reported to the federal government. OSCs
coordinate all federal efforts with, and provide support and information to local, state, and regional response communities. An OSC is an agent of either
EPA or the U.S. Coast Guard (USCG), depending on where the incident occurs. EPA's OSCs have primary responsibility for spills and releases to inland
areas and waters. USCG OSCs have responsibility for coastal waters and the Great Lakes. In general, an OSC has the following key responsibilities
during and after a response: Assessment, Monitoring, Response Assistance, and Evaluation.
Government Publication Date: Apr 4, 2024
Facility Registry Service/Facility Index:rr-FINDS/FRS-bb
The Facility Registry Service (FRS) is a centrally managed database that identifies facilities, sites, or places subject to environmental regulations or of
environmental interest. FRS creates high-quality, accurate, and authoritative facility identification records through rigorous verification and management
procedures that incorporate information from program national systems, state master facility records, and data collected from EPA's Central Data
Exchange registrations and data management personnel. This list is made available by the U.S. Environmental Protection Agency (EPA).
Government Publication Date: Aug 1, 2024
Toxics Release Inventory (TRI) Program:rr-TRIS-bb
The U.S. Environmental Protection Agency's Toxics Release Inventory (TRI) is a database containing data on disposal or other releases of toxic
chemicals from U.S. facilities and information about how facilities manage those chemicals through recycling, energy recovery, and treatment. There are
currently 770 individually listed chemicals and 33 chemical categories covered by the TRI Program. Facilities that manufacture, process or otherwise
use these chemicals in amounts above established levels must submit annual reporting forms for each chemical. Note that the TRI chemical list does
not include all toxic chemicals used in the U.S. One of TRI's primary purposes is to inform communities about toxic chemical releases to the
environment. This database includes TRI Reporting Data for calendar years 1987 through 2021 and Preliminary Data for 2022.
Government Publication Date: Sep 20, 2023
PFOA/PFOS Contaminated Sites:rr-PFAS NPL-bb
This list of Superfund Sites with Per- and Polyfluoroalkyl Substances (PFAS) detections is made available by the U.S. Environmental Protection Agency
(EPA) in their PFAS Analytic Tools data, previously the list was obtained by EPA FOIA requests. EPA's Office of Land and Emergency Management and
EPA Regional Offices maintain what is known about site investigations, contamination, and remedial actions under the Comprehensive Environmental
Response, Compensation, and Liability Act (CERCLA) where PFAS is present in the environment. Limitations: Detections of PFAS at National Priorities
List (NPL) sites do not mean that people are at risk from PFAS, are exposed to PFAS, or that the site is the source of the PFAS. The information in the
Superfund NPL and Superfund Alternative Agreement (SAA) PFAS detection site list is years old and may not be accurate today. Site information such
as site name, site ID, and location has been confirmed for accuracy; however, PFAS-related information such as media sampled, drinking water being
above the health advisory, or mitigation efforts has not been verified. For Federal Facilities data, the other Federal agencies (OFA) are the lead agency
for their data and provided them to EPA.
Government Publication Date: Sep 18, 2024
Federal Agency Locations with Known or Suspected PFAS Detections:rr-PFAS FED SITES-bb
PFAS GHG
OSC RESPONSE
FINDS/FRS
TRIS
PFAS NPL
PFAS FED SITES
162 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
List of Federal agency locations with known or suspected detections of Per- and Polyfluoroalkyl Substances (PFAS), made available by the U.S.
Environmental Protection Agency (EPA) in their PFAS Analytic Tools data. EPA outlines that these data are gathered from several federal entities, such
as the Federal Superfund program, Department of Defense (DOD), National Aeronautics and Space Administration, Department of Transportation, and
Department of Energy. The dates this data was extracted for the PFAS Analytic Tools range from 2022 to 2024. Sites on this list do not necessarily
reflect the source/s of PFAS contamination and detections do not indicate level of risk or human exposure at the site. Agricultural notifications in this
data are limited to DOD sites only. At this time, the EPA is aware that this list is not comprehensive of all Federal agencies.
Government Publication Date: Jul 22, 2024
SSEHRI PFAS Contamination Sites:rr-PFAS SSEHRI-bb
This PFAS Contamination Site Tracker database is compiled by the PFAS Project Lab, part of the Social Science Environmental Health Research
Institute (SSEHRI) at Northeastern University. According to the SSEHRI, the database records qualitative and quantitative data from each known site of
PFAS contamination, including timeline of discovery, sources, levels, health impacts, community response, and government response. The goal of this
database is to compile information and support public understanding of the rapidly unfolding issue of PFAS contamination. All data presented was
extracted from government websites, news articles, or publicly available documents. Locations for the Known PFAS Contamination Sites are sourced
from the PFAS Sites and Community Resources Map by the PFAS-REACH team, credited to PFAS Project Lab, Silent Spring Institute, and PFAS
Exchange. Disclaimer: The source conveys the data undergoes regular updates as new information becomes available, some sites may be missing
and/or contain information that is incorrect or outdated, as well as their information represents all contamination sites SSEHRI is aware of, not all
possible contamination sites. This data is not intended to be used for legal purposes. Access the following source link for the most current information:
https://pfasproject.com/pfas-sites-and-community-resources/
Government Publication Date: Jun 27, 2024
National Response Center PFAS Spills:rr-PFAS ERNS-bb
This Per- and Poly-Fluoroalkyl Substances (PFAS) Spills dataset is made available via the U.S. Environmental Protection Agency's (EPA) PFAS
Analytic Tools. The National Response Center (NRC), operated by the U.S. Coast Guard, is the designated federal point of contact for reporting all oil,
chemical, and other discharges into the environment, for the United States and its territories. This dataset contains NRC spill information from 1990 to
the present that is restricted to records associated with PFAS and PFAS-containing materials. Incidents are filtered to include only records with a
"Material Involved" or "Incident Description" related to Aqueous Film Forming Foam (AFFF). The keywords used to filter the data included "AFFF," "Fire
Fighting Foam," "Aqueous Film Forming Foam," "Fire Suppressant Foam, "PFAS," "PERFL," "PFOA," "PFOS," and "Genx." Limitations: The data from
the NRC website contains initial incident data that has not been validated or investigated by a federal/state response agency. Keyword searches may
misidentify some incident reports that do not contain PFAS. This dataset should also not be considered to be exhaustive of all PFAS spills/release
incidents.
Government Publication Date: Sep 23, 2024
PFAS NPDES Discharge Monitoring:rr-PFAS NPDES-bb
This list of National Pollutant Discharge Elimination System (NPDES) permitted facilities with required monitoring for Per- and Polyfluoroalkyl (PFAS)
Substances is made available via the U.S. Environmental Protection Agency (EPA)'s PFAS Analytic Tools. Any point-source wastewater discharger to
waters of the United States must have a NPDES permit, which defines a set of parameters for pollutants and monitoring to ensure that the discharge
does not degrade water quality or impair human health. This list includes NPDES permitted facilities associated with permits that monitor for Per- and
Polyfluoroalkyl Substances (PFAS), limited to the years 2007 - present. EPA further advises the following regarding these data: currently, fewer than half
of states have required PFAS monitoring for at least one of their permittees, and fewer states have established PFAS effluent limits for permittees. For
states that may have required monitoring, some reporting and data transfer issues may exist on a state-by-state basis.
Government Publication Date: Sep 30, 2024
Perfluorinated Alkyl Substances (PFAS) from Toxic Release Inventory:rr-PFAS TRI-bb
List of Toxics Release Inventory (TRI) facilities at which the reported chemical is a per- or polyfluoroalkyl (PFAS) substance included in the U.S.
Environmental Protection Agency's (EPA) consolidated PFAS Master List of PFAS Substances. Encompasses Toxics Release Inventory records
included in the EPA PFAS Analytic Tools. The EPA's TRI database currently tracks information on disposal or releases of 770 individually listed toxic
chemicals and 33 chemical categories from thousands of U.S. facilities and details about how facilities manage those chemicals through recycling,
energy recovery, and treatment. This listing includes TRI Reporting Data for calendar years 1987 through 2021 and Preliminary Data for 2022.
Government Publication Date: Sep 20, 2023
PFAS Water Quality Portal Sampling Data:rr-PFAS WATER-bb
This Per- and Poly-Fluoroalkyl Substances (PFAS) Environmental Media Sampling Data is made available via the U.S. Environmental Protection
Agency's (EPA) PFAS Analytic Tools. The Water Quality Portal (WQP), as a cooperative service sponsored by the United States Geological Survey, the
EPA, and the National Water Quality Monitoring Council, is part of a modernized repository storing ambient sampling data for all environmental media
and tissue samples. A wide range of federal, state, tribal and local governments, academic and non-governmental organizations, and individuals submit
project details and sampling results to this public repository. Limitations: EPA did not carry out the sampling or testing of a majority of the data in the
WQP PFAS dataset. EPA can only speak to the accuracy and completeness of the data from projects like the National Aquatic Resource Surveys for
which EPA is the data owner/organization. Data may exist within the file on Quality Assurance Project Plans (QAPPs) and the approving agency of the
QAPP, if a QAPP is entered.
PFAS SSEHRI
PFAS ERNS
PFAS NPDES
PFAS TRI
PFAS WATER
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Government Publication Date: Jul 22, 2024
PFAS TSCA Manufacture and Import Facilities:rr-PFAS TSCA-bb
The U.S. Environmental Protection Agency (EPA) issued the Chemical Data Reporting (CDR) Rule under the Toxic Substances Control Act (TSCA) and
requires chemical manufacturers and facilities that manufacture or import chemical substances to report data to EPA. This list is specific only to TSCA
Manufacture and Import Facilities with reported per- and poly-fluoroalkyl (PFAS) substances. Data file is sourced from EPA's PFAS Analytic Tools TSCA
dataset which includes CDR/Inventory Update Reporting data from 1998 up to 2020. Disclaimer: This data file includes production and importation data
for chemicals identified in EPA's CompTox Chemicals Dashboard list of PFAS without explicit structures and list of PFAS structures in DSSTox. Note
that some regulations have specific chemical structure requirements that define PFAS differently than the lists in EPA's CompTox Chemicals
Dashboard. Reporting information on manufactured or imported chemical substance amounts should not be compared between facilities, as some
companies claim Chemical Data Reporting Rule data fields for PFAS information as Confidential Business Information.
Government Publication Date: Jan 5, 2023
PFAS Waste Transfers from RCRA e-Manifest :rr-PFAS E-MANIFEST-bb
This Per- and Poly-Fluoroalkyl Substances (PFAS) Waste Transfers dataset is made available via the U.S. Environmental Protection Agency's (EPA)
PFAS Analytic Tools. Every shipment of hazardous waste in the U.S. must be accompanied by a shipment manifest, which is a critical component of the
cradle-to-grave tracking of wastes mandated by the Resource Conservation and Recovery Act (RCRA). According to the EPA, currently no Federal
Waste Code exists for any PFAS compounds. To work around the lack of PFAS waste codes in the RCRA database, EPA developed the PFAS
Transfers dataset by mining e-Manifest records containing at least one of these common PFAS keywords: • PFAS • PFOA • PFOS • PERFL • AFFF •
GENX • GEN-X (plus the Vermont state-specific waste codes). Limitations: Amount or concentration of PFAS being transferred cannot be determined
from the manifest information. Keyword searches may misidentify some manifest records that do not contain PFAS. This dataset should also not be
considered to be exhaustive of all PFAS waste transfers.
Government Publication Date: Sep 22, 2024
PFAS Industry Sectors:rr-PFAS IND-bb
This Per- and Poly-Fluoroalkyl Substances (PFAS) Industry Sectors dataset is made available via the U.S. Environmental Protection Agency's (EPA)
PFAS Analytic Tools. The EPA developed the dataset from various sources that show which industries may be handling PFAS including: EPA's
Enforcement and Compliance History Online (ECHO) records restricted to potential PFAS-handling industry sectors; ECHO records for Fire Training
Sites identified where fire-fighting foam may have been used in training exercises; and 14 CFR Part 139 Airports compiled from historic and current
records from the FAA Airport Data and Information Portal. Since July 2006, all certificated Part 139 Airports are required to have fire-fighting foam onsite
that meet certain military specifications, which to date have been fluorinated (Aqueous Film Forming Foam). Limitations: Inclusion in this dataset does
not indicate that PFAS are being manufactured, processed, used, or released by the facility. Listed facilities potentially handle PFAS based on their
industrial profile, but are unconfirmed by the EPA. Keyword searches in ECHO for Fire Training sites may misidentify some facilities and should not be
considered to be an exhaustive list of fire training facilities in the U.S.
Government Publication Date: Sep 23, 2024
Hazardous Materials Information Reporting System:rr-HMIRS-bb
The Hazardous Materials Incident Reporting System (HMIRS) database contains unintentional hazardous materials release information reported to the
U.S. Department of Transportation, Pipeline and Hazardous Materials Safety Administration.
Government Publication Date: May 29, 2024
National Clandestine Drug Labs:rr-NCDL-bb
The U.S. Department of Justice ("the Department"), Drug Enforcement Administration (DEA), provides this data as a public service. It contains
addresses of some locations where law enforcement agencies reported they found chemicals or other items that indicated the presence of either
clandestine drug laboratories or dumpsites. In most cases, the source of the entries is not the Department, and the Department has not verified the entry
and does not guarantee its accuracy.
Government Publication Date: Nov 30, 2023
Toxic Substances Control Act:rr-TSCA-bb
The U.S. Environmental Protection Agency (EPA) is amending the Toxic Substances Control Act (TSCA) section 8(a) Inventory Update Reporting (IUR)
rule and changing its name to the Chemical Data Reporting (CDR) rule. The CDR enables EPA to collect and publish information on the manufacturing,
processing, and use of commercial chemical substances and mixtures (referred to hereafter as chemical substances) on the TSCA Chemical Substance
Inventory (TSCA Inventory). This includes current information on chemical substance production volumes, manufacturing sites, and how the chemical
substances are used. This information helps the Agency determine whether people or the environment are potentially exposed to reported chemical
substances. EPA publishes submitted CDR data that is not Confidential Business Information (CBI). EPA CDR collections occur approximately every
four years and reporting requirements change per collection.
Government Publication Date: May 12, 2022
PFAS TSCA
PFAS E-MANIFEST
PFAS IND
HMIRS
NCDL
TSCA
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Hist TSCA:rr-HIST TSCA-bb
The Environmental Protection Agency (EPA) is amending the Toxic Substances Control Act (TSCA) section 8(a) Inventory Update Reporting (IUR) rule
and changing its name to the Chemical Data Reporting (CDR) rule.
The 2006 IUR data summary report includes information about chemicals manufactured or imported in quantities of 25,000 pounds or more at a single
site during calendar year 2005. In addition to the basic manufacturing information collected in previous reporting cycles, the 2006 cycle is the first time
EPA collected information to characterize exposure during manufacturing, processing and use of organic chemicals. The 2006 cycle also is the first time
manufacturers of inorganic chemicals were required to report basic manufacturing information.
Government Publication Date: Dec 31, 2006
FTTS Administrative Case Listing:rr-FTTS ADMIN-bb
An administrative case listing from the Federal Insecticide, Fungicide, & Rodenticide Act (FIFRA) and Toxic Substances Control Act (TSCA), together
known as FTTS. This database was obtained from the Environmental Protection Agency's (EPA) National Compliance Database (NCDB). The FTTS
and NCDB was shut down in 2006.
Government Publication Date: Jan 19, 2007
FTTS Inspection Case Listing:rr-FTTS INSP-bb
An inspection case listing from the Federal Insecticide, Fungicide, & Rodenticide Act (FIFRA) and Toxic Substances Control Act (TSCA), together
known as FTTS. This database was obtained from the Environmental Protection Agency's (EPA) National Compliance Database (NCDB). The FTTS
and NCDB was shut down in 2006.
Government Publication Date: Jan 19, 2007
Potentially Responsible Parties List:rr-PRP-bb
Early in the site cleanup process, the U.S. Environmental Protection Agency (EPA) conducts a search to find the Potentially Responsible Parties
(PRPs). The EPA looks for evidence to determine liability by matching wastes found at the site with parties that may have contributed wastes to the site.
This listing contains PRPs, Noticed Parties, at sites in the EPA's Superfund Enterprise Management System (SEMS).
Government Publication Date: Jul 24, 2024
State Coalition for Remediation of Drycleaners Listing:rr-SCRD DRYCLEANER-bb
The State Coalition for Remediation of Drycleaners (SCRD) was established in 1998, with support from the U.S. Environmental Protection Agency
(EPA) Office of Superfund Remediation and Technology Innovation. Coalition members are states with mandated programs and funding for drycleaner
site remediation. Current members are Alabama, Connecticut, Florida, Illinois, Kansas, Minnesota, Missouri, North Carolina, Oregon, South Carolina,
Tennessee, Texas, and Wisconsin. Since 2017, the SCRD no longer maintains this data, refer to applicable state source data where available.
Government Publication Date: Nov 08, 2017
Integrated Compliance Information System (ICIS):rr-ICIS-bb
The Integrated Compliance Information System (ICIS) database contains integrated enforcement and compliance information across most of U.S.
Environmental Protection Agency's (EPA) programs. The vision for ICIS is to replace EPA's independent databases that contain enforcement data with
a single repository for that information. Currently, ICIS contains all Federal Administrative and Judicial enforcement actions and a subset of the Permit
Compliance System (PCS), which supports the National Pollutant Discharge Elimination System (NPDES). This information is maintained by the EPA
Headquarters and at the Regional offices. A future release of ICIS will completely replace PCS and will integrate that information with Federal actions
already in the system. ICIS also has the capability to track other activities that support compliance and enforcement programs, including incident
tracking, compliance assistance, and compliance monitoring.
Government Publication Date: Apr 13, 2024
Drycleaner Facilities:rr-FED DRYCLEANERS-bb
A list of drycleaner facilities from Enforcement and Compliance History Online (ECHO) data as made available by the U.S. Environmental Protection
Agency (EPA), sourced from the ECHO Exporter file. The EPA tracks facilities that possess NAIC and SIC codes that classify businesses as drycleaner
establishments.
Government Publication Date: May 5, 2024
Delisted Drycleaner Facilities:rr-DELISTED FED DRY-bb
List of sites removed from the list of Drycleaner Facilities (sites in the EPA's Integrated Compliance Information System (ICIS) with NAIC or SIC codes
identifying the business as a drycleaner establishment).
Government Publication Date: May 5, 2024
Formerly Used Defense Sites:rr-FUDS-bb
HIST TSCA
FTTS ADMIN
FTTS INSP
PRP
SCRD DRYCLEANER
ICIS
FED DRYCLEANERS
DELISTED FED DRY
FUDS
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Formerly Used Defense Sites (FUDS) are properties that were formerly owned by, leased to, or otherwise possessed by and under the jurisdiction of the
Secretary of Defense prior to October 1986, where the Department of Defense (DOD) is responsible for an environmental restoration. The FUDS Annual
Report to Congress (ARC) is published by the U.S. Army Corps of Engineers (USACE). This data is compiled from the USACE's Geospatial FUDS data
layers and Homeland Infrastructure Foundation-Level Data (HIFLD) FUDS dataset which applies to the Fiscal Year 2021 FUDS Inventory.
Government Publication Date: May 15, 2023
FUDS Munitions Response Sites:rr-FUDS MRS-bb
Boundaries of Munitions Response Sites (MRS), published with the Formerly Used Defense Sites (FUDS) Annual Report to Congress (ARC) by the U.S.
Army Corps of Engineers (USACE). An MRS is a discrete location within a Munitions response area (MRA) that is known to require a munitions
response. An MRA means any area on a defense site that is known or suspected to contain unexploded ordnance (UXO), discarded military munitions
(DMM), or munitions constituents (MC). This data is compiled from the USACE's Geospatial MRS data layers and Homeland Infrastructure Foundation-
Level Data (HIFLD) MRS dataset.
Government Publication Date: May 15, 2023
Former Military Nike Missile Sites:rr-FORMER NIKE-bb
This information was taken from report DRXTH-AS-IA-83A016 (Historical Overview of the Nike Missile System, 12/1984) which was performed by
Environmental Science and Engineering, Inc. for the U.S. Army Toxic and Hazardous Materials Agency Assessment Division. The Nike system was
deployed between 1954 and the mid-1970's. Among the substances used or stored on Nike sites were liquid missile fuel (JP-4); starter fluids (UDKH,
aniline, and furfuryl alcohol); oxidizer (IRFNA); hydrocarbons (motor oil, hydraulic fluid, diesel fuel, gasoline, heating oil); solvents (carbon tetrachloride,
trichloroethylene, trichloroethane, stoddard solvent); and battery electrolyte. The quantities of material a disposed of and procedures for disposal are not
documented in published reports. Virtually all information concerning the potential for contamination at Nike sites is confined to personnel who were
assigned to Nike sites. During deactivation most hardware was shipped to depot-level supply points. There were reportedly instances where excess
materials were disposed of on or near the site itself at closure. There was reportedly no routine site decontamination.
Government Publication Date: Dec 2, 1984
PHMSA Pipeline Safety Flagged Incidents:rr-PIPELINE INCIDENT-bb
This list of flagged pipeline incidents is made available by the U.S. Department of Transportation (US DOT) Pipeline and Hazardous Materials Safety
Administration (PHMSA). PHMSA regulations require incident and accident reports for five different pipeline system types. Accidents reported on
hazardous liquid gravity lines (§195.13) and reporting-regulated-only hazardous liquid gathering lines (§195.15) and incidents reported on Type R gas
gathering (§192.8(c)) are not included in the flagged incident file data.
Government Publication Date: May 6, 2024
Material Licensing Tracking System (MLTS):rr-MLTS-bb
A list of sites that store radioactive material subject to the Nuclear Regulatory Commission (NRC) licensing requirements. This list is maintained by the
NRC. As of September 2016, the NRC no longer releases location information for sites. Site locations were last received in July 2016.
Government Publication Date: May 11, 2021
Historic Material Licensing Tracking System (MLTS) sites:rr-HIST MLTS-bb
A historic list of sites that have inactive licenses and/or removed from the Material Licensing Tracking System (MLTS). In some cases, a site is removed
from the MLTS when the state becomes an "Agreement State". An Agreement State is a State that has signed an agreement with the Nuclear
Regulatory Commission (NRC) authorizing the State to regulate certain uses of radioactive materials within the State.
Government Publication Date: Jan 31, 2010
Mines Master Index File:rr-MINES-bb
The Master Index File (MIF) is provided by the United States Department of Labor, Mine Safety and Health Administration (MSHA). This file, which was
originally created in the 1970's, contained many Mine-IDs that were invalid. MSHA removes invalid IDs from the MIF upon discovery. MSHA applicable
data includes the following: all Coal and Metal/Non-Metal mines under MSHA's jurisdiction since 1/1/1970; mine addresses for all mines in the database
except for Abandoned mines prior to 1998 from MSHA's legacy system (addresses may or may not correspond with the physical location of the mine
itself); violations that have been assessed penalties as a result of MSHA inspections beginning on 1/1/2000; and violations issued as a result of MSHA
inspections conducted beginning on 1/1/2000.
Government Publication Date: Feb 5, 2024
Surface Mining Control and Reclamation Act Sites:rr-SMCRA-bb
FUDS MRS
FORMER NIKE
PIPELINE INCIDENT
MLTS
HIST MLTS
MINES
SMCRA
166 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
This inventory of land and water impacted by past mining (primarily legacy coal mining operations) is maintained by the U.S. Department of the Interior's
Office of Surface Mining Reclamation and Enforcement (OSMRE), as it provides information needed to implement the Surface Mining Control and
Reclamation Act of 1977 (SMCRA). This inventory contains information on the type and extent of Abandoned Mine Land (AML) Problems, as well as
information on the cost associated with the reclamation of those problems. The data is based upon field surveys by State, Tribal, and OSMRE program
officials. It is dynamic to the extent that it is modified as new problems are identified and existing problems are reclaimed. Disclaimer: Per the OSMRE,
States and tribes who enter their data into e-AMLIS (AML Inventory System) may truncate their latitude and longitude so the precise location of usually
dangerous AMLs is not revealed in an effort to protect the public from searching for these AMLs, most of which are on private property. If more precise
location information is needed, please contact the applicable state/tribe of interest.
Government Publication Date: May 20, 2024
Mineral Resource Data System:rr-MRDS-bb
The Mineral Resource Data System (MRDS) is a collection of reports describing metallic and nonmetallic mineral resources throughout the world.
Included are deposit name, location, commodity, deposit description, geologic characteristics, production, reserves, resources, and references. This
database contains the records previously provided in the Mineral Resource Data System (MRDS) of USGS and the Mineral Availability System/Mineral
Industry Locator System (MAS/MILS) originated in the U.S. Bureau of Mines, which is now part of USGS. The USGS has ceased systematic updates of
the MRDS database with their focus more recently on deposits of critical minerals while providing a well-documented baseline of historical mine
locations from USGS topographic maps.
Government Publication Date: Mar 15, 2016
DOE Legacy Management Sites:rr-LM SITES-bb
The U.S. Department of Energy (DOE) Office of Legacy Management (LM) currently manages radioactive and chemical waste, environmental
contamination, and hazardous material at over 100 sites across the U.S. The LM manages sites with diverse regulatory drivers (statutes or programs
that direct cleanup and management requirements at DOE sites) or as part of internal DOE or congressionally-recognized programs, such as but not
limited to: Formerly Utilized Sites Remedial Action Program (FUSRAP), Uranium Mill Tailings Radiation Control Act (UMTRCA Title I, Tile II),
Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA), Resource Conservation and Recovery Act (RCRA),
Decontamination and Decommissioning (D&D), Nuclear Waste Policy Act (NWPA). This site listing includes data exported from the DOE Office of LM'
s Geospatial Environmental Mapping System (GEMS). GEMS Data disclaimer: The DOE Office of LM makes no representation or warranty, expressed
or implied, regarding the use, accuracy, availability, or completeness of the data presented herein.
Government Publication Date: Dec 12, 2023
Alternative Fueling Stations:rr-ALT FUELS-bb
This list of alternative fueling stations is sourced from the Alternative Fuels Data Center (AFDC). The U.S. Department of Energy's Office of Energy
Efficiency & Renewable Energy launched the AFDC in 1991 as a repository for alternative fuel vehicle performance data, which provides a wealth of
information and data on alternative and renewable fuels, advanced vehicles, fuel-saving strategies, and emerging transportation technologies. The data
includes Biodiesel (B20 and above), Compressed Natural Gas (CNG), Electric, Ethanol (E85), Hydrogen, Liquefied Natural Gas (LNG), Propane (LPG),
and Renewable Diesel (R20 and above) fuel type locations.
Government Publication Date: Aug 29, 2024
Superfunds Consent Decrees:rr-CONSENT DECREES-bb
This list of Superfund consent decrees is provided by the Department of Justice, Environment & Natural Resources Division (ENRD) through a Freedom
of Information Act (FOIA) applicable file. This listing includes Cases filed since 2010 limited to the following: Consent Decrees for CERCLA or Superfund
Sites filed and/or as proposed within the ENRD's Case Management System (CMS); and applicable ENRD's Environmental Defense Section (EDS)
CERCLA Cases with "Consent" in History Note. CMS may not reflect the latest developments in a case, nor can the agency guarantee the accuracy of
the data. ENRD Disclaimer: Congress excluded three discrete categories of law enforcement and national security records from the requirements of the
FOIA; response is limited to those records that are subject to the requirements of the FOIA; however, this should not be taken as an indication that
excluded records do, or do not, exist.
Government Publication Date: Jun 26, 2024
Air Facility System:rr-AFS-bb
This EPA retired Air Facility System (AFS) dataset contains emissions, compliance, and enforcement data on stationary sources of air pollution.
Regulated sources cover a wide spectrum; from large industrial facilities to relatively small operations such as dry cleaners. AFS does not contain data
on facilities that are solely asbestos demolition and/or renovation contractors, or landfills. ECHO Clean Air Act data from AFS are frozen and reflect
data as of October 17, 2014; the EPA retired this system for Clean Air Act stationary sources and transitioned to ICIS-Air.
Government Publication Date: Oct 17, 2014
Registered Pesticide Establishments:rr-SSTS-bb
MRDS
LM SITES
ALT FUELS
CONSENT DECREES
AFS
SSTS
167 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
This national list of active EPA-registered foreign and domestic pesticide and/or device-producing establishments is based on data from the Section
Seven Tracking System (SSTS). The Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) Section 7 requires that each producing establishment
must place its EPA establishment number on the label or immediate container of each pesticide, active ingredient or device produced. An EPA
establishment number on a pesticide product label identifies the EPA registered location where the product was produced. The list of establishments is
made available by the U.S. Environmental Protection Agency (EPA).
Government Publication Date: Feb 29, 2024
Polychlorinated Biphenyl (PCB) Transformers:rr-PCBT-bb
Locations of Transformers Containing Polychlorinated Biphenyls (PCBs) registered with the United States Environmental Protection Agency. PCB
transformer owners must register their transformer(s) with EPA. Although not required, PCB transformer owners who have removed and properly
disposed of a registered PCB transformer may notify EPA to have their PCB transformer de-registered. Data made available by EPA.
Government Publication Date: Oct 15, 2019
Polychlorinated Biphenyl (PCB) Notifiers:rr-PCB-bb
Facilities included in the national list of facilities that have notified the United States Environmental Protection Agency (EPA) of Polychlorinated Biphenyl
(PCB) activities. Any company or person storing, transporting or disposing of PCBs or conducting PCB research and development must notify the EPA
and receive an identification number.
Government Publication Date: May 23, 2024
Power Plants:rr-POWER PLANTS-bb
This list of power plants is provided by the U.S. Energy Information Administration (EIA). The listing includes operable electric generating plants in the
United States by energy source, originating from the EIA-860, Annual Electric Generator Report; EIA-860M, Monthly Update to the Annual Electric
Generator Report; and EIA-923, Power Plant Operations Report. It includes all operable plants by energy source with a combined nameplate capacity of
1 megawatt or more that are operating, are on standby, or out of service for short- or long-term.
Government Publication Date: Apr 15, 2024
State
Environmental Incidents:rr-SPILLS-bb
Regulated industry, permitted facilities, waste transporters and others are required by federal and/or state laws or regulations to report chemical spills
and other environmental incidents within certain time frames, depending on the type of incident. These incidents are reported to The Division of
Environmental Response & Remediation (DERR) of the Utah Department of Environmental Quality (DEQ).
Government Publication Date: Sep 19, 2024
Methamphetamine Contaminated Properties:rr-CDL-bb
Utah Administrative Rule 19-6-901 Illegal Drug Operations Site Reporting and Decontamination Act requires local health departments to maintain a list
of properties believed to be contaminated by the illegal manufacture of drugs. These properties were reported to the Salt Lake Valley Health Department
by a complaint or report from a law enforcement agency and the Department has determined that reasonable evidence exists that the property is
contaminated. Once a property is decontaminated, it is removed from this list.
Government Publication Date: Jul 6, 2024
Dry Cleaning Facilities:rr-DRYCLEANERS-bb
The Division of Air Quality of the Utah Department of Environmental Quality (DEQ) maintains a list of regulated dry cleaners that use perchlorethylene
(PCE). This site data is compiled from applicable FOIA files received from the DEQ's Division of Air Quality, the DEQ's Environmental Interactive Map
layer of Dry Cleaner Facilities, and the Utah OpenData Catalog Dry Cleaners dataset.
Government Publication Date: Aug 21, 2024
Delisted Drycleaners:rr-DELISTED DRYCLEANERS-bb
A list of sites which once appeared on - and have since been removed from - the list of regulated dry cleaners that use perchlorethylene (PCE) made
available by the Division of Air Quality of the Department of Environmental Quality (DEQ).
Government Publication Date: Aug 21, 2024
Tier 2 Chemical Inventory Program:rr-TIER 2-bb
A list of Tier 2 facilities managed by the Division of Environmental Response and Remediation (DERR) of the the Utah Department of Environmental
Quality (DEQ).
Government Publication Date: May 6, 2024
PCBT
PCB
POWER PLANTS
SPILLS
CDL
DRYCLEANERS
DELISTED DRYCLEANERS
TIER 2
168 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
Tribal
No Tribal additional environmental record sources available for this State.
County
No County additional environmental record sources available for this State.
169 erisinfo.com | Environmental Risk Information Services Order No: 24111900057
h-Definitions
Database Descriptions:This section provides a detailed explanation for each database including:source,information available,time coverage,and
acronyms used.They are listed in alphabetic order.
Detail Report:This is the section of the report which provides the most detail for each individual record.Records are summarized by location,starting
with the project property followed by records in closest proximity.
Distance:The distance value is the distance between plotted points,not necessarily the distance between the sites'boundaries.All values are an
approximation.
Direction: The direction value is the compass direction of the site in respect to the project property and/or center point of the report.
Elevation:The elevation value is taken from the location at which the records for the site address have been plotted.All values are an approximation.
Source:Google Elevation API.
Executive Summary:This portion of the report is divided into 3 sections:
'Report Summary'-Displays a chart indicating how many records fall on the project property and,within the report search radii.
'Site Report Summary'-Project Property'-This section lists all the records which fall on the project property.For more details,see the 'Detail Report'
section.
'Site Report Summary-Surrounding Properties'-This section summarizes all records on adjacent properties,listing them in order of proximity from the
project property.For more details,see the 'Detail Report'section.
Map Key:The map key number is assigned according to closest proximity from the project property.Map Key numbers always start at #1.The project
property will always have a map key of '1'if records are available.If there is a number in brackets beside the main number,this will indicate the number
of records on that specific property.If there is no number in brackets,there is only one record for that property.
The symbol and colour used indicates 'elevation':the red inverted triangle will dictate 'ERIS Sites with Lower Elevation',the yellow triangle will dictate
'ERIS Sites with Higher Elevation'and the orange square will dictate 'ERIS Sites with Same Elevation.'
Unplottables:These are records that could not be mapped due to various reasons,including limited geographic information.These records may or
may not be in your study area,and are included as reference.
Definitions
ESI 2019 Results Report Cardno
Airport West VCP #C092 819AR00640
9 v1, 12-10-21
EXECUTIVE SUMMARY
Cardno, Inc. (Cardno) is pleased to present the following Results Report summarizing the September
through October 2019 Expanded Subsurface Investigation (ESI), to the Utah Department of
Environmental Quality (UDEQ), Division of Environmental Response and Remediation (DERR) for the
Airport West property (Site), formerly the North Temple Landfill (NTL), and property west and
downgradient on land currently owned by Kennecott. The Kennecott property was formerly owned and
referenced in previous reports as the Epperson Property. The address of the Site is generally referred
as 7200 West North Temple Frontage Road in Salt Lake City, Utah (Figure 1 Regional Topographic Map
and Figure 2 Site Vicinity Map).
while Salt Lake City was still actively operating the landfill through the more recent studies undertaken
as part of the VCP. This current ESI is an expanded characterization of the shallow aquifer and soil
conditions that exist at, and adjacent to, the Site. This report supplements those more recent studies
including (1) an initial Subsurface Investigation (SI) performed along the western portions of the Site in
Final dated June
1, 2016; (2) A follow-up ESI conducted in mid-2017 to collect a second round of the 2015 ESI wells,
expand the characterization further west and downgradient of the former NTL and to collect soil vapor
samples along the western boundary of the NTL; and (3) an August 2018 Supplemental Site
Characterization Study conducted by Ninigret, the expanded scope of which included the installation of
eight new sets of nested shallow and deep wells, re-sampling of the existing nine perimeter wells
surrounding the NTL, sampling of test pits advanced into the waste cells, collection of geophysical and
chemical soil and water data and a pilot study to evaluate various leachate treatment approaches.
One of the main objectives of this 2019 ESI was to determine the extent and level of reported
contaminants identified in previous investigations along the western boundary, as to their
concentrations and potential migration in groundwater farther west in the apparent downgradient
direction. This 2019 ESI was developed to collect a second round of samples from the new shallow 2018
Airport West Perimeter wells, collect addition sample data from the historic perimeter NTL wells and
ground water data was supplemented by the collection of samples from the existing 2017 wells located
500 feet west of the Site and new wells installed as part of this study located at 700 and 900 feet west
and down gradient of the Site.
Based on the results of this ESI and previous studies, the direction of localized groundwater flow along
the NTLs western boundary has been identified as following a west to southwest direction (Figure 4
Groundwater Elevation Map) along the southwest boundary and north to northwest along the
northwest boundary. The general westerly direction of groundwater flow in the western area of the
Site may be due to the proximity and direction of flow of the West Branch of the Brighton Canal as it
ESI 2019 Results Report Cardno
Airport West VCP #C092 819AR00640
10 v1, 12-10-21
historically has bisected the trench fill construction of the former landfilling operations. Other than this
area west of the canal, the eastern area of the Site and the surrounding areas have a northerly direction
to the shallow groundwater flow.
For screening of the analytical results, a unique Project Screening Level (PSL) was established using a
hierarchy of published regulatory levels for each of the various constituents sampled. Where a United
States Environmental Protection Agency (USEPA) Maximum Contaminant Levels (MCLs) is established,
the MCL is used. Where a MCL is not established, a Utah DERR Leaking Underground Tank (LUST) Initial
Screening Level (ISL) is used. Where these standards are not established the USEPA 2020 Regional
Screening Level (RSL) is used. Where RSLs are used, the tap water RSL is used for water results. For soil
vapor results the resident air and industrial air RSL is used. Soil Vapor results were also used in USEPA
Vapor Intrusion Screening Level (VISL) model for residential and commercial exposure.
A total of 66 monitoring locations were sampled for groundwater. Thirty are located off-site and
downgradient between 200 and 900 feet to the west on the Kennecott property. Six are located along
the western boundary. Five are located along the northern boundary. Four are located along the
southwest boundary. Three are located along the southeast boundary and are consider upgradient
wells. Seven of these new wells are located along the downgradient boundary of the area within the
eastern area of the Site.
Ground water analysis
1) The highest concentration of identified contaminants were identified in the western perimeter
and western perimeter interior wells. Elevated concentrations of 1,4-dioxane and arsenic were
found present throughout the 2019 wells. The drinking water MCL for Arsenic is low and some
detection of arsenic in groundwater is common in Utah due to the higher than average
concentrations in the naturally occurring soils. There is no MCL for 1,4-dioxane and drinking
water RSL used for the PSL for 1,4-dioxane is low. The elevated levels of 1,4-dioxane in the
groundwater compared to the drinking water RSL, do not translate directly to high inhalation
risks, due to the lower potential volatilization of this VOC compound compared to other VOCs
of concern for inhalation risks. Preliminary evaluations have identified the target groundwater
concentrations to be an order of magnitude higher than levels which may pose an inhalation
metal barium varied at specific locations along the western portion of the site indicating a
correlation between source material rather than an overall site condition. No pesticides, TRPH
or TPH-GRO was detected in water above the PSL in any wells. Along the north perimeter wells
located downgradient for most of the eastern area of the Site, two of the six wells show low
detections of the compound 1,1-dichloroethane, one below the PSL and one within the same
order of magnitude as the PSL. One well shows a detection of the SVOC 1,1-biphenyl right at the
PSL, and the very northeast well continues to show a low detection of vinyl chloride right at the
ESI 2019 Results Report Cardno
Airport West VCP #C092 819AR00640
11 v1, 12-10-21
PSL. None of the other northern or eastern perimeter wells indicate other impacts than these
identified. The eastern portion of the site especially in the area identified as the initial proposed
site development area (Phase I) where the waste is relatively shallow and the in cell leachate is
at a minimum has identified minimal exceedances and to the extent they have been identified,
are localized in nature and can be addressed as part of the intended waste excavation and
removal efforts to allow for that areas brownfield development.
2) Off-site contamination (down gradient from the site) is limited to the arsenic and 1,4-dioxane
discussed below with the exception of several detections, two of which exceed the PSL for 1,1,-
DCA. Off-site impact to the north specifically in the eastern portion of the site is a few slight
exceedances over the PSL identified in this area as discussed above. Off-site impact to the west
onto the Kennecott property substantially dissipate as you move away from the Landfills
western Boundary, decreasing in orders of magnitude just west of the boundary to levels below
PSLs with the exception of the arsenic and 1,4-dioxane which remain just above the PSLs at the
700- and 900-foot distance.
3) Soil gas measured in the sampling wells along the western perimeter and down gradient from
the site exceed certain screening level thresholds for residential and commercial indoor air risk
exposures. Related evaluations for identifying potential risks associated to the inhalation of
volatilized groundwater identified four compounds: benzene, chloroform, 1,1-dichloroethane
and vinyl chloride. These may pose a potential risk based on the higher concentrations identified
in the Site groundwater. These higher concentrations were typically identified within single
locations or limited areas.
4) Certain natural characteristics of the site that have now been identified over the course of these
studies may have assisted in reducing the potential for migration of contaminants off of the site.
These include a relatively slow area wide ground water gradient, a large portion of the site
underlined with a thick layer of low permeability clay including the cell bottoms and cell walls.,
an apparent upward GW gradient on the western portion of the site between the lower water
bearing zones and the shallow unconfined groundwater.

Phase 1 Area 2021
Supplemental Investigation
Report
FINAL
Airport West VCP #C092
August 10, 2022

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec DOCUMENT INFORMATION i
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
Contact Information
Cardno
1142 West 2320 South Ste. A
Salt Lake City, UT USA
Telephone: [phone]
www.cardno.com
www.stantec.com
Document Information
Prepared for NT DEVELOPMENT, LLC

1700 South 4650 West
Salt Lake City, UT 84104 USA
Project Name Phase 1 Area 2021 Supplemental
Investigation Report
Airport West VCP #C092
File Reference Airport West VCP Phase 1 Area 2021
SI Report FINAL 8-10-22.docx
Job Reference 819AR00640
Date August 10, 2022
Version Number 1.0
Effective Date January 3, 2021
Date Approved JAN 03, 2021

Author(s) David Cline, P.E.
Project Manager

Approved By Russell Hamblin
Global Client Manager
Document History
Version Effective Date Description of Revision Prepared by Reviewed by
1.0 January 3, 2021 DRAFT David Cline Joseph Hunt
2.0 March 10, 2022 DRAFT FINAL David Cline
2.1 August 3, 2022 DRAFT FINAL – PFAS update David Cline
1.0 August 10, 2022 FINAL David Cline
© Cardno. Copyright in the whole and every part of this document belongs to Cardno and may not be used, sold, transferred, copied or
reproduced in whole or in part in any manner or form or in or on any media to any person other than by agreement with Cardno.
This document is produced by Cardno solely for the benefit and use by the client in accordance with the terms of the engagement.
Cardno does not and shall not assume any responsibility or liability whatsoever to any third party arising out of any use or reliance by
any third party on the content of this document.

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec TABLE OF CONTENTS ii
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
Table of Contents
1 INTRODUCTION .................................................................................................................. 1
1.1 BACKGROUND ................................................................................................................... 1
1.1.1 Site History and Previous Work ............................................................................ 1
1.2 HYDROGEOLOGIC SETTING ............................................................................................ 6
1.3 2021 SI OBJECTIVES ......................................................................................................... 7
2 WORK TASKS ..................................................................................................................... 9
2.1 Work Plan: ........................................................................................................................... 9
2.2 Field Activities ...................................................................................................................... 9
2.2.1 Groundwater Investigation.................................................................................... 9
2.2.2 Well Survey ........................................................................................................ 11
2.2.3 Test Pit Activities ................................................................................................ 11
2.2.4 IDW Management ............................................................................................... 12
3 INVESTIGATION RESULTS SUMMARY .......................................................................... 13
3.1 Groundwater Gradient ....................................................................................................... 13
3.2 Groundwater Analytical Results ......................................................................................... 13
3.2.1 Investigation Well Groups - NTL ........................................................................ 14
3.2.2 Groundwater Analytical Results (2021 SI) ......................................................... 15
3.3 Test Pit Results .................................................................................................................. 17
3.3.1 Soil/Waste Vapor Gas Monitoring ...................................................................... 17
3.3.2 Field Olfactometer Measurement ....................................................................... 18
3.3.3 Test Pit Field Observations ................................................................................ 18
3.3.4 Analytical Testing Results .................................................................................. 18
4 QUALITY ASSURANCE/QUALITY CONTROL ................................................................ 19
5 CONCLUSIONS ................................................................................................................. 22
5.1 Groundwater Considerations ............................................................................................. 22
5.2 Leachate Considerations ................................................................................................... 23
5.3 Soil Considerations ............................................................................................................ 23
6 REFERENCES ................................................................................................................... 24
Appendices
Appendix A Field Documents
Appendix B Laboratory Reports
Appendix C Photographs

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec TABLE OF CONTENTS iii
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
Tables
Table 1 Groundwater Elevation Data
Table 2 Phase 1 Area Analyte List
Table 3 Vapor Gas - Test Pits
Table 4 Groundwater Well Analytical Exceedance Data (Metals, VOCs, SVOCs and TDS)
Table 5 Groundwater Well Analytical Exceedance Data (PFAS)
Table 6 Test Pit Leachate Analytical Exceedance Data (PFAS)
Table 7 Test Pit Solids Analytical Exceedance Data (PFAS)
Table 8 Test Pit Analytical Exceedance Data (Metals, VOCs and SVOCs)
Figures
Figure 1 Regional Topo Map (Cover Page)
Figure 2 Site Vicinity Map
Figure 3 Site Aerial Map
Figure 4 Groundwater Elevation Map
Figure 5 VOC Exceedance Map
Figure 6 SVOC Exceedance Map
Figure 7 Metals Exceedance Map
Figure 8 PFAS Exceedance Map
Figure 9 TDS Map
Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec ACRONYMS iv
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
Acronyms
As = arsenic
AWAL = American West Analytical Laboratories
Ba = barium
BTEX = benzene, toluene, ethylbenzene, and xylenes
CLP = Contract Laboratory Program. The program set up by the USEPA to regulate Superfund
(CERCLA) activities including sampling, analysis, and data validation.
COC = Chemical of Concern
ChOC= Chain of Custody
DCB = dichlorobenzene
DCA = dichloroethane
DERR = Division of Environmental Response and Remediation
DO = dissolved oxygen
DQO = Data Quality Objectives. Qualitative and quantitative statements derived from the DQO
process that clarify study technical and quality objectives, define the appropriate type of
data, and specify tolerable levels of potential decision errors that will be used as the
basis for establishing the quality and quantity of data needed to support decisions.
DRO = diesel range organics
DUP = Duplicate
EB = equipment rinsate blank
EDB = ethylene dibromide. AWAL uses the IUPAC name “Dibromoethane”.
EGP = direct push technology Well (Former Epperson Property)
EGW = Groundwater Well (Former Epperson Property)
ESI = Expanded Subsurface Investigation
ESVP = Soil Vapor Probe (Former Epperson Property)
FID = Flame Ionization Detector
HASP = Health and Safety Plan
GC = Gas Chromatograph or Gas Chromatography
GC/MS = Gas Chromatography/Mass Spectrometry
GFAA = Graphite Furnace Atomic Absorption
GP = direct-push technology Well
GRO = gasoline range organics
GW = Groundwater
HQ = Hazard Quotient
ICP = Inductively Coupled Plasma. An atomic emission instrument for the analysis of metals.
ICP/MS = Inductively Coupled Plasma/Mass Spectrometry
ISL = Initial Screening Level
IUPAC = International Union of Pure and Applied Chemistry
LCS = Laboratory Control Sample. A laboratory generated blank sample spiked with target
analytes.
LEL = Lower Explosive Limit
LUST = Leaking Underground Storage Tank
MBLK = Method Blank
MCL = Maximum Contaminant Level
MDL = Method Detection Limit. A calculated limit determined by analyzing at least 7 replicate
samples of the same concentration (2-5 times the expected MDL). The standard
deviation is determined and multiplied by the student T value for the number of samples
analyzed.
mg/L = milligrams per Liter
MS = Matrix Spike. A sample spiked with a known concentration of target analyte(s) used for
accuracy information.

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MSD = Matrix Spike Duplicate. A second spiked sample used for both accuracy and precision
information when compared to the MS.
MTBE = methyl tert-butyl ether
MW = Monitoring Well
NELAC = National Environmental Laboratory Accreditation Committee
N/S = North to South
NTL = North Temple Landfill
NW = Northwest
ORP = Oxidation/Reduction Potential
PAH = Polynuclear Aromatic Hydrocarbons
PID = Photoionization Detector
PNA = Polynuclear Aromatic
PP = Priority Pollutants
PPMV = Parts Per Million Volume
PQL = Practical Quantitation Limit. Usually a factor of approximately 3-5 times the laboratory
MDL to better simulate a real sample matrix since the MDL is determined in a deionized
water matrix.
PSL = Project Screening Level
PZ = Piezometer
QA/QC = Quality Assurance/Quality Control
QAPP = Quality Assurance Project Plan. A formal document describing in comprehensive detail
the necessary QA, QC, and other technical activities that must be implemented to
ensure the results of the work performed will satisfy the stated performance criteria.
RCRA = Resource Conservation and Recovery Act
RSL = Regional Screening Level
SAP = Sampling and Analysis Plan
SDWA = Safe Drinking Water Act. Includes public and private drinking water. References is 40
CFR Parts 141 and 143.
SI = Subsurface Investigation
SIM = Selective Ion Monitoring
SOP = Standard Operating Procedure. A written document that details the method for an
operation, analysis, or action with thoroughly prescribed techniques and steps, and that
is officially approved as the method for performing certain routine or repetitive tasks.
SW = Southwest
Surrogates = Surrogate compounds are substances normally not found in nature that are intentionally
added at a known concentration and a recovery in percent is calculated.
SVOC = Semi Volatile Organic Compound
TAT = Turnaround Time. The time from sample receipt until final data is transmitted.
TB = Trip Blank
TCE = trichloroethylene
TCMA trichloromethane (Chloroform)
TDS = Total Dissolved Solids
TO = Toxic Organics
TOC = Top of Casing
TPH = Total Petroleum Hydrocarbons
TRPH = Total Recoverable Petroleum Hydrocarbons
TTO = Total Toxic Organics (Priority Pollutant List of Organics including volatiles, semi-
volatiles, and pesticides/PCBs).
µg/L = micrograms per Liter
USEPA = United States Environmental Protection Agency
LUST = Leaking Underground Storage Tank
VC = vinyl chloride
VCP = Voluntary Cleanup Program

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VISL = Vapor Intrusion Screening Level
VOA = Volatile Organic Analysis
VOC = Volatile Organic Compounds
VOX = Volatile Organic Halogens

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1 INTRODUCTION
Cardno, Inc. (Cardno) is pleased to present the following Supplemental Investigation (SI) Report to the Utah
Department of Environmental Quality-Division of Environmental Response and Remediation (DERR). The SI
was conducted at the Airport West Voluntary Cleanup Program (VCP) Phase 1 Area Development Site (Phase
I). The Phase I area is positioned in the southeast area of the former greater 770-acre North Temple Landfill
NTL (Site), located at 6500 West North Temple Frontage Road in Salt Lake City, Utah. See Figure 1 on Report
cover. This area as discussed in this SI is shown on Figure 2 Site Vicinity Map and labeled as Phase 1 Area
Development. Additional figures and Tables are attached to this report as Figures 2 through 9 and Tables 1
through 8 and are variously referenced throughout the document. Previous investigations were performed within
the Phase I area in 2018 and 2019 with results and finding presented in the following reports: (1) Ninigret’s
Supplemental Site Characterization Study dated August 2018; and (2) Cardno’s “Expanded Subsurface
Investigation – 2019 (ESI) Report – DRAFT Final” dated December 10, 2021.
The SI outlined in this Report is intended to supplement existing data and information for the purpose of refining
remedial methods and designs to be implemented within the initial phase of the greater NTL Site remediation.
The objectives of the SI are to:
augment previous groundwater data collected within and adjacent to the Phase I area.
provide additional analytical and depth of waste data on the buried MSW within Phase I and.
collect additional groundwater and soil data from newly installed wells for the area beneath a proposed
future waste repository.
The analytical data for the Phase 1 area is derived from both the new and existing monitoring wells and
excavated test pits within the waste cells. SI waste samples collected from the test pits included leachate, soil
and ambient air gas vapor.
This Report summarizes field activities; laboratory analyses; provides a comparison to the relevant preliminary
screening levels (PSLs); summarizes quality assurance benchmarks, provides graphic representation of the
data, and discusses data updates that were previously identified. The objectives of the SI will supplement the
previous site characterization efforts by providing information for the development of an appropriate permanent
GW monitoring network and to evaluate remedial designs and approaches for the development of a Remedial
Action Plan (RAP) for the consolidation of the municipal solid waste (MSW) within the waste trench cells into a
final engineered waste repository within the Phase 1 area.
1.1 BACKGROUND
Several soil and groundwater studies have been conducted since the late 1970s at the Site. Studies have been
completed by Salt Lake City Corporation (SLC), EMCON Associates, Bingham Engineering, Utah Department of
Health, United States Environmental Protection Agency (USEPA), URS Inc., Salt Lake County (SLCo) Health,
Bingham Environmental, Montgomery Watson, UTEX Environmental, Camp Dresser and McKee Inc. (CDM) and
others. During the recent and current VCP, Ninigret and Cardno Inc. have conducted site characterization and
subsurface investigations.
The data collected during this SI will supplement previously collected characterization data.
1.1.1 Site History and Previous Work
The SI was structured to generate additional data on the Phase I area of the Site as well as to collect new data
along a future proposed railroad alignment extending west across the Site. Figure 1 shows the regional
topography with the location of the Airport West VCP Site. Figure 2 identifies the Phase I area inclusive of the
new repository with area topography, and Figure 3 shows the aerial imagery of Phase I within the area identified
as the Airport West VCP NTL Site.

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The Phase I study area, as set forth in the Work Plan for this SI, occupies approximately 175 acres of which 45
acres (that area south of the Brighton Canal) does not contain waste cells. The waste within the 130 acres of
Phase I is planned to be excavated and reconsolidated into an on-site repository located within the west area of
the Phase 1 area. This repository will incorporate the existing Bonneville Pile and will be subsequently
considered part of Phase I and included in the legal description for Phase I RAP. This Bonneville Pile contains
the area of the former NTL-East landfill (or Bonneville) waste. The NTL-East underwent an approved waste
removal and consolidation effort with UDEQ, where the waste from the NTL-East landfill was relocated to the
NTL Site in an area located in the south-central area on the overall NTL Site referred to as the Bonneville Pile.
The location is shown on Figure 4.
As can be seen from the figures, Phase I occupies the southeast area of the former NTL Site. The NTL is a
closed municipal landfill that was operated by SLC Corporation from 1959 until 1979. The topography of the
landfill is relatively flat, with mounding and depressions due to trenching cell construction and varying landfill
practices during operation.
Soil and groundwater studies conducted at the Site have concluded that subsurface soils consist of low
permeable soils such as fine sands, silts, and clay. Geotechnical investigations conducted by Salt Lake City
Corporation, the operator of the then named North Temple Street Landfill, in 1977 and reported by EMCON in
1978, that the shallow perched groundwater in the area of the landfill flows to the north-northwest at an
estimated velocity of 1 to 10 feet per year beneath the Site and regionally. The groundwater gradient was
estimated in these studies to be one foot per mile. Figure 4 shows the greater Airport West VCP Study Area
with the types and locations of the monitoring points. The September 2021 Phase 1 groundwater elevation
contours are shown on Figure 4.
Based on historical information available for the former landfill and infield observations from test pits and soil
borings, the maximum depth of waste buried at the Site ranges from 4 to 20 feet below ground surface (bgs)
(Site Inspection Prioritization, North Temple Landfill, November 30, 1994, URS, Section 3.3, and Former North
Temple Landfill Supplemental Characterization Report, March 23, 2010, CDM, Section 1.4.3), and Ninigret’s
Supplemental Site Characterization Study dated August 2018.
In presenting the analytical results of SI, the United States Environmental Protection Agency (USEPA) Maximum
Contaminant Levels (MCLs) for drinking water have been utilized as the groundwater PSLs for the Site. If an
USEPA MCL did not exist for a chemical constituent, DERR Initial Screening Levels (ISLs) and USEPA Regional
Screening Levels (RSL) for tap water was used as the GW PSL. USEPA RSL for industrial soil have been used
for soil PSLs for the Site.
In January 2018 a supplemental characterization of the Site was performed by Ninigret. Groundwater sampling
was performed within the existing Site perimeter upgradient and downgradient wells. Four wells (NTL-GW02,
NTL-GW04; NTL-GW06 and NTL-GW09) and two newly installed nested sets of both shallow and deep cross
gradient and upgradient wells (NTL-P7S, NTL-P8S, NTL-P7D and NTL-P8D) from the Phase 1 area were
included in the 2018 sampling event. Results from the downgradient shallow wells reported exceedances of the
MCL for dissolved arsenic and the EPA RSL for the volatile organic compound (VOC) 1,4-dioxane in
groundwater.
Of the five interior wells within the Phase 1 area sampled in the 2019 ESI, (NTL-GP (63, 65-68), all five wells
exceeded the MCL for arsenic, with two wells exceeding the RSL for 1,4-Dioxane.
Three of the upgradient wells were sampled in 2019 (NTL-GW02; NTL-GW09 and NTL-P8S). No wells in those
sampled in 2019 exceeded PSLs for EPA Resource Conservation and Recovery Act (RCRA) 8 metals:
VOCs/Total Petroleum Hydrocarbons (TPH) for gasoline recoverable organics (GRO) and Total Dissolved Solids
(TDS).
Four wells along the NTL perimeter (Northeast Wells), downgradient to the Phase 1 area were sampled in 2019
(NTL-GW06; NTL-P7S; NTL-GW13; and NTL-GP69). The PSL for TDS was exceeded in all four wells, ranging
between 4,750 up to 24,100 mg/L in NTL-GW13. The average TDS concentration is 11,138 mg/L. Dissolved
arsenic was exceeded in three of the four wells, ranging between 0.0159 up to 0.671 mg/L in NTL-P7S. NTL-

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P7S is located along the eastern cross gradient boundary. The area immediately east is the Bonneville Center
commercial development. The relocated waste from the Bonneville Center was placed in a new waste
impoundment, covered with an engineered soil cover, with design slopes and drainage controls to stabilize the
cover for the reduction of potential infiltration through the relocated waste. This waste is identified as the
Bonneville Pile.
The average arsenic concentration in 2019 of the Phase 1 well group was reported as 0.254 mg/L. This is the
third highest average arsenic concentration within all the 2019 ESI well groups. The new well NTL-GP69 (3.99
µg/L) slightly exceeded the PSL 0.83 µg/L for the Semi-Volatile Organic Compound (SVOC) 1,1-Biphenyl. None
of the existing Site Northeast wells reported a detection of 1,1-Biphenyl in the 2018 samples and were therefore
not re-sampled in 2019 for SVOCs. No pesticides were detected in NTL-GW06 and NTL-GP69, the two wells
sampled for pesticides. The VOCs 1,1-DCA (PSL 2.8 µg/L) and 1,4-Dioxane (0.46 µg/L) exceeded their PSLs in
the new 2019 Site well NTL-GP69. 1,4-Dioxane and VC (2 µg/L) exceeded their PSLs in the downgradient
perimeter Site well NTL-GW06. VC has historically been detected in NTL-GW06 at low levels. These
compounds were not detected in the other downgradient Northeast Site wells. SVOCs including 1,1-Biphenyl
were detected at low concentrations above their PSL in the interior 2019 samples within the Phase 1 area Site
wells. 1,4-Dioxane was detected above the PSL in the interior 2019 Phase 1 well samples.
There were six new wells installed in the 2019 ESI as NTL-GP63 through NTL-GP68 within the Phase 1 area.
These Phase 1 area interior site wells are located in the north half of the Phase 1 area. NTL-GP64 was installed
in a location approximately 1,500 feet to the east of the planned location and only 300 feet north of NTL-GP68.
NTL-GP64 was not sampled. The adjacent well NTL-GP68 was sampled.

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The PSL for TDS (2,200 mg/L) was exceeded in all five Phase 1 2019 sampled wells, ranging between 5,700 up
to 21,800 mg/L in NTL-GW65. Four of the five wells in the Phase 1 interior area exceeded the dissolved arsenic
PSL of 0.01 mg/L, ranging between 0.0147 up to 0.310 mg/L in NTL-GP65. The average arsenic concentration
is 0.150 mg/L. Lead (PSL 0.015 mg/L) was slightly exceeded in NTL-GP63 (0.0238 mg/L). Three of the five
wells exceeded the TPH-Diesel Range Organics (DRO) PSL of 1 mg/L, ranging between 1.16 up to 2.27 mg/L in
NTL-GP63. Two of the five wells exceeded the 1,4-dioxane PSL of 0.46 µg/L, ranging between 24 up to 207 in
NTL-GP66. Three SVOCs were exceeded within the three wells NTL-GP(65-67), slightly exceeding the PSL for
the1,1-Biphenyl (3.9 µg/L) ranging between 3.99 up to 5.44 in NTL-GP67; Bis(2-ethylhexyl)phthalate and 1-
Methylnapthalene, both slightly above the PSLs 6.5 and 1.86 µg/L respectively in NTL-GP63. The pesticide 4,4-
DDE was detected in NTL-GP67 (0.0119 µg/L) below the PSL of 0.046 µg/L. The pesticide endrin was detected
in NTL-GP66 (0.00618 µg/L) below the PSL of 2 µg/L. SVOCs detected below their PSLs included
acenapthalene, caprolactam, flourene, indene, naphthalene and phenanthrene. VOCs detected below their
PSLs included 1,1-DCA, 1,4-DCB, acetone, benzene, cis-1,2-dichloroethene and methylcyclohexane.
1.2 HYDROGEOLOGIC SETTING
Previous reports for the NTL Site, including the USEPA Site Inspection Prioritization (SIP) report for the Site
(USEPA/URS Section 3 1994), summarize the local hydrogeology by describing groundwater beneath the landfill
complex in two distinct units: a shallow, unconfined aquifer, generally called the Shallow Aquifer, and a confined
artesian aquifer commonly referred to as the Principal Aquifer. The Shallow Aquifer overlies a bed of low
permeable material, which confines the water in the Principal Aquifer. The Shallow Aquifer is comprised of clay,
silt and fine sand and exhibits relatively low permeability. The thickness of the shallow aquifer is somewhat
variable, but its maximum thickness is estimated at 50 feet (SIP, North Temple Landfill, November 30, 1994,
URS, Section 3.5. The Shallow Aquifer receives recharge via upward flow from the Principal Aquifer and
infiltration from local precipitation. A reversal in this upward flow could occur if high-volume pumping of the
Principal Aquifer were to occur, such as use of municipal wells (SIP, North Temple Landfill, November 30, 1994,
URS, Section 3.5). However, this reversal is not likely to be in effect near the Site, because according to URS
(SIP, North Temple Landfill, November 30, 1994, URS, Section 3.5.), there are no municipal wells located within
the four-mile radius of the NTL site.
In a 1989 Analytical Results Report (ARR) published by UDEQ, regarding site investigation results for the NTL, it
was reported “The groundwater data and hydrogeological data indicate two important points, [the first being] well
GW07, which is the deep well of a well nest with GW05, has a higher potentiometric surface than GW05.
Therefore, the vertical gradient is upward at the site in the shallow aquifer.” Utah Department of Environmental
Quality (UDEQ - formerly Department of Health, Division of Environmental Health, Bureau of SHW), Analytical
Results Report, North Temple Landfills, 1989 (Section III, Part B Groundwater Samples, 2nd paragraph).
The static groundwater elevations measured in the 2018 Ninigret Supplemental Site Characterization, deeper
wells in the western portion of the site were again higher than those measured in the adjacent paired shallow
wells consistent with the reported NTL SIP and UDEQ ARR, further supporting the upward gradient conclusion.
The general direction of groundwater movement for the Site has historically been reported as being to the north-
northwest. The quality of the water in this shallow aquifer is poor. Utilization of the shallow aquifer is limited due
to its clayey nature, poor yield, and high salinity content. The depth to the groundwater as measured in
monitoring wells during the past 20 years at the Airport West VCP Site has ranged from 4 to 11 feet bgs
(Preliminary Assessment (PA), North Temple Landfill, Utah Division of Solid and Hazardous Waste, March 26,
1987, and ERM Groundwater Monitoring Report, May 2012 Sampling Event, September 18, 2012, Table 1)
depending on seasonal groundwater fluctuations. Generally, the depth to groundwater in the Site wells range
from 5 to 11 feet bgs in the late summer and fall months (August through October) and from 4 to 7 feet bgs
during late spring months associated with spring runoff (May-early June).
The perimeter wells along the northern boundary of the Airport West NTL Site ranged between 1.4 and 3.2 ft.
bgs. The wells along the southern and eastern areas of the Site ranged between 0.6 and 5 ft. bgs.

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The monthly published precipitation total for SLC International Airport for April 2019 is 3.45 inches. The average
monthly total precipitation for this station is 1.99 inches. The water year beginning in October 2018 through
October 2019 is approximately 130% of the Wasatch Front average for water years between 1981 and 2010.
During the September 2021 SI depth to GW readings, the levels ranged between 3.4 to 8.0 feet bgs within the
shallow new and existing monitoring well locations, throughout the Site Area. See the attached Table 1 -
Groundwater Elevation Data. This compares to the previous fall levels measured in October 2019 within the
existing locations, where the levels ranged between 1.8 to 7.2 bgs. It is noted the average difference between
the 2019 spring and fall bgs readings is approximately 3 feet. This compares to the historical bgs range
generally reported as being approximately within 2.5 feet, with levels higher in the spring. This could indicate a
higher recharge to the underlying groundwater due to the higher spring runoff in the larger canals through and
near the landfill.
The water levels within the nested shallow and deep NTL-P (1-8) wells, indicate an upward pressure generally
along the western perimeter NTL-P(1-4) wells, located in the lower playa areas west of the landfill (with the
exception for the level in NTL-P3S which was slightly higher that the depth in the nested NTL-P4D deeper well).
The nested wells, NTL-P(5-8) located along the north-west (NTL-P5S/P6S), east (NTL-P7S) boundary, and the
southeast area (NTL-P8S) indicate a deeper bgs water level in the deeper aquifer compared to the shallow
aquifer. These eight nested pairs will provide additional data across seasonal fluctuations which will bring
greater understanding to the interaction of the upper and lower water bearing zones.
The shallow, unconfined aquifer separated from a lower confined artesian aquifer with an overall upward flow
would support the argument that a confining layer exists between the two units. Existence of such a confining
layer or aquitard would likely reduce the potential for downward migration of contaminants beneath the Site,
(unless, as noted above, high-volume pumping of the principal aquifer was to occur).
The Site is predominately buried MSW with the exception of the area south of the West Branch Brighton
Diversion which runs east to west until approximately where the I-80 West exit for 7200 W begins and the
frontage road approaches the intersection of 7200 W and the Frontage Road. At this point the Diversion ditch
turns north-west. West of the area of the 7200 W exit, MSW is buried within the areas north and south of the
ditch. The Diversion has been used to convey irrigation and flood control runoff to the Brighton and Northpoint
canals north of the Site. As part of the development of the Site, the section of the West Branch Diversion will be
removed from crossing through the Site.
The Little Goggin Drain runs along the eastern boundary of the Site. The North Point Drain runs along the
northern boundary of the Airport West VCP Site. A local drainage ditch runs along the frontage road on the
Southern boundary of the Site. The drains and ditches are smaller diversion and drains to the larger canals
which convey flood and irrigations waters to the areas north of the Site. Where samples have over the years
periodically been collected from these surface drains and ditches, it is not clear any interaction between these
surface waters and the underlying groundwater beneath the Site exists.
The Phase 1 Area development plan anticipates the consolidation of the existing MSW into a repository
identified as open space following its completion. A bike trail is proposed to run along the southern boundary of
the Site along the Frontage Road. A narrow buffer zone between the bike trail and the development is identified
as open space. Neither of these open space areas are considered to be ecological or sensitive environments.
1.3 2021 SI OBJECTIVES
This SI consisted of a subsurface groundwater, soil/waste and leachate investigation designed to collect
additional data on buried waste and groundwater to further delineate conditions on the Site, for the purposes of
characterizing the extent of the impacts due to the former landfill operations, specifically in the Phase 1 area;
provide additional data to allow for the evaluation of remedial design approaches and methods, and; to provide
additional data to allow for the development of an appropriate permanent GW Monitoring Network as part of the
future redevelopment of the Site. The remedial designs including the anticipated excavation and consolidation
of waste into a new repository will be presented in detail in subsequent RAP that will be submitted to UDEQ and
will provide an opportunity for public comment. It should be noted that the project proponent has been actively

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communicating with local community groups and elected officials, providing a general overview of the findings
contained in this report and previous investigations, summarizing the anticipated regulatory process (including
public comment) and providing an identifying current conceptual plan for the site’s future development.
These specific items or areas of focus on this SI are identified as follows and are intended to provide:
Additional data set of groundwater quality constituents from the initial list of organic and inorganic contaminants
from the 2012 upgradient wells NTL-GW(09-10); 2018 Site well NTL-P7S; 2019
NTL Site, Phase 1 area and downgradient Wells (48,63,65-69) and new 2021 proposed Phase 1 repository wells
GW-RR(13,18 and 19), were collected for evaluation of contaminants for remedial design of the Site remedial
actions to be proposed.
New soil/waste and leachate sample data within the NTL Site and Phase 1 area landfill cells, collected from 16
test pits TP-RR (1-16) to evaluate MSW source areas for proposed remedial actions.
Water and soil Samples were analyzed for RCRA 8 metals; VOCs; SVOCs; TRPH; TPH-DRO; TPH-GRO;
hexavalent chromium; TDS; and per-and polyfluoroalkyl substances (PFAS).
The field work was performed by following a DERR approved August 19, 2021, Sampling and Analysis Plan
(SAP). The SAP included standard operating procedures (SOPs), Method Detection Limits (MDLs) as provided
in the November 28, 2017, North Temple Landfill Supplemental Field Investigation; August 29, 2017, NTL
Epperson Revised ESI Scope of Work (SOW). Additionally, SOPs found in Appendix B of the August 11, 2015,
SI Work Plan (WP), and the 2008 Quality Assurance Project Plan (QAPP) found in Appendix A to the
Supplemental Landfill Characterization-Sampling Analysis Plan for the North Temple Landfill, dated August 14,
2008 (2008 QAPP) are referenced. Amendments to the SI Work Plan are included in Attachment 2 – Standard
Operating Procedures of the WP, to provide procedures for soil vapor sampling and analysis. SOPs and
sampling and analysis procedures as agreed upon with the DERR for the Site groundwater monitoring are
included in Attachment 2 of the WP. SOPs were amended to include the sampling for PFAS compounds.

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2 WORK TASKS
2.1 Work Plan:
The 2021 SAP approved by DERR was utilized for the work reported in this Report. A site specific Cardno
Health and Safety Plan (HASP) was prepared for daily tailgate meetings involving onsite personnel. SAP Table
2 – Groundwater Sampling Matrix and SAP Table 4 – Laboratory MDL and PQL values were distributed to field
and laboratory personnel. The SAP identified SOPs were followed for the execution on the field activities. Field
and laboratory QA/QC samples identified in the SAP were followed for sample collection, laboratory analysis and
data evaluation.
Deviations to the SAP encountered during implementation are listed as:
A duplicate sample was identified in the SAP for NTL-GP65. This was anticipated as a split sample by the
agency. No split sample was requested.
A duplicate sample was identified in the SAP for the soil/solid waste samples. This was anticipated as a split
sample by the agency. No split sample was requested.
A total of three trip blanks were identified in the SAP. A total of six were collected due to the additional days
collecting the GW samples with VOCs.
2.2 Field Activities
2.2.1 Groundwater Investigation
2.2.1.1 Groundwater Monitoring Well Installation
Direct-push drilling technology (DPT) was performed by Direct Push Services, a licensed well driller of Utah.
Because DPT was used, minimal amounts of soil waste were generated. Work was performed in September
2021.
Installation of 3 temporary 2-inch slotted PVC monitoring wells (MW) installed within DPT drill holes (DH), (GW-
RR13W, GW-RR18W, and GW-RR19W), along the western boundary of the Phase 1 area and proposed future
Rail Line Alignment (Site) in the proposed Repository #1 area.
All temporary MW locations were installed with 15 feet of sand filter screen.
Each of the 3 new temporary monitoring GW well locations included a 3-foot PVC stick up and slip cap in order
to assist with locating the wells in the future. The wells were constructed using 2-inch O.D., Schedule 40 PVC
blank casing and 15-foot-long slotted screen. The depth to groundwater during drilling was estimated to be
approximately 6 to 10 feet bgs beneath the Site. The well drill holes (DH) were drilled to an approximate depth
of 20 feet bgs with the well screen intervals being determined in the field at the time of drilling based on the
encountered depth to groundwater. The DH diameter for the installation of the 2-inch diameter monitoring wells
was between 3 and 3.5 inches which was sufficient for the well installations, development, and sampling in this
investigation and also complied with the Utah well and drilling guidelines for well installations less than 30 feet
bgs.
The results of the 3 groundwater samples in the proposed Repository #1 was evaluated to further delineate
conditions in the Proposed Repository #1 area. This information is provided to allow for the evaluation of
remedial options and design plans.

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2.2.1.2 Monitoring Well Purging
Beginning August 29, 2021, and continuing through September 21, 2021, the monitoring wells were purged prior
to sampling. Purging of the new wells occurred a minimum of 24 hours following their installation and consisted
of the following:
Purging of 3 new Monitoring wells, GW-RR13, GW-RR18, and GW-RR19.
Purging of 9 existing monitoring wells NTL-P7S, NTL-GW(9, 10), NTL-GP-(48, 63, 65-67, 69) wells.
Prior to the collection of groundwater samples from each of the new monitoring wells, as well as the existing
wells, wells were purged using low-flow purging and sampling methods with a peristaltic pump, following
procedures outlined in the August 2021 SAP for Supplemental Investigation for Phase 1 Area Development
Airport West VCP Site #C092 (Formerly the North Temple Landfill-NTL) groundwater investigation. The following
procedures were followed:
Prior to purging and sampling, monitoring wells were measured to determine the static groundwater level, total
depth and volume of groundwater in the well before any wells purged and sampled. An electronic water level
indicator, accurate to 0.01 foot, was used to measure static groundwater levels relative to the top of the PVC well
casing. The total well depth was then measured by lowering the water level indicator until the bottom of the well can
be felt. The well casing volume was calculated based on measurements of total depth, depth to water, and the
inside diameter of the well casing. All measurements and calculations were recorded in the field data sheets and
provided in Appendix A.
Purging and groundwater sample collection was completed using low-flow (minimal drawdown) purging and
sampling methodology. The low-flow methodology was used in all locations to ensure that the water sampled is
representative of the surrounding formation, while minimizing the generation of excess purge water. The field
sampling technician used a new pair of disposable latex gloves before handling all downhole equipment or materials
used for purging or sampling. Low flow purging of groundwater in each monitoring well was accomplished prior to
sampling using a peristaltic pump with dedicated or disposable tubing. As recommended by EPA guidance (U.S.
EPA, 1996, Low-Flow [Minimal Drawdown] Ground-Water Sampling Procedures, EPA/540/S- 59/504), the pump
intake was placed in the middle or slightly above the middle of the saturated screened interval. Also, in accordance
with EPA guidance, the purge flow rate was adjusted between 100 ml/min and 500 ml/min to maintain less than 0.1
meters (0.3 feet) of drawdown. The depth to groundwater was measured at intervals of at least three minutes during
purging to monitor drawdown. The flow rate was adjusted as necessary.
Monitoring wells were purged of stagnant groundwater to draw in water representative of the surrounding formation.
Low-flow purging continued until groundwater field parameters stabilized, or until a maximum of three casing
volumes had been removed. Groundwater field parameters included pH, temperature, specific conductivity,
dissolved oxygen (DO), and oxidation/reduction potential (ORP). Groundwater field parameters were measured at
intervals of at least 5 minutes during the purging process using a multi-parameter closed flow- through cell. Each
instrument used for measuring field parameters was calibrated in accordance with the manufacturer’s specifications.
Groundwater field parameters were recorded and checked to verify that these parameters had stabilized, ensuring
that representative formation water was entering the well. Groundwater was considered stable and representative
when three consecutive measurements meet the following requirements for each item’s previous respective
reading: pH is within 0.2 units, temperature and DO were within 10%, ORP is within +/- 10 millivolts, and specific
conductivity was within 5%.
If a well was purged dry before field parameters stabilized, purging ceased, and the well was allowed to recover. In
this case, as soon as there was a sufficient volume of water in the well, samples were collected for laboratory
analysis. If there was not sufficient volume in the well for sampling within 12 to 72 hours after purging, the well will
be assumed dry, and no sample was collected during that sampling event.
2.2.1.3 Groundwater/Leachate Sample Collection
Table 2 lists the sample and the analytes collected at each of the well locations. Beginning August 30, 2021, and
continuing through September 22, 2021, the monitoring wells which were planned for the collection of
groundwater samples were sampled between 24 and 72 hours following purging of each of the new monitoring
wells, as follows.

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• Collection of 10 Leachate samples from Test Pits
• Collection of 3 new groundwater samples from Monitoring wells, GW-RR-13, GW-RR-18, and GW-RR-19.
• Collection of 9 existing groundwater samples from monitoring wells NTL-P7S, NTL-GW-(9, 10), NTL-GP-(48, 63, 65-
67, 69) wells.
• Following purging and stabilization of field parameters, the flow-through cell was disconnected to allow collection of
groundwater samples from the discharge tubing of the peristaltic pump directly into the appropriate containers
provided by the laboratory. The pumping flow rate during sample collection was maintained at the same flow rate
used during purging. Samples that were to be submitted for metals analysis were field filtered using a disposable
0.45-micron filter.
Groundwater samples were collected from the following groundwater wells for analysis as identified below of,
RCRA 8 Metals by EPA Method 6010D/6020B and 7470A/7471A; Hexavalent Chromium by EPA Method
7196A; VOCs and TPH-GRO by EPA Method 8260C; HEM-SGT Total Recoverable Petroleum Hydrocarbons
(TRPH) by EPA 1664; SVOCs & TPH-DRO by EPA Method 8270D (Selective Ionization Mode -SIM); PFAS by
EPA Method 537 MOD; TDS; Samples for RCRA 8 Metals including arsenic, barium, cadmium, chromium, lead,
mercury, selenium and silver by EPA Method 6010B/6020B and 7470A/7471A. For sample locations with
reported EPA Method 8260C Full Scan levels of 1,4 Dioxane below the Laboratory Reporting Limit (Practical
Quantitation Limit), EPA Method 8260C (SIMS) was also performed to achieve reporting levels at the lower PSL.
Groundwater samples were collected and held for Toxicity Characterization Leaching Procedure (TCLP)
analysis pending laboratory analysis. After receiving total laboratory analysis, it was determined that TCLPs
were not necessary.
Quality assurance-quality control (QA/QC) samples were collected and included duplicate samples; equipment
or rinsate samples, field blank samples, Matrix Spike/Matrix Spike Duplicate (MS/MSD), and VOC trip blank
samples. The duplicates were collected at a rate of 1 for every ten samples. Three rinsate or equipment blanks
were collected for the project where decontamination of equipment was performed. The three MS/MSD samples
were submitted at a rate of 1 for every sample set submitted. The VOC trip blanks were collected for each cooler
containing samples for VOC analysis.
2.2.2 Well Survey
GPS data was prepared and reported as latitude and longitude for the new well locations. Project well locations
were reported using a GPS on September 22, 2021. Based on ground surface level and stick-up height were
used to determine the top-of-casing (TOC) level for the 3 new wells.
As part of this SI, Cardno also recorded depth-to-groundwater measurements as collected for a Phase 1 area
groundwater potentiometric contouring map. This was performed within a 36-hour period with no measurable
precipitation and following no less than a 5-day period from removal of water from the wells. Table 1
summarizes the groundwater elevation data. Measurements for depth to GW in the wells was recorded between
August 30 and September 2, 2021, and on September 22, 2021.
2.2.3 Test Pit Activities
Test pit excavation activities were performed on September 2-7, 2021. The test pits (TP) were excavated to an
approximate depth of 3.5 to 12 feet bgs with dimensions approximately 11 to 19 feet long and approximately 4
feet wide. Groundwater was encountered and recorded between approximately 4 to 11 feet bgs beneath the
surface and MSW was observed within the test pits ranging from 1 to 12 feet bgs. The MSW profiles ranged
from 2 to 9 feet in depth.
Specific test pit activities included the following:
Excavation of a total of sixteen (16) test pits, TP-RR(1-16) within the boundary of the NTL Site for this SI.
Excavation of eight (8) of the total sixteen (16) test pits, TP-RR(9-16) from within the Phase 1 area.
A total of eight (8) Cone Penetrometer Test locations were completed along the length of the proposed rail line.
The results and locations are included the Remedial Action Plan prepared for the Phase 1 Area.

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Figure 4 shows the locations of all test pits. Each of the 16 test pit locations were recorded for GPS
coordinates. Previous characterization studies including the use of test pits have occurred within the Phase 1
Area to evaluate the waste profiles.
2.2.3.1 Test Pit Activities Soil Sample
Soil sampling was performed during test pit excavation activities. Table 2 lists the test pits and the analytes
collected at each of the test pit locations. The following activities were conducted:
Collection of soil samples from 10 of the 16 test pits.
Ten soil samples were submitted for analysis of the listed parameters in Table 2.
The soil samples were collected from the soil/waste interface at the bottom of the waste profiles.
Soil samples were collected during the test pit excavations for the following analyses:
RCRA 8 Metals including arsenic, barium, cadmium, chromium, lead, mercury, selenium and silver by EPA
Methods 6010D/6020B and 7470A/7471A; VOCs and TPH-GRO by EPA Method 8260C, TPH- DRO and
SVOCs by EPA Method 8270D (Selective Ionization Mode -SIM); HEM-SGT TRPH by EPA Method 1664B;
hexavalent chromium by EPA Method SW-846 7196A and PFAS by EPA Method 537 Mod.
QA/QC samples were collected which included VOC trip blank samples and temperature blanks. The VOC trip
and temperature blanks were collected for each cooler containing samples for VOC and PFAS analyses,
respectively.
2.2.4 IDW Management
Because DPT was used, minimal soil waste was generated during drilling. The investigation-derived waste
(IDW) materials including minor amounts of decontamination fluids, and groundwater purge well development
water was contained in Utah Department of Transportation (UDOT)-approved 35-gallon drums. These drums
were labeled and stored temporarily on the Site. Following a review of the laboratory analytical data, the water
was disposed as investigative derived waste by discharging with-in depressed areas within the landfill cells
upgradient from impacted wells with similar COC, during the first week in October 2021.

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3 INVESTIGATION RESULTS SUMMARY
3.1 Groundwater Gradient
As part of the 2019 investigation which included the installation of the Phase 1 area monitoring wells, a
groundwater elevation survey of sampled monitoring wells was conducted. Data obtained from the top-of-casing
elevations, state plane northing and easting, along with measured water table elevations were utilized to prepare
a groundwater contour map for the site. The groundwater well coordinates and elevation data are summarized in
Table 1, while the contours are illustrated in Figure 2. Based upon the data collected, the groundwater flow
direction in the Phase 1 area of the Site is toward the North-Northwest with a gradient of approximately .0011
feet/foot measured between NTL-GW10 and NTL-GP69. The groundwater flow direction in the Phase 1 area
as measured in 2019 is towards the North with a gradient of approximately 0.0012 feet/foot measured between
NTL-P8S and NTL-GP69. The gradients along the western boundary of the NTL Site are four to six times higher
than those on the eastern area of the Site, encompassing the Phase 1 area. The direction and gradients on the
eastern area of the Site appear to be more indicative of the surrounding regional areas. The shallow lower
profile waste cells typical of the Phase 1 area are believed to have less of an impact on the underlying
groundwater gradients. Review of the data from groundwater wells surrounding the landfill indicates regional
groundwater flow is to the North.
The West Branch of the Brighton Canal crosses the NTL Site in an east to west direction in the eastern area of
the NTL Site and changes to a northwest direction, before leaving the NTL at the north-west corner of the Site.
There is an apparent mounding of higher groundwater elevations in the western area of the NTL. This area is
characterized by deeper and thicker waste cells compared to the shallow and dryer waste cells in the area of
Phase 1. Plans to relocate the Brighton Canal around the Site would eliminate any possibility for recharge of
canal water into these areas and the potential effect it may have on the direction and gradients within the Site
boundary.
3.2 Groundwater Analytical Results
As discussed in the Groundwater Gradient section above and as shown on the 2019 ESI Figure 4, Groundwater
Elevation Map – Shallow Aquifer, the characteristics of the Phase 1 area compared to the overall NTL lends
itself to being discussed as two halves: east (Phase 1) and west (remainder of NTL. These two halves can be
further distinguished into two additional areas: north and south. The east half Site is comprised of the north and
south perimeter wells along the boundary of the former NTL Site, and the interior area encompassing the
southeast area of the site identified as the Phase I area. Within the Phase 1 area the groundwater moves south
to north in a northerly direction. On the west half of the remaining NTL Site the groundwater moves west in a
west-northwesterly direction in the north half and west-southwesterly direction in the south half.
The western NTL Site is characterized by deeper and wetter MSW cells. This may be attributed to the larger
waste profiles as a result of the deeper cells and general higher topographic surface profile compared to the
lower surrounding topographic outside the landfilled areas. The groundwater is characterized as having more
detections of constituents at the highest levels throughout the NTL Site. The east area of the NTL Site in
particular the Phase 1 area is dryer, shallow waste profiles with fewer constituents detected, and at the lowest
levels throughout the NTL Site.

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3.2.1 Investigation Well Groups - NTL
A total of 70 well locations have been sampled as part of the overall characterization of the Airport West VCP for
the NTL site (2018-2019). These are grouped in the following areas and are briefly described below in proximity
to the Phase 1 area.
PH
A
S
E

1
AR
E
A
Southeast Wells –Upgradient 6 WELLS
Northeast Perimeter Wells –North and East Downgradient 5 WELLS
Phase 1 Area Wells –Interior Source 9 WELLS
SO
U
T
H
WE
S
T
Southwest NTL Site Boundary Wells –West and South Cross gradient 15 WELLS
Southwest NTL Offsite Wells West Downgradient 16 WELLS
NO
R
T
H
WE
S
T
Northwest NTL Boundary Wells –West and North Cross gradient 9 WELLS
Northwest NTL Offsite Wells –West Downgradient 14 WELLS
3.2.1.1 Phase 1 Southeast Wells (Upgradient) – 6 Wells
The Southeast wells NTL-GW01; NTL-GW02; NTL-P8; NTL-GW09; NTL-GW10 and NTL-GW11 are
hydrologically upgradient of the landfill waste cells. These wells are grouped together and are considered
upgradient wells to the underlying groundwater at the Site. During the redevelopment of the areas
encompassing several of these wells, a relocation of certain wells identified in the future groundwater monitoring
program will be determined. See Figure 4. Existing wells NTL-GW9 and NTL-GW10 from this group were re-
sampled for this current 2021 SI.
3.2.1.2 Phase 1 Northeast Boundary Wells (Perimeter and Off-site Downgradient) – 5 Wells
The Northeast wells NTL-GW04; NTL-GW06; NTL-P7; NTL-GW13; and the 2019 ESI well NTL-GP69 are
hydrologically downgradient of the Phase 1 area and located along the north and east boundary of the former
landfill. These wells are grouped together and are considered perimeter downgradient wells to the shallower
older waste cells associated with the Phase 1 area and downgradient from the Phase I area wells. See Figure
4. Wells NTL-P7S and NTL-GP69 were re-sampled for this current 2021 SI.
3.2.1.3 Phase 1 Interior Wells (Phase 1 Development Area) – 9 Wells
A group of six wells which were installed in 2019 ESI are the wells in the area described as the Phase 1 area
wells. These are NTL-GP63 through NTL-GP68 and are located in the north half of the Phase 1 area, within the
eastern area of former waste cells. Also, three new GW monitoring wells were installed and sampled during this
SI, (GW-RR13, RR18 and RR19). These were located in the general area being proposed for a new repository
waste cell for the Phase 1 area. See Figure 4. Seven of these Phase 1 area interior wells were sampled in this
SI (NTL63, 65-67) and the three new wells (GW-RR13, RR18 and RR19).
3.2.1.4 Southwest NTL Boundary Wells (Perimeter, Interior and Off-site Downgradient) – 31 Wells
The Southwest NTL wells are grouped in three sub-groups within the southwest area of the NTL Site. The first
sub-group are the perimeter wells NTL-P1, NTL-P2, NTL-GW12, NTL-PZ13, NTL-PZ14, NTL-GP58, NTL-GP61
and, NTL-GP62. The second sub-group are the 2019 interior wells located between 50 and 200 feet east of the
southern and western boundary. These nine wells are NTL-GP51 through NTL-GP57, NTL-GP59 and NTL-
GP60. The third sub-group of the Southwest NTL Site wells are the wells located within 900 feet downgradient
and offsite of the western boundary, west of the landfill, in the area currently owned by Kennecott Utah Copper.
These wells include the 200 feet west- 2015 wells (EGW5, EGW7, EGW9 and EGW13); the 500 feet west -
2017 wells (EGW19; EGW20; and, EGW21); and, the 2019 ESI wells (EGP22, EGP23, EGP(30-36) and
EGP(42-47). The 2019 ESI wells EGP30 through EGP36 are located 700 feet downgradient from the western

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boundary, west of the landfill. The 2019 ESI wells EGP42 through EGP47, are located downgradient 900 feet
from the western boundary, west of the landfill. These wells are all located west and cross gradient from the
Phase 1 area. See Figure 4.
3.2.1.5 Northwest NTL Boundary Wells (Perimeter, interior and Off-site Downgradient) – 23 Wells
The Northwest NTL Site wells are grouped into three similar sub-groups within the northwest area of the NTL
Site. The first sub-group are the perimeter wells NTL-P3, NTL-P4, NTL-P5, NTL-P6, NTL-GW14, NTL-GW15,
and NTL-PZ15. These wells are located along the western boundary of the former landfill with the exception of
NTLP5 and NTLP6 which are located along the northern boundary within the northwest area of the former
landfill. The second sub-group are the NTL Site interior perimeter wells (NTL-GP48 through NTL-GP50). These
wells are located within the interior of the landfill 200 feet east of the western boundary of the NTL Site. The third
sub-group of the Northwest wells are the western offsite wells located within the first 900 feet west and
downgradient of the former landfill in an area currently owned by NWQ, LLC. These wells include the 200 feet
west 2015 ESI wells (EGW1, EGW3 and the 2017 ESI well EGW-7; the 500 feet west 2017 ESI downgradient
wells (EGW14; EGW15; EGW16; and EGW17 (200 feet); and, the 2019 ESI wells EGP(24-29) and EGP(37-41).
The 2019 ESI wells EGP(24-29) are located 700 feet downgradient from the western boundary, west of the
landfill. The 2019 ESI wells EGP(38-41) are located downgradient 900 feet from the western boundary, west of
the landfill. These wells are all located west and cross gradient from the Phase 1 area. Northwest boundary NTL
Site well NTL-GP48 from this group was sampled during this SI. This well was included within the area of a
future proposed railroad alignment which was sampled for both soil, leachate and vapor during this SI. See
Figure 4.
3.2.2 Groundwater Analytical Results (2021 SI)
3.2.2.1 Southeast Phase 1 Wells (Upgradient) NTL-GW(09,10)
Two existing wells in the Southeast upgradient group were sampled in 2021 (NTL-GW09 and NTL-GW10). The
PSLs for dissolved arsenic (0.01 mg/L) in NTL-GW10 was exceeded (0.0581 mg/L). No other analytes were
reported exceeding their PSL. A TDS PSL for the 2019 ESI was established on an average of the upgradient
wells plus 2 * STDEV. This value equates to 2200 mg/L. The 2019 values for arsenic were comparable to the
2018 reported values, with the largest change being about equal to the PQL or laboratory reporting value of
0.002 mg/l. The 2019 ESI values for TDS were comparable to the 2018 reported values with the largest change
being around 11% decrease. Approximately a third of the 29 PFAS compounds were detected at low
concentrations below their PSL in the off-site upgradient well NTL GW 09. Four of the 29 PFAS compounds
were detected at low concentrations below their PSL in the upgradient well NTL GW 10. See Tables 4 and 5.
3.2.2.2 Northeast Boundary Well Group (NTL Perimeter Downgradient wells) NTL-P7S and NTL-
GP69
Two wells in the Northeast downgradient well group were sampled in this 2021 SI: NTL-P7S; and NTL-GP69.
The PSL for TDS (2,200 mg/L) was exceeded in both wells. Dissolved arsenic was exceeded in both wells,
NTL-P7S (0.267 mg/L) and NTL-GP69 (0.013 mg/L). No other RCRA metals exceeded their PSL. NTL-P7S is
located along the eastern boundary. The area immediately east is the Bonneville Center commercial
development. This area contained the former NTL-East landfill. The NTL-East underwent an approved waste
removal and consolidation effort with UDEQ where the waste from the NTL-East landfill was relocated to a new
covered impoundment cell in the south-central area on the Site identified as the Bonneville Pile. Elevated
arsenic in the GW beneath the NTL-East MSW was identified during the NTL-East remedial action work.
Reported detections in this SI include the VOC 1,4-dioxane exceeding the PSL (0.46 µg/L) in NTL-GP69 (298
µg/L) and in NTL-P7S (1.62 µg/L). The PSL for TDS (2,200 mg/L) was exceeded in both sampled wells, (6870
mg/L in NTL-GP69 and 4180 mg/L in NTL-P7S. No other PSLs were exceeded in NTL-P7S. The NTL northern
downgradient boundary well NTL-GP69 is reported as exceeding PSLs for two other VOCs: 1,1-DCA at 39.3
µg/L (PSL 2.8 µg/L) and VC at 3.29 µg/L (PSL 2.0 µg/L). No other PSLs were exceeded in these perimeter
downgradient wells. The PSL for the SVOC 1,1-Biphenyl was exceeded in NTL-GP69 in the 2019 ESI sampling.
The MDL is reported as 1.01 µg/L, slightly exceeded the PSL 0.83 µg/L for the SVOC 1,1-Biphenyl. None of the

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existing Northeast wells reported a detection of 1,1-Biphenyl in the 2018 samples and were therefore not re-
sampled in 2019 for SVOCs.
Seven of the 29 PFAS compounds were detected at low to moderate concentrations in the perimeter cross
gradient well NTL P7S. No PFAS compounds exceeded their PSL. Eight of the 29 PFAS compounds were
detected at low concentrations in the perimeter down gradient well NTL-GP-69. No PFAS compounds exceeded
their PSL. See Tables 4 and 5 – GW Exceedance Summary Phase 1 Area Wells and Figures 5-9.
3.2.2.3 Phase 1 Area Site Interior Wells NTL-GP(63,65-67) and GW (RR13w, RR18w and RR19w)
Seven wells (NTL-GP63, NTL-GP65 through NTL-GP67 and the three new wells in the proposed repository area
(GW RR13, RR18 and RR19) were sampled in this 2021 SI.
The PSL for TDS (2,200 mg/L) was exceeded in all seven sampled wells, ranging between 4,180 mg/L up to
33,400 mg/L in GW-RR19. Five of the wells in the Site area exceeded the dissolved arsenic PSL of 0.01 mg/L,
ranging between 0.01497 up to 0.875 mg/L in GW-RR19. Cadmium (PSL 0.005 mg/L) was exceeded in NTL-
GP65 (0.00565 mg/L), GW-RR13 (0.00679 mg/L) and GW-RR19 (0.0156 mg/L). Hexavalent chromium was
added to the analyte list in this 2021 SI. No detection of concentrations for hexavalent chromium are reported.
All of the seven wells exceeded the 1,4-dioxane PSL of 0.46 µg/L, ranging between 0.83 µg/L up to 48.4 µg/L in
NTL-GP66w. No SVOCs PSL were exceeded within the seven Site wells in this 2021 SI. In the 2019 ESI, the
Site wells, NTL-GP(65-67), reported exceeding the PSLs for 1,1-Biphenyl (0.83 µg/L) ranging between 3.99 up
to 5.44 in NTL-GP67. Bis(2-ethylhexyl) phthalate and 1-Methylnapthalene, both were reported above the PSLs
6.5 and 1.86 µg/L respectively in NTL-GP63. The pesticide 4,4-DDE was detected in NTL-GP67 (0.0119 µg/L)
below the PSL of 0.046 µg/L. The pesticide endrin was detected in NTL-GP66 (0.00618 µg/L) below the PSL of
2 µg/L. SVOCs detected below their PSLs included acenapthalene, caprolactam, flourene, indene, naphthalene
and phenanthrene. VOCs detected below their PSLs included 1,1-DCA, 1,4-DCB, acetone, benzene, cis-1,2-
dichloroethene and methylcyclohexane.
Nine of the 29 PFAS compounds were detected at low to moderate concentrations in the Phase 1 Site interior
wells NTL-GP (63,65-67). The PSL for PFOS (40 ng/L) was exceeded in NTL-GP-66 (130 ng/L). The PSL for
PFOA (60 ng/L) was exceeded in NTL-GP-63 (71 ng/L); NTL-GP-65 (70 ng/L); and NTL-GP-66 (w90 ng/L).
Twelve of the 29 PFAS compounds were detected at low to moderate concentrations in the well locations in the
footprint or downgradient of the proposed Phase 1 Site repository location. The PSL for PFOS (40 ng/L) was
exceeded in NTL-GW-RR-19 (53 ng/L); NTL-GW-RR13 (110 ng/L) and NTL-GW-RR18 (140 ng/L). The PSL for
PFOA (60 ng/L) was exceeded in NTL-GW-RR-19 (99 ng/L); NTL-GW-RR13 (160 ng/L) and NTL-GW-RR18
(190 ng/L). See the attached Tables 4 and 5 GW Phase 1 Area Wells and Figures 5-9.
3.2.2.4 Southwest NTL Boundary Wells (Perimeter Wells NTL-GW12; NTL-P(1,2); NTL-GP(58,61,62);
and Interior wells NTL-GP(51-57,59,60).
None of the 15 wells in this group were sampled in the 2021 SI. This area of the NTL is cross gradient from the
MSW cells in Phase I. See Figure 4.
3.2.2.5 Southwest NTL Off-Site Downgradient West Wells (NTL-GP-51-57,59,60); EGW(19-21);
EGP(22-23); EGP(30-36)
None of the 16 wells in this group were sampled in the 2021 SI. This area of the NTL is cross gradient from the
MSW cells in Phase I. See Figure 4.
3.2.2.6 Northwest NTL Boundary Wells (Perimeter Wells NTL-GW(14-15); NTL-P(3-6); and Interior
wells NTL-GP(48-50)
Of the nine wells in this group, NTL-GP48 was sampled in the 2021 SI. NTL-GP48 is located at the western end
of a future railroad alignment proposed to extend west through the Site. This area of the NTL is cross gradient
from the MSW cells in the Phase 1 area. In the NW perimeter interior well NTL-GP48 the TDS is 4,580 mg/L,
exceeding the Phase 1 area upgradient TDS PSL of 2,200 mg/L. The dissolved metal arsenic concentration in
NTL-GP48 was 0.282 mg/L exceeding the arsenic PSL of 0.01 mg/L. The arsenic levels in 2019 for the

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Northwest NTL interior well group ranged between a low of 0.0237 in NTL-GP50, 0.244 in NTL-GP48, and up to
0.307 mg/L in NTL-GP49). Barium PSL (2 mg/L) was not exceeded in the NTL-GP48 in 2021. One SVOC was
detected above the PSLs (1.1 µg/L) in NTL-GP48 (3.3 µg/L 1-methylanaphthalene). The VOCs 1,4-dioxane,
benzene and methylene chloride were detected above the PSLs in NTL-GP48. 1,4-Dioxane (0.46 µg/L) was
exceeded at a level (242 µg/L). The reported concentration of benzene is 10.8 µg/L exceeding the PSL of 5
µg/L. The reported concentration of methylene chloride in well NTL-GP48 is 6.7 µg/L, exceeding the PSL of 5
µg/L. TPH-DRO did not exceed the PSL in the 2021 SI sampling, in NTL-GP48. In 2019 all three of the NTL
northwest interior wells along the western boundary ranged from a low of NTL-GP48 (2.45 mg/L), NTL-GP-49
(3.04 mg/L), up to 3.33 mg/L in NTL-GP50. Two pesticides were detected below the Lab PQL in NTL-GP48 in
2019.
Seven of the 29 PFAS compounds were detected at low to moderate concentrations in the Northwest NTL
interior well NTL-GP-48. The PSL for PFOS (40 ng/L) was exceeded in NTL-GP-48 (98 ng/L). The PSL for
PFOA (60 ng/L) was exceeded in NTL-GP-48 (250 ng/L). NTL-GP-48 is location at the western downgradient
area of the larger NTL boundary. See the attached Tables 4 and 5 - GW Phase 1 Area Wells and Figures 5-9.
3.2.2.7 Northwest NTL Downgradient Off-Site Wells EGW(14-16,18,24-29,38-41)
None of the 16 wells in this group were sampled in the 2021 SI. This area of the NTL is cross gradient from the
MSW cells in Phase I. See Figure 4.
3.3 Test Pit Results
Sixteen test pits were excavated across the Airport West VCP site extending from the western boundary of the
NTL easterly through the Phase 1 area to the eastern area of the Phase 1 area (see Figure 4). The test pits
were excavated within the existing waste cells. Nine test pits were excavated in the MSW located in the Phase
1 area (TP-RR6, TP-RR9 through TP-RR16). Seven test pits were excavated along a future proposed rail line
extending west to the western boundary of the NTL (TP-RR1 through TP-RR5 and TP-RR7 and TP-RR8). The
test pits were excavated to observe and monitor the waste characteristics and moisture content of the waste
cells. Ten Samples were collected from the soil/waste matrix at the bottom of the waste profile. Samples of the
leachate when present were collected for laboratory analysis. Nine leachate sample plus a duplicate were
collected and analyzed. See Table 2 Phase 1 - SI Analyte List, for laboratory testing. Samples for TCLP
analysis were collected for testing, following a review of the initial sample results. Following the procedures
outlined in the SAP, if the reported total concentrations represented potentially hazardous waste concentrations,
then TCLP analysis was performed. No TCLP analysis was performed based on the initial reported total
concentration ranges. See Tables 8. See Appendix C for photographs.
3.3.1 Soil/Waste Vapor Gas Monitoring
3.3.1.1 Soil/Waste Vapor Field Multi Gas Monitoring
During excavation of the 16 test pits located in the MSW cells, field monitoring of the soil/waste vapor gas was
measured. A MultiRAE Five-Gas Monitor with Advanced VOC Detection Capability, model PGM-6228 was use.
Five gas parameters were monitoring during excavation and within the stockpiled soil/waste material. These
parameters included hydrogen sulfide, methane, carbon monoxide, oxygen and volatile organic compounds.
The test pits were continually monitored during the excavation and sampling process, with measurements
recorded at spaced intervals. Test pit gas measurement readings were recorded between 2 to 5 times
depending on the duration of the locations process time. Typically 3 readings were recorded. See Table 3 -
Vapor Gas Test Pits Phase 1 area includes the average readings for each gas parameter per TP location.
All 14 of the 16-test pit location were reported as: non-detect; a range considered background; or within the
normal or safe range. Two test pits (TP-RR10 and TP-RR11) were measured with average detections of H2S
and VOCs above background. TP-RR10 was measured at 35.93 ppm for VOCs. TP-RR11 was measured at
1.1 ppm for H2S. See Section 3.3.2 for field olfactometer data for odor measurements in the test pits.

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec INVESTIGATION RESULTS SUMMARY 18
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
3.3.2 Field Olfactometer Measurement
3.3.2.1 3.3.2.1 Field Olfactometer Odor Data
Half or 8 of the 16 test pits were recorded as very weak to weak for odor measurements with the Nasal Ranger
Field Olfactometer. Test Pits TP-RR(1,2,4,5 and 12) were recorded as moderate. Test Pit TP-RR3 was
recorded as strong and Test Pits TP-RR(10 and 11) were recorded as very strong. Tabular field olfactometer
data is included in the field measurement section of the appendices.
3.3.3 Test Pit Field Observations
3.3.3.1 Visual Waste Characteristics
Visual waste characteristics were recorded for the waste composition in the excavated test pit waste stockpiles.
Seven categories were recorded by percent composition (plastics, tires, wood, glass, paper, metal and other).
Plastics ranged between 0 to 40 percent. Tires ranged between 0 to 10 percent. Wood ranged between 10 to
50 percent. Paper ranged between 0 to 25 percent. Metal was 0 percent in all test pits. Other was 0 to 55
percent, with 0 percent in TP-RR1 through TP-RR8.
Cover material ranged between 1 and 4 feet in thickness, with TPs located in Phase I ranging between 1 to 2
feet in thickness. The waste profiles ranged between 2 to 9 feet in thickness, with the TPs located in Phase I
ranging between 2 to 4 feet in thickness. Depth to a saturation zone in the TPs ranged between 0 to 11 feet, with
7 of the 9 TPs in Phase I showing no water in the excavations. Overall depth of the TPs ranged between 3.5 to
15 feet, with the TPs located in Phase I ranging between 3.5 to 6.5 feet. In-field comments and notes are
provided in the filed forms section of Appendix A.
3.3.4 Analytical Testing Results
3.3.4.1 Soil/Waste Solids Test Results
Arsenic was the only solids result in the soil/waste matrix to report exceeding the PSL (3 mg/kg). All 10 TPs
sampled, reported arsenic exceeding the PSL in the soil/waste matrix. The arsenic ranged between 7.76 mg/kg
and the high of 27.8 mg/kg in TP-RR8 (see Table 8).
3.3.4.2 Leachate Test Results – Metals
The arsenic PSL (0.01 mg/L) was exceeded in 5 of the 9 TPs sampled. The arsenic concentrations ranged
between 0.14 mg/L to a high of 0.153 mg/L in TP-RR1L. With very little leachate present in the Phase 1 TPs, the
sole location with an exceedance for the arsenic PSL was TP-RR11L with a concentration of 0.0178 mg/L. The
cadmium PSL (0.005 mg/L) was reported as exceeded in the sole location of TP-RR11L with a concentration of
0.00519 mg/L. See Table 8 and Figure 7.
3.3.4.3 Leachate Test Results – VOCs
The benzene PSL (5 µg/L) was exceeded in five of the TPs, ranging from 10.5 µg/L to a high of 146 µg/L in TP-
RR5L. Benzene was not exceeded in any of the leachate samples within the Phase I TPs. The PSL for
methylene chloride (5 µg/L) was exceeded in three of the TPs ranging between 6.1 µg/L in TP-RRDupe3, the
field duplicate of TP-RR8, to a high of 216 µg/L in TP-RR3. The Phase I TP-RR11 was reported exceeding the
methylene chloride PSL with a concentration of 6.4 µg/L. Seven of the nine TPs reported exceeding the 1,4-
dioxane PSL of 0.46 µg/L, ranging from 4.31 µg/L to a high of 393 in TP-RR1. The sole Phase I TP reporting
exceeding the 1,4-dioxane PSL was TPRR11 with a concentration of 3.7 µg/L. TP-RR3 located on the western
area of the NTL reported exceeding nine other VOCs. See Table 5 - Phase 1 Area Test Pits Summary for the
concentrations for these other VOC exceedances in TP-RR3. See Figure 5.
3.3.4.4 Leachate Test Results – SVOCs
The PSL for the SVOC of benzo(a)pyrene (0.2 µg/L) was exceeded in TP-RR11, at a concentration of 0.23 µg/L.
No other PSL for SVOCs was exceeded in the Phase I TPs. Eight PSLs for SVOCs were exceeded in 1 to 7 TP

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec The PSL for PFOA (60 ng/L) was exceeded in 8 of the 9 TPs
sampled for PFAS. The PFOA concentrations ranged between 31 to 530 ng/L. The PSL for PFOS (40 ng/L) was exceeded in the same 8 of
9 TPs sampled. The PFOS concentrations ranged between ND to 400 ng/ 19
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
locations west of Phase I in the western area of the NTL Site. This western area of the NTL Site is
hydrologically cross gradient from the Phase I area. See Table 5 - Phase 1 Area Test Pits Summary for the
concentrations for these other VOC exceedances in these wells located in the western area of the NTL. See
Figure 6.
3.3.4.5 Leachate Test Results – TDS
The PSL for the Phase 1 area TDS (2,200 mg/L) was established to characterize the shallow groundwater within
the Phase 1 area TDS compared to the upgradient groundwater quality. The PSL for TDS in the leachate
should only be applied as a reference. It is assumed MSW leachate will be elevated in TDS values. There is
little movement of the leachate and high contact with the decomposing waste material. The leachate TDS
values can be useful when developing leachate treatment designs for the handling and disposal of the leachate
during excavation of the waste and remediation of the landfill. The concentration of TDS in the test pits ranged
between 2580 mg/L up to 26,000 mg/L in NTL-TP11. See Table 8 and Figure 9.
3.3.4.6 Leachate Test Results – PFAS
The PSL for PFOA (60 ng/L) was exceeded in 8 of the 9 TPs sampled for PFAS. The PFOA concentrations
ranged between 31 to 530 ng/L. The PSL for PFOS (40 ng/L) was exceeded in the same 8 of 9 TPs sampled.
The PFOS concentrations ranged between ND to 400 ng/L. No exceedances for PFAS constituent PSLs were
exceeded in the leachate within the Phase 1 Area Development boundary. See Table 6 and Figure 8.

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec 20
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
4 QUALITY ASSURANCE/QUALITY CONTROL
The SI Quality Assurance/Quality Control program followed CDM’s Final Supplemental Landfill Characterization
Quality Assurance Project Plan (QAPP), dated August 6, 2008, for the NTL Site. In accordance with this QAPP
the number of Field Duplicate (DUP), Equipment Rinsate Blank (EB), and Trip Blank (TB) sample conducted for
solid and aqueous samples are listed in Table 2 - Sample Matrix Table. Two field duplicates were collected from
within the sampled locations, (one at NTL-GP69 and one at TP-RR8. A total of 3 Equipment Rinsate Blanks
(EB) were collected on a daily basis where decontamination of equipment was performed and analyzed.
Cardno, Inc.’s ESI WP sampling methodologies were specifically developed to minimize the potential for cross-
contamination to occur in the field through the combination of a reduction of the use of “common” equipment and
strict decontamination methods. During groundwater sampling the only “common” equipment used was the
“PFAS safe” water level probe used during low flow pumping to gauge the steady state for water levels in the
well. A total of 6 Trip Blanks (TB) were submitted for laboratory analysis. The TB was submitted for each batch
of VOC samples submitted to the laboratory.
The analytical methods used for the SI are listed in the attached Table 2 - Phase 1 Area Analyte Table. The
laboratory’s PQLs and MDLs are listed in the GW and Test Pit Exceedance Summary Tables 4 through 8. The
Analytical Summary Results Tables list each analyte individual PQL and MDL. AWAL followed the USEPA
Level III data quality program as part of the laboratory reporting effort. AWAL provided a quality assurance
evaluation of all laboratory data in order to determine if the data are of sufficient quality in accordance with Level
III criteria. The laboratory evaluation is provided with the laboratory reports provided in Appendix B. A summary
of the QC Summary Report qualified data on the samples is provided in Summary Results Tables 4 through 8.
The preparations and analyses of the samples were performed within the method holding times following the
methods stated on the analytical reports. All samples were received in appropriate containers and properly
preserved. The samples were prepared and analyzed following the methods stated on the analytical reports. All
instrument calibration and calibration check requirements were met, with continuing calibration verification
exceptions noted on the reports. No target analytes were detected within the method blank (MBLK), above
reporting limits, indicating the procedure was free from contamination. All laboratory control samples (LCS), and
LCS duplicate sample (LCSD) percent recoveries were within control limits. Matrix spike (MS) and MS duplicate
samples (MSD) percent recoveries and/or relative percent differences (RPD) were inside established limits. The
parameters that required a duplicate analysis had RPDs within the control limits, with the exception of, due to
suspected sample non-homogeneity or sample matrix interference. All surrogate recoveries were within
established limits, with the Laboratory QC summary listed exceptions. Data deemed acceptable as no analytes
associated with this surrogate were observed in the field sample. The MS yielded similar results indicating
sample matrix interference; No corrective action was required on any of the laboratory sets. A full narrative is
provided in the analytical laboratory reports in Appendix B.
As part of the QA/QC program, a TB was included in each sample cooler containing samples to be analyzed for
VOCs. Review of the TB laboratory results indicated no detection of VOCs above the laboratory PQLs.
Two groundwater field duplicate samples were collected during the SI sample collection and the comparison on
detections above the laboratory PQL are presented in Tables 4 and 8.
A comparison of the blind duplicate and primary water samples reported above the PQL results indicate +/- less
than 0% to 42% were observed. For compounds reported exceeding their respective PSLs, the range was +/-
less than 0% to 20%, with a range up to 36%.
QC samples, including 6 trip blanks, 3 equipment blanks, 2 blind duplicates, 6 MS/MSD sample sets were
collected. All samples were collected in containers provided by the testing laboratory and met analysis holding
times.

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec QUALITY ASSURANCE/QUALITY CONTROL 21
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
Based upon a comprehensive review of the QC data, the quality objectives and measurement performance
criteria indicators of precision, accuracy, completeness, representativeness and comparability have been met
and the data are valid and useable.

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec CONCLUSIONS 22
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
5 CONCLUSIONS
The SI was successful at supplementing the existing Phase 1 area data such that requisite remedial action
designs can be better evaluated and developed to support the environmental remediation necessary to address
the impacts associated with the former landfill operation and thereby facilitate commercial redevelopment of the
Phase 1 area. These objectives were accomplished by a) delineating the type and extent of groundwater
contamination within the Phase 1 area via groundwater sampling of both existing and new monitoring wells; b)
determining the groundwater flow direction across the Phase 1 area to establish hydrologically upgradient and
downgradient positions with respect to the Phase 1 area; and c) providing additional data on the buried MSW via
newly excavated test pits within the waste cells.
Consistent with the realization of the aforementioned project objectives, a permanent groundwater monitoring
network will be designed based on the aggregate groundwater data and both the groundwater gradient and flow
direction. Further, a RAP will also be developed which will more succinctly describe the design considerations
and remedial approaches associated with the consolidation of the MSW within the trench cells into a final
engineered waste repository within the Phase 1 area boundary.

5.1 Groundwater Considerations
Of the eight major analyte groups analyzed including dissolved metals, TDS, VOCs, SVOCs, TPH-GRO, TPH-
DRO, TRPH, and PFAS, four of the groups were reported in well locations above their PSL, including dissolved
metals, TDS, VOCs and PFAS. Based on the hydrogeologic gradient and flow direction, the furthest
downgradient Site well NTL-GP69 exhibited PSL exceedances of TDS, As, 1,4 dioxane, 1,1-DCA and VC while
the Phase 1 area wells did not report any PSL exceedances of 1,1-DCA or VC. While the contaminants of TDS,
As and 1,4-dioxane may exceed their respective PSLs in groundwater beneath the Phase 1 area, other regional
environmental factors also exist that affect their presence, concentration, and distribution in both shallow and
deeper regional water-bearing zones.
Regarding TDS, while its PSL was exceeded throughout the Phase 1 area monitoring wells, with the highest
concentration being reported for GW-RR18 (34,700 mg/L) located within the proposed repository area, the Site
is located within and is underlain by a poorly drained area of non-potable Class IV groundwater due to the highly
saline nature and high natural TDS of area groundwater. Further, the Site and is in an area that is rapidly
developing with both commercial and industrial applications.
Similarly, while dissolved arsenic is as widespread through all media at the Site and exceeded its PSL in most all
of the on-site monitoring wells (including the upgradient wells along the southern Phase 1 boundary), arsenic is
naturally occurring within both soil and groundwater within the Salt Lake Valley and is reported to be higher
throughout the western area of the US. Beyond arsenics ubiquitous presence throughout the Salt Lake Valley,
dissolution of arsenic from the soil underlying the Site may also possibly occur through continuous hydrolysis of
the buried MSW. This potential is part of the working and evolving development of the Site Conceptual Model
(SCM) as part of the RAP. This would occur via microbial conversion of biodegradable organic content causing
production of volatile organic acids that would result in a lowering of leachate pH and a subsequent dissolution
of dissolved arsenic that could potentially impact shallow groundwater. With planned future removal of the MSW
from the poorly covered Site waste cells and contaminant reduction of any generated acidic leachate, future
Site-related arsenic impacts (if any) to the underlying groundwater should decrease.
With respect to the detected groundwater VOCs and with the exception of the compound 1,4-dioxane, one other
detection of a single VOC occurred above their respective VOC PSLs in the Phase 1 on-site wells. This
included 1,4-DCB in the well location in NTL-GP63 (at 2.1 µg/L) in the 2019 ESI sampling. No VOCs other than
1,4-dioxane were detected above their PSL in the 2021 SI well sampling.
In addition, 1,4-dioxane exceeded its PSL in most all of the Phase 1 monitoring well locations including one of
the upgradient well locations NTL-GW10.
1,4-dioxane is currently used as a solvent in a variety of commercial and industrial applications such as in the
manufacture of other chemicals, a processing aid, functional fluid, a laboratory chemical, in adhesives and

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec CONCLUSIONS 23
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
sealants, in spray polyurethane foam, in printing inks, and as a dry film lubricant. It is also found as a
contaminant in consumer products such as soaps and detergents.
The presence of elevated TDS and arsenic in groundwater beneath the Site are related to the background
conditions and as such, further investigations down gradient of the landfill site as well as the upgradient wells will
be conducted to understand the background or regional detection of 1,4-dioxane within groundwater and what
impacts the past landfill operations have had.
The other analytical suites including SVOCs and TPH-DRO compounds both indicated PSL exceedances in 4 of
the Phase 1 well locations from the 2019 ESI sampling. The PFAS compounds PFOS and PFOA exceeded
their respective PSL in a number of the perimeter downgradient Phase 1 Site area wells (NTL-GP 63, 65 and 66)
and (NTL-GW 13, 18 and 19).
5.2 Leachate Considerations
Of the eight major analyte groups that were sampled during this SI (dissolved metals, TDS, VOCs, SVOCs,
TPH-GRO, TPH-DRO, TRPH, and PFAS), the only analyte groups reported to have test pit leachate locations in
the Phase 1 area above their respective PSL’s are dissolved metals, TDS, VOCs, SVOCs and PFAS. The PSL
for arsenic and cadmium were exceeded in a single test pit (TP-RR11L) in the Phase 1 area. Both exceedances
were within the same order of magnitude as the PSL. The compounds 1,4-dioxane and methylene chloride are
the only VOCs exceeding the PSLs in the test pits in the Phase 1 area. The methylene chloride exceedance is
within the same order of magnitude as the PSL. The compounds benzo(a)pyrene, 1 -Methylnaphthalene and
Bis(2-ethylhexyl) phthalate are the SVOCs exceeding the PSLs in the Phase 1 test pits. The exceedances are in
two locations and is within the same order of magnitude as the PSL. The 1,4-dioxane exceedance is within one
order of magnitude above the PSL within the Phase 1 area. The PFAS compounds PFOS and PFOA exceeded
their respective PSL in an eight of the TPs sampled. None of these TPs were located in the Phase 1 Site
boundary area.
The RAP which is being prepared for the future remedial actions will calculate and identify risk levels for
receptors. The RAP will identify management procedures as a precautionary measure to minimize exposure to
leachate and noted exceedances in ground water. These procedures will specifically be directed to minimize
exposure by ingestion and dermal contact to the short- term construction worker, which is identified as the
exposure receptor for the proposed remedial action.
5.3 Soil Considerations
Nine soil samples were collected from the soil/waste matrix samples from sixteen location for analysis of
seven major analyte groups (dissolved metals, VOCs, SVOCs, TPH-GRO, TPH-DRO, TRPH, and PFAS).
Of these suites, only arsenic was reported as exceeding its PSL.
Future and On-Going Monitoring
While the focus of this SI has been the Phase 1 Area Development and the proposed RAP associated with
this area, on-going monitoring and investigations of other areas of the NTL Site are planned for future
remedial actions and periodic monitoring necessary to characterize the levels and extent of the impacts
from the MSW and the remedies to address these impacts.

Phase 1 Area 2021 Supplemental Investigation Report
Airport West VCP #C092
August 10, 2022 Cardno, now Stantec REFERENCES 24
Airport West VCP Phase 1 Area 2021 SI Report FINAL 8-10-22.docx
6 REFERENCES
Salt Lake City Corporation/EMCON Associates 1977. Geotechnical Investigation and Evaluation of the West
North Temple Street Landfill
Bingham Engineering 1982. Site Investigation, Bonneville Center
Utah Department of Health 1987. Preliminary Assessment (PA) NTL
Utah Department of Health 1989. Analytical Results Report (ARR) - Site Inspection (SI) NTL
USEPA/URS, Inc. 1994. Site Inspection Prioritization (SIP) NTL
USEPA/URS, Inc. 1995. Analytical Results Report - Site Inspection Prioritization (SIP) NTL
Salt Lake County Health Department/Maxim Technologies, Inc. 1998 Groundwater Sampling Event NTL
Bingham Environmental, Inc. 1998 thru 2004 Semi-Annual GW Monitoring Reporting – Voluntary Cleanup
Program (VCP) – Bonneville Center
Kennedy/Jenks Consultants 2005 thru 2006 Semi-Annual GW Monitoring Reporting – Voluntary Cleanup
Program (VCP) – Bonneville Center
Montgomery Watson 2000. Site Investigation and Sampling Summary Report NTL
HKC & Associates, Inc., UTEX Environmental Services, LLC 2005. Solid Waste Excavation and Sampling NTL
HKC & Associates, Inc., UTEX Environmental Services, LLC 2006. Revised – Groundwater Monitoring and
Sampling (OCT05) NTL
HKC & Associates, Inc., UTEX Environmental Services, LLC 2006. Sporting Clay Shooting Area NTL
HKC & Associates, Inc., UTEX Environmental Services, 2006 Groundwater Monitoring and Sampling (FEB06)
NTL
IHI Environmental, Inc 2006. Phase II ESA 712 Acre Parcel North of NTL
UTEX Environmental Services, LLC, 2006 Report of Water Analysis from Pilot Dewatering Area
URS/CDM/SLR, 2008 Planning Level Geotechnical Study – NW Quadrant Development Planning
ERM, 2012 Quarterly Groundwater Monitoring Report
Cardno, Inc. 2016 Subsurface Investigation Report
The Ninigret Group, 2018 Supplemental Site Characterization Study
Cardno, Inc. 2019 Expanded Subsurface Investigation Report

Table 1
GROUNDWATER ELEVATION DATA
AUG/SEPT 2021
AIRPORT WEST PHASE 1 - SUPPLIMENTAL INVESTIGATION
12/14/202110:45 AM
NAME
Depth from
TOC
State Plane
NORTHING
State Plane
EASTING
SURVEY
No.
TOC - Top
PVC
WL Sept
2021
NTL-GW-10 6.42 3441160.04 1489661.53 7026 4228.07 4221.65
NTL-P7S 9.67 3443534.23 1490935.79 7046 4230.24 4220.57
NTL GP 63 7.93 3442542.43 1488574.55 8087 4229.13 4221.2
NTL GP 65 9.25 3444005.29 1489270.96 8088 4229.56 4220.31
NTL GP 66 11.02 3444026.96 1490389.73 8091 4230.82 4219.8
NTL GP 67 10.2 3442672.08 1491004.08 8099 4230.56 4220.36
NTL GP 69 8.75 3445282.07 1489174.56 8092 4225.93 4217.18
NTL-GW-09 9.07 3441209.97 1491351.19 7025 4232.04 4222.97
GW-RR-13 9.15 4228 4218.85
GW-RR-18 6.81 4227 4220.19
GW-RR-19 7.9 4227 4219.1
Airport West Water Level 1 819AR00640
Airport West Phase 1 Site Investigation Analyte Matrix Table 2 (AUG/SEP 2021)Sampling Matrix 12/13/2021 2:44 PM
Sample I.D.Number of
Samples
Approx. Depth of
Wells (bgs)
RCRA 8 Metals
(EPA 6020B/6010D
&
74070A/7471A)
Hexavalent
Chromium 7196A
VOCs & TPH GRO
(EPA 8260C /
Full Scan ) (1)
HEM-SGT TRPH
(EPA Method
1664)
SVOCs & TPH DRO
(EPA 8270D /
SIM) (2)
PFAS (EPA
Method 537
MOD)
VOCs; O2;
%LEL CH4;
CO; and HS4
TDS Depth to Water
Measured
Duplicate Sample
I.D.
Equipment
Blank (1/Day)
Sample I.D.
Trip Blank
(1/Day) Sample
I.D.
NTL-P7-S 1 15 1 1 1 1 1 1 1 1 1
NTL-GP63 1 17 1 1 1 1 1 1 1 1
NTL-GP65 1 17 1 1 1 1 1 1 1 1
NTL-GP66 1 17 1 1 1 1 1 1 1 1
NTL-GP67 1 17 1 1 1 1 1 1 1 1
NTL-GP69 1 17 1 1 1 1 1 1 1 1 1 1
NTL-GP48 1 22 1 1 1 1 1 1 1 1 1 1
NTL-GW09 1 15 1 1 1 1 1 1 1 1 1
NTL-GW10 1 15 1 1 1 1 1 1 1 1
GW-RR-13 1 20 1 1 1 1 1 1 1 1 1 1
GW-RR-18 1 20 1 1 1 1 1 1 1 1
GW-RR-19 1 20 1 1 1 1 1 1 1 1
Test Pit Soil/Waste Matrix 10 Subsurface 10 10 10 10 10 10 10 10 10
Test Pit Leachate 10 surface 9 9 9 9 9 9 9 9 9 1 1 1
Air (Soil/Waste) Vapor Monitoring 16 MSW 16
TOTAL 48 31 31 31 31 31 31 35 31 31 2 3 6
(1) Lab will run full scan on VOCs including 1,4 Dioxane. Lab will also run SIM for 1,4 Dioxane for full scan results under PQL (Estimated at 50%)
(2) Full list plus SIM (PAH Single Selected Ion Mode)
GW/Soil/MSW Sample Matrix
Phase 1 Area SI Analyte Table 2.xlsx 819AR00640
Table 3
SOIL/WASTE VAPOR GAS
MONITORING RESULTS SUMMARY
TEST PITS
PHASE 1 AREA DEVELOPMENT
AIRPORT WEST VCP
SEPTEMBER 2021
12/19/2021 3:24 PM
Date TP Name
Values TP RR1 TP RR2 TP RR3 TP RR4 TP RR5 TP RR6 TP RR7 TP RR8 TP RR10 TP RR11 TP RR12 TP RR13 TP RR14 TP RR15 TP RR16
H2S (ppm)0.0 0.0 0.2 0.0 0.0 0.0 0.0 0.0 0.0 1.1 0.3 0.0 0.0 0.0 0.0
CH4 (% LEL)0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
CO (ppm)0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
O2 (% vol)20.9 20.9 20.9 20.9 20.9 20.9 20.9 20.9 20.9 20.9 20.9 21 20.9 20.9 20.9
VOC (ppmv)0.30 0.13 0.33 0.10 0.20 0.00 0.02 0.23 35.93 0.83 0.07 0.00 0.00 0.00 0.00
Sample
Depth (ft.)
12 12 11 10 8.5 5.5 8.5 5 6 6.5 5 4.5 3.5 4 4.5
Notes
TP Test Pit
RR Railroad Alignment
H2S Hydrogen Sulfide (ppm)
CH4 Methane (% LEL)
CO Carbon Monoxide (ppm)
O2 Oxygen (% vol)
VOC Volatile Organic Compound (ppm)
ppm Parts per million
LEL Lower explosive limit
vol Volume
9/2/2021 9/3/2021 9/7/2021
TP gas_JRT.xlsx 1 CARDNO 819AR00640
TABLE 4
PSL EXCEEDANCE SUMMARY
GW WELLS
PHASE 1 AREA DEVELOPMENT
AIRPORT WEST VCP
OCTOBER 2021
1/4/2022 5:43 PM
ClientSampID CollectionDate Lab Set
NTL GP 48 W NTL GW 10 W NTL GP 63 W NTL GP 65 W NTL Dupe 1 W NTL GP 66 W NTL GP 67 W NTL GP 69 W NTL P7S W GW RR13 w GW RR18 w GW RR19 w
9/2/2021 8/30/2021 8/31/2021 9/1/2021 9/3/2021 9/1/2021 8/31/2021 9/1/2021 8/31/2021 9/22/2021 9/22/2021 9/22/2021
TestCode Analyte CAS Matrix Units Values 2109080 2108825 2108875 2109038 2109038 2109038 2108875 2109038 2108875 2109568 2109568 2109568
RESULT 0.282 0.0581 0.326 0.35 0.229 0.013 0.267 0.244 0.0497 0.875
PQL 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.004
MDL 0.00127 0.00127 0.00127 0.00127 0.00127 0.00127 0.00127 0.00127 0.00127 0.00127
PSL 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01
QualCode 1
RESULT 0.00565 0.00679 0.0156
PQL 0.0007 0.0007 0.0007
MDL 0.000136 0.000136 0.000136
PSL 0.005 0.005 0.005
QualCode
RESULT 39.3
PQL 2
MDL 1.15
PSL 2.8
QualCode
RESULT 10.8
PQL 20
MDL 1.47
PSL 5
QualCode J
RESULT 6.7
PQL 20
MDL 4.51
PSL 5
QualCode J$B
RESULT 3.29
PQL 1
MDL 0.205
PSL 2
QualCode
RESULT 48.4 298 28.9 63.6
PQL 50 50 50 50
MDL 21.5 21.5 21.5 21.5
PSL 0.46 0.46 0.46 0.46
QualCode J J
RESULT 242 1.71 0.83 7.07 0.85 1.62 16.5
PQL 3 0.3 0.3 0.3 0.3 0.3 0.3
MDL 1.8 0.18 0.18 0.18 0.18 0.18 0.18
PSL 0.46 0.46 0.46 0.46 0.46 0.46 0.46
QualCode 1
RESULT 3.33
PQL 0.48
MDL 0.0988
PSL 1.1
QualCode @
RESULT 4580 5400 23000 22400 9600 9120 6870 4180 22600 34700 33400
PQL 100 100 100 100 50 100 50 100 100 100 100
MDL 80 80 80 80 40 80 40 80 80 80 80
PSL 2200 2200 2200 2200 2200 2200 2200 2200 2200 2200 2200
QualCode
NOTES
PSL Project Screening Level
PQL Laboratory Practical Quantitation Limit
MDL Laboratory Method Detection Limit
SIM Laboratory Selected Ion Monitoring Method
NTL Former North Temple Landfill waste cell
TP Test Pit
RR Railroad Aliagnment
Qualifier Definition
J Estimated value between the MDL and the reporting limit (PQL).
B This analyte was also detected in the method blank below the PQL.
@ High RPD due to suspected sample non homogeneity or matrix interference.
1 Matrix spike recovery indicates matrix interference.The method is in control as indicated by the LCS.
$This compound exceeded (low)the control limit for the CCV.The compound concentration is estimated and may be biased low.
NTL Dupe 1 w is duplicate of NTL GP 65
(blank)
Aqueous
mg/L
µg/L
mg/L
7440 38 2
7440 43 9
75 34 3
71 43 2
75 09 2
75 01 4
123 91 1
90 12 0
8260D W
8260D W SIM 1,4 Dxn
8270E W SIM 3511
TDS W 2540C
Arsenic
Cadmium
1,1 Dichloroethane
Benzene
Methylene chloride
Vinyl chloride
1,4 Dioxane
1 Methylnaphthalene
Total Dissolved Solids
6020B DIS
Copy of AWAL detection_DKC_JRT.xlsx 1 OF 1 CARDNO 819AR00640
TABLE 5
PSL EXCEEDANCE SUMMARY (PFAS)
GW WELLS
PHASE 1 AREA DEVELOPMENT
AIRPORT WEST VCP
JULY 2022
8/10/2022 3:55 PM
Client Sample ID Lab Sample ID Collection Date
NTL P7S W NTL GP 48 W NTL GP 63 W NTL GP 65 W NTL GP 66 W NTL GP 67 W NTL GP 69 W NTL GW 09 W NTL GW 10 W NTL GW RR19 W NTL GW RR13 W NTL GW RR18 W
320 78807 5 320 78807 10 320 78807 3 320 78807 6 320 78807 7 320 78807 4 320 78807 8 320 78807 1 320 78807 2 320 79409 3 320 79409 1 320 79409 2
Matrix
Analysis
Method Unit Analyte CAS PSL Values
8/31/2021 9/2/2021 8/31/2021 9/1/2021 9/1/2021 8/31/2021 9/1/2021 8/30/2021 8/30/2021 9/22/2021 9/22/2021 9/22/2021
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.29 1.6 1.4 1.3 2.6 0.26 0.27 0.26 0.27 0.28 2.8 3.2
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.36 2 1.7 1.7 3.3 0.32 0.34 0.33 0.34 0.35 3.5 4
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.22 1.2 1 1 2 0.19 0.2 0.2 0.2 0.21 2.1 2.4
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 4.5 25 22 21 41 4.1 4.2 4.1 4.3 4.3 43 50
MDL 2.3 12 11 10 20 2 2.1 2.1 2.1 2.2 22 25
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.42 2.3 2 1.9 3.8 0.37 0.39 0.38 0.39 0.4 4 4.6
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.22 1.2 1 1 2 0.19 0.2 0.2 0.2 0.21 2.1 2.4
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 3.6 20 17 17 33 3.2 3.4 3.3 3.4 3.5 35 40
MDL 1.4 7.4 6.5 6.3 12 1.2 1.3 1.2 1.3 1.3 13 15
QualCode H H
Result 1.9 ND ND ND ND ND ND ND ND 2.1 ND 21
PQL 4.5 25 22 21 41 4.1 4.2 4.1 4.3 4.3 43 50
MDL 1.2 6.4 5.6 5.4 11 1.1 1.1 1.1 1.1 1.1 11 13
QualCode J H H J J
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 4.5 25 22 21 41 4.1 4.2 4.1 4.3 4.3 43 50
MDL 1.1 5.9 5.2 5 9.8 0.97 1 0.99 1 1 10 12
QualCode H H
Result ND ND 40 110 110 5.5 4 10 0.84 210 130 240
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.18 0.98 0.87 0.84 1.6 0.16 0.17 0.16 0.17 0.17 1.7 2
QualCode H JH
Result ND 380 ND 140 400 15 19 8.7 3.4 320 140 420
PQL 19 25 21 21 41 4.1 4.2 4.1 4.3 4.3 43 50
MDL 19 12 21 10 20 1.9 2 2 2 2.1 21 24
QualCode G G H JH
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.29 1.6 1.4 1.3 2.6 0.26 0.27 0.26 0.27 0.28 2.8 3.2
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.28 1.5 1.3 1.3 2.5 0.25 0.26 0.26 0.26 0.27 2.7 3.1
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.5 2.7 2.4 2.3 4.5 0.45 0.46 0.45 0.47 0.48 4.8 5.5
QualCode H H
Result ND ND ND 1.8 4.9 ND ND ND ND 1.6 7 ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.17 0.93 0.82 0.79 1.6 0.15 0.16 0.16 0.16 0.17 1.7 1.9
QualCode JI J H H J J
Result 4.4 71 16 47 86 1.3 2.6 1.3 ND 52 51 120
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.23 1.2 1.1 1 2 0.2 0.21 0.21 0.21 0.22 2.2 2.5
QualCode J JH H
NE
60
NE
6000
NE
763051 92 9
919005 14 4
757124 72 4
27619 97 2
39108 34 4
756426 58 1
13252 13 6
2991 50 6
2355 31 9
375 73 5
375 22 4
335 77 3
335 76 2
307 55 1
375 92 8
11Cl PF3OUdS
4,8 Dioxa 3H perfluorononanoic acid
(ADONA)
4:2 FTS
6:2 FTS
8:2 FTSGr
o
u
n
d
w
a
t
e
r
53
7

(
m
o
d
i
f
i
e
d
)
ng
/
L
375 85 9
9Cl PF3ONS
HFPO DA (GenX)
NEtFOSAA
NMeFOSAA
Perfluorobutanesulfonic acid (PFBS)
Perfluorobutanoic acid (PFBA)
Perfluorodecanesulfonic acid (PFDS)
Perfluorodecanoic acid (PFDA)
Perfluorododecanoic acid (PFDoA)
Perfluoroheptanesulfonic Acid (PFHpS)
Perfluoroheptanoic acid (PFHpA)
320 78807 1_Eurofins.xlsx 1 OF 2 819AR00640
TABLE 5
PSL EXCEEDANCE SUMMARY (PFAS)
GW WELLS
PHASE 1 AREA DEVELOPMENT
AIRPORT WEST VCP
JULY 2022
8/10/2022 3:55 PM
Client Sample ID Lab Sample ID Collection Date
NTL P7S W NTL GP 48 W NTL GP 63 W NTL GP 65 W NTL GP 66 W NTL GP 67 W NTL GP 69 W NTL GW 09 W NTL GW 10 W NTL GW RR19 W NTL GW RR13 W NTL GW RR18 W
320 78807 5 320 78807 10 320 78807 3 320 78807 6 320 78807 7 320 78807 4 320 78807 8 320 78807 1 320 78807 2 320 79409 3 320 79409 1 320 79409 2
Matrix
Analysis
Method Unit Analyte CAS PSL Values
8/31/2021 9/2/2021 8/31/2021 9/1/2021 9/1/2021 8/31/2021 9/1/2021 8/30/2021 8/30/2021 9/22/2021 9/22/2021 9/22/2021
Result 5.2 ND 25 11 68 1.7 1 2.8 ND 48 88 100
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.52 2.8 2.5 2.4 4.7 0.46 0.48 0.47 0.49 0.5 5 5.7
QualCode J H H
Result 6.5 120 17 160 250 2.5 8.4 7.2 ND 92 100 260
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.53 2.8 2.5 2.4 4.8 0.47 0.49 0.48 0.5 0.5 5 5.8
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.34 1.8 1.6 1.5 3 0.3 0.31 0.3 0.32 0.32 3.2 3.7
QualCode H H
Result ND ND ND ND ND 0.27 ND 1.1 0.62 0.43 ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.25 1.3 1.2 1.1 2.2 0.22 0.23 0.22 0.23 0.23 2.3 2.7
QualCode J JH JH J
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.89 4.8 4.2 4.1 8 0.8 0.83 0.81 0.84 0.85 8.5 9.8
QualCode H H
Result 20 98 ND ND 130 3.3 ND 5.5 1.9 53 110 140
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.49 2.6 2.3 2.3 4.4 0.44 0.46 0.45 0.46 0.47 4.7 5.4
QualCode H H
Result 40 250 71 70 290 38 5.2 7.9 ND 99 160 190
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.77 4.2 3.7 3.5 7 0.69 0.72 0.7 0.73 0.74 7.4 8.5
QualCode H H
Result 3.9 7.9 23 24 53 0.88 1.3 0.54 ND 100 71 120
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.27 1.5 1.3 1.3 2.5 0.24 0.25 0.25 0.26 0.26 2.6 3
QualCode J J J JH H
Result ND 44 14 40 49 1.6 3.4 12 ND 71 58 240
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.44 2.4 2.1 2 4 0.4 0.41 0.4 0.42 0.43 4.3 4.9
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 0.66 3.6 3.2 3 6 0.59 0.62 0.6 0.62 0.63 6.4 7.3
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 1.2 6.4 5.6 5.4 11 1.1 1.1 1.1 1.1 1.1 11 13
QualCode H H
Result ND ND ND ND ND ND ND ND ND ND ND ND
PQL 1.8 9.8 8.7 8.4 16 1.6 1.7 1.6 1.7 1.7 17 20
MDL 1 5.4 4.8 4.6 9 0.89 0.93 0.91 0.94 0.96 9.6 11
QualCode H H
NOTES:
250 Result exceeds the PSL
ng/L nano gram per liter (ppt)
PSL Project Screening Level
PQL Laboratory Practical Quantitation Limit
MDL Laboratory Method Detection Limit
NTL Former North Temple Landfill
RR Railroad Aliagnment
NE Not Established
ND Not Detected above the MDL
QualCode Qualifier Definition
G The reported quantitation limit has been raised due to an exhibited elevated noise or matrix interference
H Sample was prepped or analyzed beyond the specified holding time
I Value is EMPC (estimated maximum possible concentration).
J Result is less than the RL but greater than or equal to the MDL and the concentration is an approximate value
60
NE
390
NE
59
NE
40
2706 91 4
2706 90 3
376 06 7
72629 94 8
2058 94 8
68259 12 1
375 95 1
754 91 6
1763 23 1
335 67 1
Perfluoroundecanoic acid (PFUnA)
Perfluorooctanoic acid (PFOA)
Perfluoropentanesulfonic acid (PFPeS)
Perfluoropentanoic acid (PFPeA)
Perfluorotetradecanoic acid (PFTeA)
Perfluorotridecanoic acid (PFTrDA)
Perfluorohexanoic acid (PFHxA)
Perfluorononanesulfonic acid (PFNS)
Perfluorononanoic acid (PFNA)
Perfluorooctanesulfonamide (FOSA)
Perfluorooctanesulfonic acid (PFOS)
355 46 4
307 24 4
Perfluorohexanesulfonic acid (PFHxS)
320 78807 1_Eurofins.xlsx 2 OF 2 819AR00640
TABLE 6
EXCEEDANCE SUMMARY (PFAS)
TEST PIT LEACHATE
PHASE 1 DEVELOPMENT AREA
AIRPORT WEST VCP
JULY 2022
8/4/2022 2:23 PM
Client Sample ID Lab Sample ID Collection Date
NTL TP RR1 L NTL TP RR2 L NTL TP RR3 L NTL TP RR4 L NTL TP RR5 L NTL TP RR6 L NTL TP RR7 L NTL TP RR8 L NTL TP RR11 L
320 78805 1 320 78805 2 320 78805 3 320 78805 4 320 78805 5 320 78805 7 320 78805 8 320 78805 9 320 78805 10
Matrix Analysis Method Unit Analyte CAS PSL Values 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/3/2021 9/3/2021 9/3/2021 9/3/2021
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 3.1 1.6 1.6 1.6 1.5 0.32 1.6 0.31 0.27
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 3.9 2 1.9 2 1.9 0.4 2 0.39 0.34
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 200 9.7 10 9.3 2 10 1.9 1.7
MDL 2.3 24 1.2 1.2 1.1 0.24 1.2 0.23 0.21
QualCode H
Results ND ND ND ND ND ND ND ND ND
PQL 48 25 24 25 23 5 25 4.8 4.3
MDL 24 12 12 13 12 2.5 12 2.4 2.1
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 4.4 2.3 2.2 2.3 2.1 0.46 2.3 0.45 0.39
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 2.3 1.2 1.2 1.2 1.1 0.24 1.2 0.23 0.21
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 39 20 19 20 19 4 20 3.9 3.4
MDL 14 7.5 7.3 7.5 7 1.5 7.5 1.5 1.3
QualCode
Results 77 150 110 63 120 14 59 28 ND
PQL 48 25 24 25 23 5 25 4.8 4.3
MDL 13 6.5 6.3 6.5 6.1 1.3 6.5 1.3 1.1
QualCode
Results 13 6.1 10 ND ND ND ND ND ND
PQL 48 25 24 25 23 5 25 4.8 4.3
MDL 12 6 5.8 6 5.6 1.2 6 1.2 1
QualCode J J J
Results ND 87 31 33 180 77 92 150 47
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 1.9 1 0.97 1 0.93 0.2 1 0.19 0.17
QualCode I I
Results 990 360 580 42 240 290 180 280 190
PQL 48 25 24 25 23 5 25 24 4.3
MDL 23 12 12 12 11 2.4 12 12 2.1
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 3.1 1.6 1.6 1.6 1.5 0.32 1.6 0.31 0.27
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 3 1.5 1.5 1.6 1.4 0.31 1.5 0.3 0.27
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 5.3 2.7 2.7 2.8 2.6 0.55 2.7 0.53 0.47
QualCode
Results ND ND ND 8.7 22 7 15 8.2 ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 1.8 0.95 0.93 0.95 0.89 0.19 0.95 0.18 0.16
QualCode J
Results 110 110 130 23 80 44 56 92 26
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 2.4 1.2 1.2 1.3 1.2 0.25 1.2 0.24 0.21
QualCode
375 85 9
NMeFOSAA
Le
a
c
h
a
t
e
53
7

(
m
o
d
i
f
i
e
d
)
ng
/
L
11Cl PF3OUdS
4,8 Dioxa 3H perfluorononanoic acid
(ADONA)
4:2 FTS
Perfluorobutanesulfonic acid (PFBS)
Perfluorobutanoic acid (PFBA)
Perfluorodecanesulfonic acid (PFDS)
Perfluorodecanoic acid (PFDA)
6:2 FTS
8:2 FTS
9Cl PF3ONS
HFPO DA (GenX)
NEtFOSAA
Perfluorododecanoic acid (PFDoA)
Perfluoroheptanesulfonic Acid (PFHpS)
Perfluoroheptanoic acid (PFHpA)
375 92 8
763051 92 9
919005 14 4
757124 72 4
27619 97 2
39108 34 4
756426 58 1
13252 13 6
2991 50 6
2355 31 9
375 73 5
375 22 4
335 77 3
335 76 2
307 55 1
NE
60
NE
6000
NE
320 78805 1 Eurofins.xlsx 1 of 2 819AR00640
TABLE 6
EXCEEDANCE SUMMARY (PFAS)
TEST PIT LEACHATE
PHASE 1 DEVELOPMENT AREA
AIRPORT WEST VCP
JULY 2022
8/4/2022 2:23 PM
Client Sample ID Lab Sample ID Collection Date
NTL TP RR1 L NTL TP RR2 L NTL TP RR3 L NTL TP RR4 L NTL TP RR5 L NTL TP RR6 L NTL TP RR7 L NTL TP RR8 L NTL TP RR11 L
320 78805 1 320 78805 2 320 78805 3 320 78805 4 320 78805 5 320 78805 7 320 78805 8 320 78805 9 320 78805 10
Matrix Analysis Method Unit Analyte CAS PSL Values 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/3/2021 9/3/2021 9/3/2021 9/3/2021
Results ND 24 29 37 150 63 130 120 9.4
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 5.5 2.8 2.8 2.9 2.7 0.57 2.8 0.55 0.49
QualCode
Results 440 770 290 32 120 89 82 150 87
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 5.6 2.9 2.8 2.9 2.7 0.58 2.9 0.56 0.5
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 3.6 1.8 1.8 1.9 1.7 0.37 1.8 0.36 0.32
QualCode
Results ND ND 4 2 ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 2.6 1.3 1.3 1.4 1.3 0.27 1.3 0.26 0.23
QualCode J J
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 9.5 4.9 4.8 4.9 4.6 0.98 4.9 0.95 0.84
QualCode
Results 110 100 170 310 390 120 430 160 ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 5.2 2.7 2.6 2.7 2.5 0.54 2.7 0.52 0.46
QualCode
Results 400 530 420 150 240 94 270 190 31
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 8.2 4.2 4.1 4.3 4 0.85 4.2 0.82 0.73
QualCode
Results ND 14 ND 9 110 55 68 100 13
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 2.9 1.5 1.5 1.5 1.4 0.3 1.5 0.29 0.26
QualCode J
Results 68 82 170 24 84 88 63 120 34
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 4.7 2.4 2.4 2.5 2.3 0.49 2.4 0.47 0.42
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 7 3.6 3.6 3.7 3.4 0.73 3.6 0.71 0.63
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 13 6.5 6.3 6.5 6.1 1.3 6.5 1.3 1.1
QualCode
Results ND ND ND ND ND ND ND ND ND
PQL 19 10 9.7 10 9.3 2 10 1.9 1.7
MDL 11 5.5 5.4 5.5 5.1 1.1 5.5 1.1 0.94
QualCode
NOTES:
400 Result exceeds the PSL
ng/L nano gram per liter (ppt)
PSL Project Screening Level
PQL Laboratory Practical Quantitation Limit
MDL Laboratory Method Detection Limit
NTL Former North Temple Landfill
RR Railroad Aliagnment
NE Not Established
ND Not Detected above the MDL
QualCode Qualifier Definition
H Sample was prepped or analyzed beyond the specified holding time
I Value is EMPC (estimated maximum possible concentration).
J Result is less than the RL but greater than or equal to the MDL and the concentration is an approximate value.
355 46 4
307 24 4
68259 12 1
Perfluorotetradecanoic acid (PFTeA)
Perfluorotridecanoic acid (PFTrDA)
Perfluoropentanoic acid (PFPeA)
Perfluorohexanesulfonic acid (PFHxS)
Perfluorohexanoic acid (PFHxA)
Perfluorononanesulfonic acid (PFNS)
Perfluoroundecanoic acid (PFUnA)
Perfluorononanoic acid (PFNA)
Perfluorooctanesulfonamide (FOSA)
Perfluorooctanesulfonic acid (PFOS)
Perfluorooctanoic acid (PFOA)
Perfluoropentanesulfonic acid (PFPeS)
376 06 7
72629 94 8
2058 94 8
390
NE
375 95 1
754 91 6
1763 23 1
335 67 1
2706 91 4
2706 90 3
59
NE
40
60
NE
320 78805 1 Eurofins.xlsx 2 of 2 819AR00640
TABLE 7
PSL EXCEEDANCE SUMMARY (PFAS)
TEST PIT SOLIDS
PHASE 1 DEVELOPMENT AREA
AIRPORT WEST VCP
JULY 2022
8/4/2022 1:21 AM
Client Sample ID Lab Sample ID Collection Date
NTL TP RR1 NTL TP RR2 NTL TP RR3 NTL TP RR4 NTL TP RR5 NTL TP RR6 NTL TP RR7 NTL TP RR8 NTL TP RR10 NTL TP RR11 NTL TP RR16
320 78806 1 320 78806 2 320 78806 3 320 78806 4 320 78806 5 320 78806 6 320 78806 7 320 78806 8 320 78806 10 320 78806 11 320 78806 9
Matrix Analysis Method Unit Analyte PSL Values 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/3/2021 9/3/2021 9/3/2021 9/7/2021 9/7/2021 9/7/2021
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.045 0.044 0.04 0.043 0.038 0.055 0.038 0.042 0.043 0.036 0.036
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.056 0.055 0.05 0.054 0.048 0.069 0.048 0.053 0.054 0.046 0.046
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.073 0.072 0.066 0.071 0.063 0.091 0.063 0.069 0.071 0.06 0.06
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.039 0.038 0.035 0.038 0.033 0.048 0.033 0.037 0.038 0.032 0.032
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.05 0.049 0.045 0.049 0.043 0.062 0.043 0.047 0.049 0.041 0.041
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.05 0.049 0.045 0.049 0.043 0.062 0.043 0.047 0.049 0.041 0.041
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.059 0.058 0.053 0.057 0.05 0.073 0.051 0.055 0.057 0.048 0.048
QualCode
Result 0.41 1.5 0.23 0.26 1.5 6.1 0.16 2.3 ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.069 0.068 0.062 0.067 0.059 0.085 0.059 0.065 0.067 0.056 0.056
QualCode J J J
Result 0.034 0.11 ND 0.035 ND ND 0.028 ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.033 0.032 0.03 0.032 0.028 0.041 0.028 0.031 0.032 0.027 0.027
QualCode J J J J
Result ND ND ND ND 0.058 0.18 0.049 ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.055 0.054 0.049 0.053 0.047 0.068 0.047 0.051 0.053 0.045 0.045
QualCode J J J
Result 0.32 0.22 ND 0.14 0.17 0.22 ND 0.11 ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.066 0.065 0.059 0.064 0.057 0.082 0.057 0.062 0.064 0.054 0.054
QualCode J J J J J
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.075 0.073 0.067 0.072 0.064 0.093 0.064 0.07 0.073 0.061 0.061
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.069 0.068 0.062 0.067 0.059 0.085 0.059 0.065 0.067 0.056 0.056
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.043 0.042 0.039 0.042 0.037 0.053 0.037 0.041 0.042 0.035 0.035
QualCode
Result ND ND ND ND ND 0.2 ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.07 0.069 0.063 0.068 0.06 0.087 0.061 0.066 0.068 0.057 0.058
QualCode J
Result ND ND ND ND ND ND ND ND ND ND ND
NE
Perfluorodecanesulfonic acid (PFDS)
Perfluorodecanoic acid (PFDA)
Perfluorododecanoic acid (PFDoA)
Perfluoroheptanesulfonic Acid (PFHpS)
9Cl PF3ONS
HFPO DA (GenX)
NEtFOSAA
NMeFOSAA
Perfluorobutanesulfonic acid (PFBS)
Perfluorobutanoic acid (PFBA)
11Cl PF3OUdS
4,8 Dioxa 3H perfluorononanoic acid (ADONA)
4:2 FTS
6:2 FTS
8:2 FTS
NE
3500
NE
250000
320 78806 1 Eurofins.xlsx 1 of 2 819AR00640
TABLE 7
PSL EXCEEDANCE SUMMARY (PFAS)
TEST PIT SOLIDS
PHASE 1 DEVELOPMENT AREA
AIRPORT WEST VCP
JULY 2022
8/4/2022 1:21 AM
Client Sample ID Lab Sample ID Collection Date
NTL TP RR1 NTL TP RR2 NTL TP RR3 NTL TP RR4 NTL TP RR5 NTL TP RR6 NTL TP RR7 NTL TP RR8 NTL TP RR10 NTL TP RR11 NTL TP RR16
320 78806 1 320 78806 2 320 78806 3 320 78806 4 320 78806 5 320 78806 6 320 78806 7 320 78806 8 320 78806 10 320 78806 11 320 78806 9
Matrix Analysis Method Unit Analyte PSL Values 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/3/2021 9/3/2021 9/3/2021 9/7/2021 9/7/2021 9/7/2021
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.055 0.054 0.049 0.053 0.047 0.068 0.047 0.051 0.053 0.045 0.045
QualCode
Result ND ND ND ND 0.072 0.51 0.077 ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.042 0.041 0.037 0.04 0.036 0.052 0.036 0.039 0.04 0.034 0.034
QualCode J
Result 0.19 0.49 ND ND 0.044 0.28 ND 0.055 ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.045 0.044 0.04 0.043 0.038 0.055 0.038 0.042 0.043 0.036 0.036
QualCode J J J J
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.042 0.041 0.037 0.04 0.036 0.052 0.036 0.039 0.04 0.034 0.034
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.032 0.031 0.028 0.031 0.027 0.039 0.027 0.03 0.031 0.026 0.026
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.047 0.047 0.043 0.046 0.041 0.059 0.041 0.045 0.046 0.039 0.039
QualCode
Result 0.065 0.12 ND 0.59 0.78 8.9 0.27 0.65 ND ND 0.29
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.062 0.061 0.055 0.06 0.053 0.077 0.053 0.058 0.06 0.05 0.051
QualCode J J
Result 0.12 0.33 0.073 0.089 0.12 0.59 0.11 0.095 0.1 ND 0.08
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.076 0.075 0.068 0.074 0.065 0.094 0.065 0.072 0.074 0.062 0.062
QualCode J J J J J J J J
Result ND ND ND ND ND 0.15 ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.053 0.052 0.048 0.051 0.046 0.066 0.046 0.05 0.052 0.043 0.044
QualCode J
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.059 0.058 0.053 0.057 0.05 0.073 0.051 0.055 0.057 0.048 0.048
QualCode
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.053 0.052 0.048 0.051 0.046 0.066 0.046 0.05 0.052 0.043 0.044
QualCode
Result ND ND ND ND ND ND 0.039 ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.03 0.03 0.027 0.029 0.026 0.037 0.026 0.028 0.029 0.025 0.025
QualCode J
Result ND ND ND ND ND ND ND ND ND ND ND
PQL 0.29 0.28 0.26 0.28 0.25 0.36 0.25 0.27 0.28 0.23 0.24
MDL 0.06 0.059 0.054 0.058 0.052 0.075 0.052 0.057 0.059 0.049 0.049
QualCode
NOTES:
µg/Kg microgram per kilogram (ppb)
PSL Project Screening Level
PQL Laboratory Practical Quantitation Limit
MDL Laboratory Method Detection Limit
NTL Former North Temple Landfill
RR Railroad Aliagnment
NE Not Established
ND Not Detected above the MDL
QualCode Qualifier Definition
J Result is less than the RL but greater than or equal to the MDL and the concentration is an approximate value.
2500
NE
16000
NE
2500
NE
1600
Perfluorohexanoic acid (PFHxA)
Perfluorononanesulfonic acid (PFNS)
Perfluorononanoic acid (PFNA)
Perfluorooctanesulfonamide (FOSA)
Perfluorooctanesulfonic acid (PFOS)
Perfluorooctanoic acid (PFOA)
Perfluoroheptanoic acid (PFHpA)
Perfluorohexanesulfonic acid (PFHxS)
Perfluoropentanesulfonic acid (PFPeS)
Perfluoropentanoic acid (PFPeA)
Perfluorotetradecanoic acid (PFTeA)
Perfluorotridecanoic acid (PFTrDA)
Perfluoroundecanoic acid (PFUnA)
320 78806 1 Eurofins.xlsx 2 of 2 819AR00640
TABLE 8
PSL EXCEEDANCE SUMMARY
TEST PITS LEACHATE/SOLIDS
(Metals, VOCs, SVOCs)
PHASE 1 AREA DEVELOPMENT
AIRPORT WEST VCP
OCTOBER 2021
8/4/2022 11:08 AM
ClientSampID CollectionDate Lab Set
NTL TP RR1 NTL TP RR1 L NTL TP RR2 NTL TP RR2 L NTL TP RR3 NTL TP RR3 L NTL TP RR4 NTL TP RR4 L NTL TP RR5 NTL TP RR5 L NTL TP RR7 NTL TP RR7 L NTL TP RR8 NTL TP RR8 L NTL TP RR10 NTL TP RR11 NTL TP RR11 L NTL TP RR16
9/7/2021 9/7/2021
TestCode Analyte CAS Matrix Units Values 2109082 2109081 2109082 2109081 2109082 2109081 2109082 2109081 2109082 2109081 2109116 2109116 2109116 2109116 2109161 2109161 2109160 2109161
RESULT 14.6 7.76 15.4 17 11.6 8.63 27.8 11.2 9.14 14.8
PQL 0.665 0.779 0.718 0.717 0.678 0.661 0.733 0.569 0.613 0.635
MDL 0.182 0.213 0.196 0.196 0.185 0.181 0.2 0.155 0.167 0.173
PSL 3 3 3 3 3 3 3 3 3 3
QualCode 3
RESULT 0.153 0.014 0.0274 0.054 0.0178
PQL 0.004 0.004 0.004 0.004 0.004
MDL 0.00127 0.00127 0.00127 0.00127 0.00127
PSL 0.01 0.01 0.01 0.01 0.01
QualCode
RESULT 0.00519
PQL 0.0007
MDL 0.000136
PSL 0.005
QualCode
RESULT 3100
PQL 200
MDL 115
PSL
QualCode ~
RESULT 10.5 30.8 16.4 30.7 146
PQL 2 2 20 2 2
MDL 0.147 0.147 1.47 0.147 0.147
PSL 5 5 5 5 5
QualCode J
RESULT 216 6.4
PQL 20 20
MDL 4.51 4.51
PSL 5 5
QualCode B JB
RESULT 15.1
PQL 10
MDL 2.05
PSL 2
QualCode
RESULT 4060
PQL 20
MDL 3.26
PSL 200
QualCode
RESULT 58.3
PQL 20
MDL 7.82
PSL 7
QualCode
RESULT 691
PQL 20
MDL 7.85
PSL 5
QualCode
RESULT 75.9
PQL 20
MDL 1.88
PSL 70
QualCode
RESULT 97.3
PQL 20
MDL 4.58
PSL 5
QualCode *
RESULT 81.7
PQL 20
MDL 1.8
PSL 5
QualCode
9/3/2021 9/7/2021
Soil
Aqueous
mg/kg dry
mg/L
7440 38 2
7440 43 9
75 34 3
71 43 2
75 09 2
75 01 4
71 55 6
75 35 4
56 23 5
156 59 2
127 18 4
79 01 6
Arsenic
Cadmium
1,1 Dichloroethane
Benzene
Methylene chloride
Vinyl chloride
1,1,1 Trichloroethane
1,1 Dichloroethene
Carbon tetrachloride
cis 1,2 Dichloroethene
Tetrachloroethene
Trichloroethene
6020B S
6020B DIS
8260D W
9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/3/2021
AWAL detection_DKC_JRT_update.xlsx 1 OF 2 CARDNO 819AR00640
TABLE 8
PSL EXCEEDANCE SUMMARY
TEST PITS LEACHATE/SOLIDS
(Metals, VOCs, SVOCs)
PHASE 1 AREA DEVELOPMENT
AIRPORT WEST VCP
OCTOBER 2021
8/4/2022 11:08 AM
ClientSampID CollectionDate Lab Set
NTL TP RR1 NTL TP RR1 L NTL TP RR2 NTL TP RR2 L NTL TP RR3 NTL TP RR3 L NTL TP RR4 NTL TP RR4 L NTL TP RR5 NTL TP RR5 L NTL TP RR7 NTL TP RR7 L NTL TP RR8 NTL TP RR8 L NTL TP RR10 NTL TP RR11 NTL TP RR11 L NTL TP RR16
9/7/2021 9/7/2021
TestCode Analyte CAS Matrix Units Values 2109082 2109081 2109082 2109081 2109082 2109081 2109082 2109081 2109082 2109081 2109116 2109116 2109116 2109116 2109161 2109161 2109160 2109161
9/3/2021 9/7/20219/2/2021 9/2/2021 9/2/2021 9/2/2021 9/2/2021 9/3/2021
RESULT 393 128 70
PQL 500 50 50
MDL 215 21.5 21.5
PSL
QualCode J~
RESULT 4.31 13 8.54 3.7
PQL 0.3 0.3 0.3 3
MDL 0.18 0.18 0.18 1.8
PSL
QualCode
RESULT 5.11 4.15 280 36.3 1.76 1.11 1.38
PQL 0.497 0.49 95.2 0.502 2.44 0.477 0.486
MDL 0.102 0.101 19.6 0.103 0.503 0.0983 0.1
PSL 1.1 1.1 1.1 1.1 1.1 1.1 1.1
QualCode J @
RESULT 0.402 0.211
PQL 0.199 0.201
MDL 0.135 0.137
PSL 0.03 0.03
QualCode
RESULT 0.399 0.23
PQL 0.0995 0.115
MDL 0.0807 0.0932
PSL 0.2 0.2
QualCode @
RESULT 0.29
PQL 0.199
MDL 0.112
PSL 0.25
QualCode
RESULT 499 47.7
PQL 38.1 0.201
MDL 11.2 0.0589
PSL 36 36
QualCode
RESULT 38.8
PQL 57.1
MDL 20.9
PSL 25
QualCode J
RESULT 769 53.7
PQL 1900 10
MDL 217 1.14
PSL 36 36
QualCode J
RESULT 19.6 7.84
PQL 10 9.54
MDL 3.63 3.45
PSL 6 6
QualCode J
RESULT 18.3
PQL 48.9
MDL 6.6
PSL 12
QualCode J
NOTES:
PSL Project Screening Level
PQL Laboratory Practical Quantitation Limit
MDL Laboratory Method Detection Limit
SIM Laboratory Selected Ion Monitoring Method
NTL Former North Temple Landfill waste cell
TP Test Pit
RR Railroad Aliagnment
Qualifier Definition
J Estimated value between the MDL and the reporting limit (PQL).
B This analyte was also detected in the method blank below the PQL.
@ High RPD due to suspected sample non homogeneity or matrix interference.
1 Matrix spike recovery indicates matrix interference.The method is in control as indicated by the LCS.
$This compound exceeded (low)the control limit for the CCV.The compound concentration is estimated and may be biased low.
117 81 7
86 30 6
µg/L
50 32 8
205 99 2
91 57 6
218 01 9
91 57 6
N
Nitrosodiphenylamine
123 91 1
90 12 0
56 55 3
8270E W 3511
1,4 Dioxane
1 Methylnaphthalene
Benz(a)anthracene
8260D W SIM 1,4 Dxn
8270E W SIM 3511
Benzo(a)pyrene
Benzo(b)fluoranthene
2 Methylnaphthalene
Chrysene
2 Methylnaphthalene
Bis(2 ethylhexyl)
phthalate
AWAL detection_DKC_JRT_update.xlsx 2 OF 2 CARDNO 819AR00640

195 North 1950 West, 4th
Mailing -4820
Telephone [phone]
www.deq.utah.gov
Printed on 100% recycled paper
State of Utah

Department of
Environmental Quality

Kimberly D. Shelley
Executive Director

DIVISION OF AIR QUALITY
Bryce C. Bird
Director

SPENCER J. COX
Governor

DEIDRE HENDERSON
Lieutenant Governor
December 5, 2022 DAQA-472-22

Audra Heinzel and Julie Kilgore
Wasatch Environmental, Inc.
2410 West California Avenue
Salt Lake City, UT 84104

Dear Ms. Heinzel & Ms. Kilgore:

Re: Alternative Work Practice Request Airport West VCP Phase I Area Renovation Project

On November 22, 2022, the Utah Division of Air Quality (DAQ) received an alternative work practice
request (AWPR) from Wasatch Environmental, Inc./Audra Heinzel and Julie Kilgore for the Airport West
VCP Phase I Area Renovation located at 6500 West North Temple Frontage Road, Salt Lake City, Utah.
The DAQ has reviewed and has attached the accepted AWPR and you can start the project on the notified
start date or upon receipt of this signed letter, whichever is later.

Please ensure that the procedures listed in the AWPR are followed during this project. This AWPR
acceptance is only for those items specifically identified. All other applicable rules remain in effect for this
project.

Please contact Mike Zucker at [phone] or [e-mail] if you have any questions regarding
this letter.

Sincerely,

Bryce C. Bird
Director

BCB:MZ:lr

Stantec Consulting Services Inc.
2890 East Cottonwood Parkway
Suite 300
Salt Lake City UT 84121-7283
October 11, 2023
Project/File: 238000430
David Bird
Division of Environmental Response and Remediation
195 N 1950 W
Salt Lake City, UT 84116
Dear David,
Reference: Airport West VCP Phase I RAP Shotgun Shooting Range
Stantec is attaching information regarding the XRF results of scrape soil within the lead (Pb) impacted
areas within Phase I of the Airport West VCP remediation from the former shotgun shooting range. This
information is being provided to address the Pb impacted surface soils associated with the former shotgun
shooting range.
Please review and provide any comments, questions, or acceptance of these remedial actions.

Thank You,
STANTEC CONSULTING SERVICES INC.

David Cline P. E.
Sr. Environmental Engineer
Phone: [phone]
Mobile: [phone]
[e-mail]

Attachments:
1. Scrape Area Figures - Shotgun Shooting Range
2. Tables – Scraped Lead Shot Soil Stockpiles, XRF Summary
3. Analytical Lab Reports
cc Gary McEntee – NT Development
Eric Rice – NT Development
Background
The approved Airport West VCP Phase I Remedial Action Plan (Phase I RAP) identified a soil scrape of
impacted areas as a means to address the lead (Pb) contamination from the site of the former Shotgun
Shooting Range within the Phase I area. The RAP identified areas within Phase I to be included in the
scrape based upon the revised Former Sporting Shotgun Shooting Range Remedial Investigation Report
(Report) dated April 26, 2010, which was submitted by CDM to the UDERR and the SLVHD.
In preparation of the RAP, the XRF data (in-situ field samples and collected bulk samples) along with the
bulk sample laboratory confirmation data, that were collected and presented in the 2010 Report, (Table
3 – Lead Shot Content, XRF and Analytical Summary) identify the approximate locations of the Pb shot
scape areas (Figure A-11). The RAP also acknowledged that prior to initiating the remedial activities
UDERR and Stantec representatives would conduct a site visit and visual reconnaissance of the area to
determine the actual extent of the necessary soil scrape. The site reconnaissance was conducted on
May 11, 2023 by UDERR, Stantec and NT Development.
Prior to the planned site reconnaissance, the Utah Division of Environmental Remediation and Response
(UDERR) requested Stantec review the Report data and evaluate the amount of Pb shot mass to the dry
weight of the bulk soil sample as an alternative means to identify the areas requiring Pb soil scrape.
UDERR had previously identified an action level of 800 mg/kg for the intended Pb soil scrape based on
the EPA RSL value for non-carcinogenic screening level for industrial soil as 800 mg/kg.
Stantec provided UDERR with an evaluation showing the relationship of the laboratory data for Pb shot
pellets in the soil, reported as a percentage of the mass weight of the Pb pellets to the dry weight of the
bulk soil sample (ppm). A linear regression analysis was shown and plotted on the graph. For a percent
weight (Pb pellets to dry soil) of 800 ppm, the mass of Pb shot pellets equates to an approximate
amount of 3000 mg. With the corresponding bulk sample laboratory XRF data and confirmation
analytical results below the 800 mg/kg, it was proposed to remove the areas where Pb shot pellets were
above the 3000 mg.
In preparation for the site reconnaissance Stantec produced figures which were shared with UDERR to
show the locations where test samples were measured in the laboratory as over 3000 mg. These figures
and locations were reviewed on site as part of the May 11, 2023 site reconnaissance and subsequently
incorporated into the Stantec Airport West VCP – Phase I Area – Shotgun Shooting Range Scrape Plan
dated June 7, 2023 which was submitted to UDERR outlining the planned approach for the Pb scrape
portion of the site remediation efforts. UDERR issued their June 28,2023 letter accepting the Scrape Plan
under the VCP with the revised stipulation that areas exceeding the Pb shot pellet percent weight of 800
ppm were to be expanded into the proposed scrape areas. DERR’s rationale was that the entire mass
weight of Pb shot could fully leach into the soil over time.
Shotgun Shooting Range Scrape Efforts and Confirmation Sampling Results.
Approximately 36 acres within the Phase I area were scraped (Figure 2). The scraped areas north of the
former Brighton Canal were approximately 14 acres. The scraped areas south of the former Brighton
Canal were approximately 20 acres and the areas located in the southeast area total approximately 2
acres combined. The surface soil (a minimum of 4 inches) within the defined areas was scraped and
collected into small individual piles to allow for confirmation testing. Each soil pile was then tested in
accordance with the procedures set forth in the June 7, 2023 Scrape Plan.
The XRF testing results of the scaped piles are presented in Table 1 attached. Table 1 identifies the XRF
testing conducted on a total of 247 scrape piles. A total of 78 scrape piles south of the Brighton Canal
were tested for Pb, by XRF, with an average of 92 ppm. The XRF testing for Pb conducted on the 169
scrape piles, located east of the Bonneville Pile and those in the southeast area, recorded an average of
134 ppm.
A total of 16 laboratory confirmation tests (EPA SW-846 Method 6020), were completed to confirm the
XRF readings with the laboratory analysis and are presented in Table 1. The average Pb concentration
of the 6 lab samples for the 78 scrape piles south of the Brighton Canal is 73.3 mg/kg per dry weight
basis. The moisture content of the 6 lab samples averaged 8.8 %. The average Pb concentrations of the
10 lab samples for the 169 scraped piles east of the Bonneville Pile and areas in the southeast area is
202.3 mg/kg per dry weight basis. The moisture content of the 10 lab samples averaged 1.2 %. The drier
the XRF sample, the more accurate are the results when comparing field XRF measurements to
laboratory dry weight results. When the moisture content is between 5 and 20 percent the overall error
from moisture may be minimal (EPA SW-846 Method 6200). The soil dry weight values are considered
an actual representation of the concentration of the metal within the solid media and is the basis for the
regulatory action levels. However, there will exist a difference between the field concentration and the
laboratory dry weight basis due to the difference in moisture content. The laboratory dry weight result
is considered a higher concentration and therefore a more conservative value.
For Method 6200 data precision, multiple readings were taken on various samples. The relative
standard deviation (RSD) average for the precision sample readings was 2.2%. For field portable XRF
(FPXRF) data to be considered adequately precise, the RSD should not be greater than 20 percent.
For Method 6200 comparability analysis was determined by submitting a total of sixteen FPXRF analyzed
samples for laboratory analysis. The FPXRF samples were submitted from the middle range of
concentrations. A log-transformed data set was used due to the range of data ranging greater than an
order of magnitude. A linear regression analysis was performed on the log-transformed data. The
correlation coefficient (r) for the results was 0.86. The correlation coefficient (r) for the results should
be 0.7 or greater for the FPXRF data to be considered screening level data. If the (r) is 0.9 or greater
and inferential statistics indicate the FPXRF data and the confirmatory data are statistically equivalent at
a 99 percent confidence level, the data could potentially meet definitive level data criteria.
Soil Pile Groups
Avg. Soil Pile
Group XRF
Measurement
(ppm)
Sample ID.
(Soil Pile ID shown in
parentheses)
XRF
Measurement
(ppm)
Laboratory Result
(mg/kg) dry
weight
Relative
Percent
Difference
South 1-10 147.9 SSR1-(10) 80 92.4 14
South 11-20 96.5 SSR1-(20) 94 79.3 -17
South 21-30 81.6 SSR1-(30) 53 64.9 20
South 31-40 84.6 SSR1-(40) 52 77.8 40
Soil Pile Groups
Avg. Soil Pile
Group XRF
Measurement
(ppm)
Sample ID.
(Soil Pile ID shown in
parentheses)
XRF
Measurement
(ppm)
Laboratory Result
(mg/kg) dry
weight
Relative
Percent
Difference
South 41-57 82.4 -
South 100-110 90.8 SSR1-(105) 35 47.2 17
South 111-120 69.8 SSR1-(1)15 73 78.3 30
South2 1-22 68.7 AW COMP 1-22(11) 63 48.1 27
East 23-39 83.9 AW COMP 23-39(27) 74 36.3 -68
East 40-65 106.7 AW COMP 40-65(58) 101 559 139
Southeast 66-73 45.5 AW COMP 66-73(69) 77 103 29
East 74-76 40.3 AW COMP 74-76(74) 56 80.6 36
East 77-113 252.1 AW COMP 77-113(98) 170 184 8
East 114-135 81.0 AW COMP 114-135(124) 112 67 -50
East 136-146 38.8 AW COMP 136-146(142) 65 94.8 37
East 148-159 222.2 AW COMP 148-159(158) 109 366 108
East 160-169 209.6 AW COMP 160-169(161) 97 484 133
AVERAGE 106.02 82.7 153.9 27
Upon completion of the analytical testing the individual scrape piles were consolidated into a windrow
pile located west of the existing Bonniville waste pile.
Over an area approximately 36 acres, soil was scraped into 247 soil separate piles. Each pile was
sampled by collecting 3 sub-samples into a single composite sample. The composite sample was
measured by XRF for Pb. A split sample from a portion of the composite samples were analyzed for Pb
in a State of Utah certified laboratory. All samples were below the Project Action level (PAL) of 800
mg/kg. The XRF sample average submitted for the corresponding lab results was 82.7 ppm. The
corresponding laboratory sample average was 153.9 mg/kg. The laboratory sample results were
compared to their corresponding XRF composite sample. The relative percent difference average was
27.The laboratory quality control matrix spike and matrix spike duplicate limits should be set at +/-25 %
recovery and </= 20% RPD for EPA method 6020. The RSD was computed to be 2.2%. For the FPXRF
data to be considered adequately precise, the RSD should not be greater than 20 percent. The linear
regression analysis (r) value determined the FPXRF data to meet the screening level data criteria. The
samples are all below the PAL of 800 mg/kg. The Pb impacted soil was initially identified within the top
several inches. The impacted topsoil material has been removed and stockpiled. The levels of Pb in the
soil is below the EPA’s Regional Screening Level of 800 mg/kg for industrial soil. The area is considered
free of Pb impacted soil and is proposed as no further action.
N
DISCLAIMER: THIS PLAN IS INTENDED ONLY FOR CONCEPTUAL USE.
IT DOES NOT REFLECT THE EXACT LOCATION OF UTILITIES OR ANY
STRUCTURES. THIS DRAWING IS NOT INTENDED FOR USE IN
PERMITTING OR CONSTRUCTION. THIS CONCEPT PLAN IS
PROPERTY OF ET ENVIRONMENTAL.
0 300'1200'600'
1" = 300'
1500'
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2NR2
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E8.5 E10
GFE0
F9 3
3NRC
1NR9
7NR1
10NR1
3NRA
10NRA10NRB
1TS9
6TS9
7TS9
1TS8
3TS8
4TS8
5TS8
7TS8
1TS7
2TS7
5TS7
3TS6
1TS5
4TS5
2TS4
5TS4
1TS3
6TS3
1TS2
4TS2
1TS1
2TS1
BA5 BA9
BA10
BA11
BA12
BA7
BA3 BA4
7TS5 7TS7 7TS7TS1 7TS11
10NRC
3NRB
BA2BA1
6.5TS10 GFC2
GFB3
GFE2
GFC0
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GFBA
5.5TS8
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10NRD
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8TS8
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7NR10
3NR9
4NR9
5NR9
6NR9
7NR9
9NR9
10NR9
11NR9
12NR9
7NR8
10NR8
3NR7
7NR7
10NR7
3NR6
7NR6
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1NR5
2NR5
4NR5
5NR5
6NR5
7NR5
8NR5
9NR5
10NR5
11NR5
3NR4
7NR4
10NR4
12NR5
3NR3
7NR3
10NR3
4NR2
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I7 I8
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F2 F3 F11
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J2 J3 J4 J5 J6 J7 J8 J9 J10
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SL-10
SL-11
SL-12
SL-14
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SL-1
SL-13
SL-15
±0 500
Feet
SLR/NTL Former Sporting Clay Shooting Area
Salt Lake City, Utah
Data Sources: Images from
http://terraserver-usa.com/
Figure 2
Sampling Locations -
Overview Map
See Figure 3 and 6
See Figure 4 and 7
See Figure 5 and 8

June 2009 XRF
Ex Situ Sediment
Sample Locations
Legend
J7 March 2008 Field XRF
Surface Soil Sample
Locations
June 2009 Soil
Sample Locations
SED-1
#*
Metal Post
Approximate February
2006 UTEX Sample
Locations
(140)
")
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October 2008 Soil
Sample Locations
SL-11
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Lead Scraped Soil Stockpiles
XRF/Lab Measurements
Shotgun Shooting Range
Airport West VCP
10/12/2023
Stockpile Sample XRF Total Solids Lab Dry Weight
ID ppm % mg/kg
SOUTH BONNEVILLE PILE
1 197
2 303
3 107
474
5 121
6 197
7 280
857
963
10 80 88.0% 92.4
11 89
12 101
13 149
14 109
15 120
16 65
17 86
18 59
19 93
20 94 91.9% 79.3
21 86
22 90
23 65
24 83
25 92
26 130
27 54
28 84
29 79
30 53 89.4% 64.9
31 37
32 74
33 74
34 73
35 117
36 71
37 120
38 156
39 72
40 52 86.9% 77.8
41 52
42 49
43 97
44 95
45 55
46 87
47 83
48 149
49 146
50 38
51 206
52 97
53 55
54 58
55 43
56 50
57 40
100 271
101 130
102 86
103 73
104 197
105 35 95.6% 47.2
106 60
107 15
108 16
109 70
110 46
111 0
112 43
SOUTHEAST BONNEVILLE PILE
XRF Summary 247 samples 238000430.005
Lead Scraped Soil Stockpiles
XRF/Lab Measurements
Shotgun Shooting Range
Airport West VCP
10/12/2023
Stockpile Sample XRF Total Solids Lab Dry Weight
ID ppm % mg/kg
113 55
114 61
115 73 95.6% 78.3
116 0
117 29
118 33
119 372
120 32
SOUTH BONNEVILLE PILE
175
269
381
445
589
6ND
750
8 143
981
10 74
11 63 99.1% 48.1
12 143
13 66
14 65
15 57
16 34
17 50
18 81
19 95
20 80
21 48
22 22
EAST BONNEVILLE PILE
23 50
24 15
25 243
26 501
27 74 98.7% 36.3
28 304
29 24
30 28
31 39
32 36
33 ND
34 25
35 ND
36 ND
37 31
38 44
39 12
40 22
41 14
42 18
43 17
44 44
45 25
46 61
47 71
48 87
49 92
50 64
51 47
52 73
53 47
54 383
55 132
56 286
57 153
58 101 98.5% 559
59 101
60 249
61 332
62 177
XRF Summary 247 samples 238000430.005
Lead Scraped Soil Stockpiles
XRF/Lab Measurements
Shotgun Shooting Range
Airport West VCP
10/12/2023
Stockpile Sample XRF Total Solids Lab Dry Weight
ID ppm % mg/kg
63 58
64 69
65 51
SOUTHEAST SHOOTING RANGE AREA
66 52
67 46
68 49
69 77 99.0% 103
70 39
EAST BONNEVILLE PILE
71 42
72 37
73 22
74 56 99.1% 80.6
75 48
76 17
77 66
78 132
79 57
80 461
81 359
82 39
83 24
84 187
85 49
86 198
87 143
88 228
89 238
90 384
91 187
92 338
93 111
94 188
95 107
96 211
97 461
98 170 99.0% 184
99 318
100 684
101 746
102 579
103 503
104 63
105 91
106 369
107 248
108 567
109 725
110 20
111 21
112 56
113 ND
114 191
115 77
116 163
117 195
118 120
119 251
120 ND
121 63
122 25
123 87
124 112 98.9% 67
125 37
126 26
127 18
128 101
129 46
130 23
131 38
132 55
XRF Summary 247 samples 238000430.005
Lead Scraped Soil Stockpiles
XRF/Lab Measurements
Shotgun Shooting Range
Airport West VCP
10/12/2023
Stockpile Sample XRF Total Solids Lab Dry Weight
ID ppm % mg/kg
133 16
134 85
135 52
136 94
137 17
138 49
139 30
140 44
141 20
142 65 98.4% 94.8
143 3
144 20
145 44
146 41
147 810
148 42
149 174
150 249
151 120
152 177
153 219
154 211
155 423
156 149
157 61
158 109 98.5% 366
159 144
160 189
161 97 98.8% 484
162 265
163 292
164 231
165 198
166 51
167 268
168 124
169 381
RED indicates Brighton Canal Piles
XRF Summary 247 samples 238000430.005
ANALYTICAL REPORT
June 26, 2023
Stantec Consulting Corp - UT
Sample Delivery Group:L1627639
Samples Received:05/16/2023
Project Number:238000430.005A
Description:Airport West VCP SSR
Site:AIRPORT WEST VCP
Report To:David Cline
2890 East Cottonwood Parkway
Suite 300
Salt Lake City, UT 84121
Entire Report Reviewed By:
June 26, 2023
[Preliminary Report]
Chris Ward
Project Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be
reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace
Analytical National is performed per guidance provided in laboratory standard operating procedures ENV-SOP-MTJL-0067 and
ENV-SOP-MTJL-0068. Where sampling conducted by the customer, results relate to the accuracy of the information provided,
and as the samples are received.
Pace Analytical National
12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 www.pacenational.com
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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June 27, 2023
Jason Romer
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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TABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 3
Cn: Case Narrative 4
Sr: Sample Results 5
SSR1-10 L1627639-01 5
SSR1-20 L1627639-02 6
SSR1-30 L1627639-03 7
SSR1-40 L1627639-04 8
SSR1-105 L1627639-05 9
SSR1-115 L1627639-06 10
Qc: Quality Control Summary 11
Total Solids by Method 2540 G-2011 11
Metals (ICPMS) by Method 6020 12
Gl: Glossary of Terms 13
Al: Accreditations & Locations 14
Sc: Sample Chain of Custody 15
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
SSR1-10 L1627639-01 Solid Tom Garden 05/05/23 10:00 05/16/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2061549 1 05/18/23 11:55 05/18/23 12:07 MAS Mt. Juliet, TN
Metals (ICPMS) by Method 6020 WG2084335 5 06/26/23 08:50 06/26/23 18:11 LD Mt. Juliet, TN
Collected by Collected date/time Received date/time
SSR1-20 L1627639-02 Solid Tom Garden 05/05/23 00:00 05/16/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2061549 1 05/18/23 11:55 05/18/23 12:07 MAS Mt. Juliet, TN
Metals (ICPMS) by Method 6020 WG2084335 5 06/26/23 08:50 06/26/23 18:14 LD Mt. Juliet, TN
Collected by Collected date/time Received date/time
SSR1-30 L1627639-03 Solid Tom Garden 05/05/23 14:00 05/16/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2061549 1 05/18/23 11:55 05/18/23 12:07 MAS Mt. Juliet, TN
Metals (ICPMS) by Method 6020 WG2084335 5 06/26/23 08:50 06/26/23 18:18 LD Mt. Juliet, TN
Collected by Collected date/time Received date/time
SSR1-40 L1627639-04 Solid Tom Garden 05/05/23 16:00 05/16/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2061549 1 05/18/23 11:55 05/18/23 12:07 MAS Mt. Juliet, TN
Metals (ICPMS) by Method 6020 WG2084335 5 06/26/23 08:50 06/26/23 18:30 LD Mt. Juliet, TN
Collected by Collected date/time Received date/time
SSR1-105 L1627639-05 Solid Tom Garden 05/05/23 18:00 05/16/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2061549 1 05/18/23 11:55 05/18/23 12:07 MAS Mt. Juliet, TN
Metals (ICPMS) by Method 6020 WG2084335 5 06/26/23 08:50 06/26/23 18:33 LD Mt. Juliet, TN
Collected by Collected date/time Received date/time
SSR1-115 L1627639-06 Solid Tom Garden 05/05/23 20:00 05/16/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2061549 1 05/18/23 11:55 05/18/23 12:07 MAS Mt. Juliet, TN
Metals (ICPMS) by Method 6020 WG2084335 5 06/26/23 08:50 06/26/23 18:37 LD Mt. Juliet, TN
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the
appropriate preservatives, and within method specified holding times, unless qualified or notated within
the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples
have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control
are within established criteria except where addressed in this case narrative, a non-conformance form
or properly qualified within the sample results. By my digital signature below, I affirm to the best of my
knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the
quality of the data have been identified by the laboratory, and no information or data have been
knowingly withheld that would affect the quality of the data.
[Preliminary Report]
Chris Ward
Project Manager
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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Jason Romer
Project Manager
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SAMPLE RESULTS - 01
L1627639
SSR1-10
Collected date/time: 05/05/23 10:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 88.8 1 05/18/2023 12:07 WG2061549
Metals (ICPMS) by Method 6020
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 93.0 0.111 2.25 5 06/26/2023 18:11 WG2084335
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 02
L1627639
SSR1-20
Collected date/time: 05/05/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 91.9 1 05/18/2023 12:07 WG2061549
Metals (ICPMS) by Method 6020
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 71.0 0.108 2.18 5 06/26/2023 18:14 WG2084335
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 03
L1627639
SSR1-30
Collected date/time: 05/05/23 14:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 89.4 1 05/18/2023 12:07 WG2061549
Metals (ICPMS) by Method 6020
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 62.1 0.111 2.24 5 06/26/2023 18:18 WG2084335
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 04
L1627639
SSR1-40
Collected date/time: 05/05/23 16:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 86.9 1 05/18/2023 12:07 WG2061549
Metals (ICPMS) by Method 6020
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 89.3 0.114 2.30 5 06/26/2023 18:30 WG2084335
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 05
L1627639
SSR1-105
Collected date/time: 05/05/23 18:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 95.6 1 05/18/2023 12:07 WG2061549
Metals (ICPMS) by Method 6020
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 49.3 0.104 2.09 5 06/26/2023 18:33 WG2084335
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 06
L1627639
SSR1-115
Collected date/time: 05/05/23 20:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 95.6 1 05/18/2023 12:07 WG2061549
Metals (ICPMS) by Method 6020
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 87.0 0.104 2.09 5 06/26/2023 18:37 WG2084335
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2061549
Total Solids by Method 2540 G-2011 L1627639-01,02,03,04,05,06
Method Blank (MB)
(MB) R3926829-1 05/18/23 12:07
MB Result MB Qualifier MB MDL MB RDL
Analyte %%%
Total Solids 0.00100
L1616879-06 Original Sample (OS) • Duplicate (DUP)
(OS) L1616879-06 05/18/23 12:07 • (DUP) R3926829-3 05/18/23 12:07
Original Result DUP Result Dilution DUP RPD DUP Qualifier DUP RPD
Limits
Analyte %%%%
Total Solids 94.2 95.1 1 0.991 10
Laboratory Control Sample (LCS)
(LCS) R3926829-2 05/18/23 12:07
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte %%%%
Total Solids 50.0 50.0 100 85.0-115
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2084335
Metals (ICPMS) by Method 6020 L1627639-01,02,03,04,05,06
Method Blank (MB)
(MB) R3941487-1 06/26/23 17:00
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/kg mg/kg mg/kg
Lead 0.0269 J 0.0198 0.400
Laboratory Control Sample (LCS)
(LCS) R3941487-2 06/26/23 17:03
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte mg/kg mg/kg %%
Lead 100 88.8 88.8 80.0-120
L1625164-01 Original Sample (OS) • Matrix Spike (MS) • Matrix Spike Duplicate (MSD)
(OS) L1625164-01 06/26/23 17:07 • (MS) R3941487-5 06/26/23 17:17 • (MSD) R3941487-6 06/26/23 17:20
Spike Amount
(dry)
Original Result
(dry)MS Result (dry)MSD Result
(dry)MS Rec.MSD Rec.Dilution Rec. Limits MS Qualifier MSD Qualifier RPD RPD Limits
Analyte mg/kg mg/kg mg/kg mg/kg %%%%%
Lead 101 3.51 94.9 97.4 90.8 93.3 1 75.0-125 2.60 20
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
The information below is designed to better explain the various terms used in your report of analytical results from the Laboratory. This is not
intended as a comprehensive explanation, and if you have additional questions please contact your project representative.
Results Disclaimer - Information that may be provided by the customer, and contained within this report, include Permit Limits, Project Name,
Sample ID, Sample Matrix, Sample Preservation, Field Blanks, Field Spikes, Field Duplicates, On-Site Data, Sampling Collection Dates/Times, and
Sampling Location. Results relate to the accuracy of this information provided, and as the samples are received.
Abbreviations and Definitions
(dry)Results are reported based on the dry weight of the sample. [this will only be present on a dry report basis for soils].
MDL Method Detection Limit.
MDL (dry)Method Detection Limit.
RDL Reported Detection Limit.
RDL (dry)Reported Detection Limit.
Rec.Recovery.
RPD Relative Percent Difference.
SDG Sample Delivery Group.
Analyte The name of the particular compound or analysis performed. Some Analyses and Methods will have multiple analytes
reported.
Dilution
If the sample matrix contains an interfering material, the sample preparation volume or weight values differ from the
standard, or if concentrations of analytes in the sample are higher than the highest limit of concentration that the
laboratory can accurately report, the sample may be diluted for analysis. If a value different than 1 is used in this field, the
result reported has already been corrected for this factor.
Limits
These are the target % recovery ranges or % difference value that the laboratory has historically determined as normal
for the method and analyte being reported. Successful QC Sample analysis will target all analytes recovered or
duplicated within these ranges.
Original Sample The non-spiked sample in the prep batch used to determine the Relative Percent Difference (RPD) from a quality control
sample. The Original Sample may not be included within the reported SDG.
Qualifier
This column provides a letter and/or number designation that corresponds to additional information concerning the result
reported. If a Qualifier is present, a definition per Qualifier is provided within the Glossary and Definitions page and
potentially a discussion of possible implications of the Qualifier in the Case Narrative if applicable.
Result
The actual analytical final result (corrected for any sample specific characteristics) reported for your sample. If there was
no measurable result returned for a specific analyte, the result in this column may state “ND” (Not Detected) or “BDL”
(Below Detectable Levels). The information in the results column should always be accompanied by either an MDL
(Method Detection Limit) or RDL (Reporting Detection Limit) that defines the lowest value that the laboratory could detect
or report for this analyte.
Uncertainty
(Radiochemistry)Confidence level of 2 sigma.
Case Narrative (Cn)
A brief discussion about the included sample results, including a discussion of any non-conformances to protocol
observed either at sample receipt by the laboratory from the field or during the analytical process. If present, there will
be a section in the Case Narrative to discuss the meaning of any data qualifiers used in the report.
Quality Control
Summary (Qc)
This section of the report includes the results of the laboratory quality control analyses required by procedure or
analytical methods to assist in evaluating the validity of the results reported for your samples. These analyses are not
being performed on your samples typically, but on laboratory generated material.
Sample Chain of
Custody (Sc)
This is the document created in the field when your samples were initially collected. This is used to verify the time and
date of collection, the person collecting the samples, and the analyses that the laboratory is requested to perform. This
chain of custody also documents all persons (excluding commercial shippers) that have had control or possession of the
samples from the time of collection until delivery to the laboratory for analysis.
Sample Results (Sr)
This section of your report will provide the results of all testing performed on your samples. These results are provided
by sample ID and are separated by the analyses performed on each sample. The header line of each analysis section for
each sample will provide the name and method number for the analysis reported.
Sample Summary (Ss)This section of the Analytical Report defines the specific analyses performed for each sample ID, including the dates and
times of preparation and/or analysis.
Qualifier Description
J The identification of the analyte is acceptable; the reported value is an estimate.
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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Pace Analytical National 12065 Lebanon Rd Mount Juliet, TN 37122
Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN000032021-1
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹TN00003
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹DW21704
Georgia NELAP North Carolina ³41
Georgia ¹923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶KY90010 South Carolina 84004002
Kentucky ²16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴2006
Louisiana LA018 Texas T104704245-20-18
Maine TN00003 Texas ⁵LAB0152
Maryland 324 Utah TN000032021-11
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 110033
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 998093910
Montana CERT0086 Wyoming A2LA
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS

¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace Analytical.
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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ANALYTICAL REPORT
August 13, 2023
Stantec Consulting Corp - UT
Sample Delivery Group:L1642211
Samples Received:08/03/2023
Project Number:
Description:Airport West-Gun Range
Report To:David Cline
2890 East Cottonwood Parkway
Suite 300
Salt Lake City, UT 84121
Entire Report Reviewed By:
August 13, 2023
[Preliminary Report]
Chris Ward
Project Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be
reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace
Analytical National is performed per guidance provided in laboratory standard operating procedures ENV-SOP-MTJL-0067 and
ENV-SOP-MTJL-0068. Where sampling conducted by the customer, results relate to the accuracy of the information provided,
and as the samples are received.
Pace Analytical National
12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 www.pacenational.com
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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August 14, 2023
Chris Ward
Project Manager
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TABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 3
Cn: Case Narrative 5
Sr: Sample Results 6
AW-COMP 1-22 L1642211-01 6
AW-COMP 23-39 L1642211-02 7
AW-COMP 40-65 L1642211-03 8
AW-COMP 66-73 L1642211-04 9
AW-COMP 74-76 L1642211-05 10
AW-COMP 77-113 L1642211-06 11
AW-COMP 114-135 L1642211-07 12
AW-COMP 136-146 L1642211-08 13
AW-COMP 148-159 L1642211-09 14
AW-COMP 160-169 L1642211-10 15
Qc: Quality Control Summary 16
Total Solids by Method 2540 G-2011 16
Metals (ICP) by Method 6010B 18
Gl: Glossary of Terms 20
Al: Accreditations & Locations 21
Sc: Sample Chain of Custody 22
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
AW-COMP 1-22 L1642211-01 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107944 1 08/04/23 15:46 08/04/23 16:01 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:14 ZSA Mt. Juliet, TN
Collected by Collected date/time Received date/time
AW-COMP 23-39 L1642211-02 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107944 1 08/04/23 15:46 08/04/23 16:01 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:17 ZSA Mt. Juliet, TN
Collected by Collected date/time Received date/time
AW-COMP 40-65 L1642211-03 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107944 1 08/04/23 15:46 08/04/23 16:01 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:20 ZSA Mt. Juliet, TN
Collected by Collected date/time Received date/time
AW-COMP 66-73 L1642211-04 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107944 1 08/04/23 15:46 08/04/23 16:01 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:29 ZSA Mt. Juliet, TN
Collected by Collected date/time Received date/time
AW-COMP 74-76 L1642211-05 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107944 1 08/04/23 15:46 08/04/23 16:01 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:32 ZSA Mt. Juliet, TN
Collected by Collected date/time Received date/time
AW-COMP 77-113 L1642211-06 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107944 1 08/04/23 15:46 08/04/23 16:01 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:35 ZSA Mt. Juliet, TN
Collected by Collected date/time Received date/time
AW-COMP 114-135 L1642211-07 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107944 1 08/04/23 15:46 08/04/23 16:01 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:38 ZSA Mt. Juliet, TN
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
AW-COMP 136-146 L1642211-08 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107948 1 08/04/23 15:27 08/04/23 15:44 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:41 ZSA Mt. Juliet, TN
Collected by Collected date/time Received date/time
AW-COMP 148-159 L1642211-09 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107948 1 08/04/23 15:27 08/04/23 15:44 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107745 1 08/04/23 12:52 08/07/23 17:44 ZSA Mt. Juliet, TN
Collected by Collected date/time Received date/time
AW-COMP 160-169 L1642211-10 Solid Tom Gordon 07/29/23 00:00 08/03/23 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2107948 1 08/04/23 15:27 08/04/23 15:44 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2107965 1 08/04/23 16:47 08/11/23 20:02 ZSA Mt. Juliet, TN
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the
appropriate preservatives, and within method specified holding times, unless qualified or notated within
the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples
have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control
are within established criteria except where addressed in this case narrative, a non-conformance form
or properly qualified within the sample results. By my digital signature below, I affirm to the best of my
knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the
quality of the data have been identified by the laboratory, and no information or data have been
knowingly withheld that would affect the quality of the data.
[Preliminary Report]
Chris Ward
Project Manager
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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Chris Ward
Project Manager
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SAMPLE RESULTS - 01
L1642211
AW-COMP 1-22
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 99.1 1 08/04/2023 16:01 WG2107944
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 48.1 0.210 0.505 1 08/07/2023 17:14 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 02
L1642211
AW-COMP 23-39
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 98.7 1 08/04/2023 16:01 WG2107944
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 36.3 0.211 0.507 1 08/07/2023 17:17 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 03
L1642211
AW-COMP 40-65
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 98.5 1 08/04/2023 16:01 WG2107944
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 559 0.211 0.508 1 08/07/2023 17:20 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 04
L1642211
AW-COMP 66-73
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 99.0 1 08/04/2023 16:01 WG2107944
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 103 0.210 0.505 1 08/07/2023 17:29 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 05
L1642211
AW-COMP 74-76
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 99.1 1 08/04/2023 16:01 WG2107944
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 80.6 0.210 0.504 1 08/07/2023 17:32 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 06
L1642211
AW-COMP 77-113
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 99.0 1 08/04/2023 16:01 WG2107944
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 184 0.210 0.505 1 08/07/2023 17:35 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 07
L1642211
AW-COMP 114-135
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 98.9 1 08/04/2023 16:01 WG2107944
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 67.0 0.210 0.506 1 08/07/2023 17:38 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 08
L1642211
AW-COMP 136-146
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 98.4 1 08/04/2023 15:44 WG2107948
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 94.8 0.211 0.508 1 08/07/2023 17:41 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 09
L1642211
AW-COMP 148-159
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 98.5 1 08/04/2023 15:44 WG2107948
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 366 0.211 0.508 1 08/07/2023 17:44 WG2107745
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 10
L1642211
AW-COMP 160-169
Collected date/time: 07/29/23 00:00
Total Solids by Method 2540 G-2011
Result Qualifier Dilution Analysis Batch
Analyte %date / time
Total Solids 98.8 1 08/04/2023 15:44 WG2107948
Metals (ICP) by Method 6010B
Result (dry)Qualifier MDL (dry)RDL (dry)Dilution Analysis Batch
Analyte mg/kg mg/kg mg/kg date / time
Lead 484 J3 V 0.211 0.506 1 08/11/2023 20:02 WG2107965
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2107944
Total Solids by Method 2540 G-2011 L1642211-01,02,03,04,05,06,07
Method Blank (MB)
(MB) R3957216-1 08/04/23 16:01
MB Result MB Qualifier MB MDL MB RDL
Analyte %%%
Total Solids 0.00100
L1642211-06 Original Sample (OS) • Duplicate (DUP)
(OS) L1642211-06 08/04/23 16:01 • (DUP) R3957216-3 08/04/23 16:01
Original Result DUP Result Dilution DUP RPD DUP Qualifier DUP RPD
Limits
Analyte %%%%
Total Solids 99.0 99.1 1 0.148 10
Laboratory Control Sample (LCS)
(LCS) R3957216-2 08/04/23 16:01
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte %%%%
Total Solids 50.0 50.0 100 85.0-115
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2107948
Total Solids by Method 2540 G-2011 L1642211-08,09,10
Method Blank (MB)
(MB) R3957215-1 08/04/23 15:44
MB Result MB Qualifier MB MDL MB RDL
Analyte %%%
Total Solids 0.000
L1642211-09 Original Sample (OS) • Duplicate (DUP)
(OS) L1642211-09 08/04/23 15:44 • (DUP) R3957215-3 08/04/23 15:44
Original Result DUP Result Dilution DUP RPD DUP Qualifier DUP RPD
Limits
Analyte %%%%
Total Solids 98.5 98.7 1 0.171 10
Laboratory Control Sample (LCS)
(LCS) R3957215-2 08/04/23 15:44
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte %%%%
Total Solids 50.0 50.0 100 85.0-115
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2107745
Metals (ICP) by Method 6010B L1642211-01,02,03,04,05,06,07,08,09
Method Blank (MB)
(MB) R3957869-1 08/07/23 16:18
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/kg mg/kg mg/kg
Lead U 0.208 0.500
Laboratory Control Sample (LCS)
(LCS) R3957869-2 08/07/23 16:21
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte mg/kg mg/kg %%
Lead 100 90.1 90.1 80.0-120
L1640455-01 Original Sample (OS) • Matrix Spike (MS) • Matrix Spike Duplicate (MSD)
(OS) L1640455-01 08/07/23 16:24 • (MS) R3957869-5 08/07/23 16:33 • (MSD) R3957869-6 08/07/23 16:36
Spike Amount Original Result MS Result MSD Result MS Rec.MSD Rec.Dilution Rec. Limits MS Qualifier MSD Qualifier RPD RPD Limits
Analyte mg/kg mg/kg mg/kg mg/kg %%%%%
Lead 100 1.00 95.9 97.8 94.9 96.8 1 75.0-125 1.89 20
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2107965
Metals (ICP) by Method 6010B L1642211-10
Method Blank (MB)
(MB) R3959948-1 08/11/23 19:56
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/kg mg/kg mg/kg
Lead U 0.208 0.500
Laboratory Control Sample (LCS)
(LCS) R3959948-2 08/11/23 19:59
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte mg/kg mg/kg %%
Lead 100 86.5 86.5 80.0-120
L1642211-10 Original Sample (OS) • Matrix Spike (MS) • Matrix Spike Duplicate (MSD)
(OS) L1642211-10 08/11/23 20:02 • (MS) R3959948-5 08/11/23 20:11 • (MSD) R3959948-6 08/11/23 20:14
Spike Amount
(dry)
Original Result
(dry)MS Result (dry)MSD Result
(dry)MS Rec.MSD Rec.Dilution Rec. Limits MS Qualifier MSD Qualifier RPD RPD Limits
Analyte mg/kg mg/kg mg/kg mg/kg %%%%%
Lead 101 484 409 666 0.000 180 1 75.0-125 V J3 V 47.9 20
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
The information below is designed to better explain the various terms used in your report of analytical results from the Laboratory. This is not
intended as a comprehensive explanation, and if you have additional questions please contact your project representative.
Results Disclaimer - Information that may be provided by the customer, and contained within this report, include Permit Limits, Project Name,
Sample ID, Sample Matrix, Sample Preservation, Field Blanks, Field Spikes, Field Duplicates, On-Site Data, Sampling Collection Dates/Times, and
Sampling Location. Results relate to the accuracy of this information provided, and as the samples are received.
Abbreviations and Definitions
(dry)Results are reported based on the dry weight of the sample. [this will only be present on a dry report basis for soils].
MDL Method Detection Limit.
MDL (dry)Method Detection Limit.
RDL Reported Detection Limit.
RDL (dry)Reported Detection Limit.
Rec.Recovery.
RPD Relative Percent Difference.
SDG Sample Delivery Group.
U Not detected at the Reporting Limit (or MDL where applicable).
Analyte The name of the particular compound or analysis performed. Some Analyses and Methods will have multiple analytes
reported.
Dilution
If the sample matrix contains an interfering material, the sample preparation volume or weight values differ from the
standard, or if concentrations of analytes in the sample are higher than the highest limit of concentration that the
laboratory can accurately report, the sample may be diluted for analysis. If a value different than 1 is used in this field, the
result reported has already been corrected for this factor.
Limits
These are the target % recovery ranges or % difference value that the laboratory has historically determined as normal
for the method and analyte being reported. Successful QC Sample analysis will target all analytes recovered or
duplicated within these ranges.
Original Sample The non-spiked sample in the prep batch used to determine the Relative Percent Difference (RPD) from a quality control
sample. The Original Sample may not be included within the reported SDG.
Qualifier
This column provides a letter and/or number designation that corresponds to additional information concerning the result
reported. If a Qualifier is present, a definition per Qualifier is provided within the Glossary and Definitions page and
potentially a discussion of possible implications of the Qualifier in the Case Narrative if applicable.
Result
The actual analytical final result (corrected for any sample specific characteristics) reported for your sample. If there was
no measurable result returned for a specific analyte, the result in this column may state “ND” (Not Detected) or “BDL”
(Below Detectable Levels). The information in the results column should always be accompanied by either an MDL
(Method Detection Limit) or RDL (Reporting Detection Limit) that defines the lowest value that the laboratory could detect
or report for this analyte.
Uncertainty
(Radiochemistry)Confidence level of 2 sigma.
Case Narrative (Cn)
A brief discussion about the included sample results, including a discussion of any non-conformances to protocol
observed either at sample receipt by the laboratory from the field or during the analytical process. If present, there will
be a section in the Case Narrative to discuss the meaning of any data qualifiers used in the report.
Quality Control
Summary (Qc)
This section of the report includes the results of the laboratory quality control analyses required by procedure or
analytical methods to assist in evaluating the validity of the results reported for your samples. These analyses are not
being performed on your samples typically, but on laboratory generated material.
Sample Chain of
Custody (Sc)
This is the document created in the field when your samples were initially collected. This is used to verify the time and
date of collection, the person collecting the samples, and the analyses that the laboratory is requested to perform. This
chain of custody also documents all persons (excluding commercial shippers) that have had control or possession of the
samples from the time of collection until delivery to the laboratory for analysis.
Sample Results (Sr)
This section of your report will provide the results of all testing performed on your samples. These results are provided
by sample ID and are separated by the analyses performed on each sample. The header line of each analysis section for
each sample will provide the name and method number for the analysis reported.
Sample Summary (Ss)This section of the Analytical Report defines the specific analyses performed for each sample ID, including the dates and
times of preparation and/or analysis.
Qualifier Description
J3 The associated batch QC was outside the established quality control range for precision.
V The sample concentration is too high to evaluate accurate spike recoveries.
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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Pace Analytical National 12065 Lebanon Rd Mount Juliet, TN 37122
Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN000032021-1
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹TN00003
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹DW21704
Georgia NELAP North Carolina ³41
Georgia ¹923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶KY90010 South Carolina 84004002
Kentucky ²16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴2006
Louisiana LA018 Texas T104704245-20-18
Maine TN00003 Texas ⁵LAB0152
Maryland 324 Utah TN000032021-11
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 110033
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 998093910
Montana CERT0086 Wyoming A2LA
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS

¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace Analytical.
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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APPENDIX E
CREDENTIALS

Ellie Roubal
Field Geologist
PROFESSIONAL EXPERIENCE
Ellie is a Field Geologist for the Environmental Department of the Salt Lake
Terracon office. She evaluates and interprets field, sampling data, reports,
maps, drawings, tests, and aerial photographs to develop conclusions
concerning recognized environmental conditions (RECs). Ellie also writes
reports of significant findings to help the client assess the property in
question.
Terracon’s Incident and Injury Free® safety goals align with Ellie’s values
and concern for performance in all aspects of her job and personal life. She
is diligent and versatile. Ellie is interested in environmental conservation,
marine research, and building effective relationships within her workplace.
Ellie also speaks some French and Italian.
PROJECT EXPERIENCE
Confidential ESA—Salt Lake City, Utah
Ellie performed field work on this Phase I Environmental Site Assessment
(ESA) for a National Terracon Account to assess RECs on an existing
property. This property had added challenges of vapor encroachment,
impacts from a nearby landfill. Sub-slab soil had concentrations exceeding
target vapor intrusion screening levels (VISLs) with air sample
concentrations below the United States Environmental Protection Agency
(EPA) Regional Screening Levels (RSLs). Ellie performed the site
reconnaissance and research to develop a report of findings. She researched
several previous reports of air and soil testing on site and databases that
included a wetlands study, topographical and aerial maps, city directories,
title search, and lien information to formulate findings concerning the
property. The report recommended that the Client conduct indoor air
sampling and develop a Spill Prevention, Control, and Countermeasure
(SPCC) plan.
Proposed Student Housing—Salt Lake City, Utah
This ESA was done on this urban property that included multiple commercial spaces being developed into
apartments. Ellie performed the site reconnaissance and research to develop a report of findings. She
researched databases that included Sanborn, topographical and aerial maps, city directories, a title search,
and lien information concerning the property. The earliest record of the site showed development of the area
since at least 1898. Federal and state databases revealed quite a few listed properties that needed to be
assessed for impacts. Ellie used strong attention to detail in the research of large historical databases in the
development of a tabletop assessment for this site, and provided a continuous narrative of the evolving and
dense city block.
Owned Warehouse—Price, Utah
Ellie acted as the field geologist for this Phase I ESA on a former beverage distribution warehouse slated for
renovation or development. She gathered observations of the property by conducting a site walk with the Unit
General Manager where she identified evidence of former storage tanks, subgrade mechanic pits, and
EDUCATION
Bachelor of Science, Geology &
Environmental Science,
University of Michigan
Ann Arbor, MI, 2023
REGISTRATIONS/
CERTIFICATIONS
UDEQ Soil and Groundwater
Sampler, ID# GS-1953
PROFESSIONAL TRAINING
OSHA 10-Hour Health & Safety
HAZWOPER 40-Hour, pending
completion in December 2024
Union Pacific Fiber Optics
Safety Trained, 2024
ArcGIS Pro software application
*Project Experience prior to
Terracon employment
Ellie Roubal Cont.

hydraulic lifts then evaluated for possible RECs. Ellie sought local knowledge and surveyed historical and
government databases to develop recommendations regarding impacts to the site.
Mountain View Corridor and 126th South ESA—Riverton, Utah
This Phase I ESA was conducted for a National Terracon Account to assess RECs for proposed development.
Ellie worked as a field geologist, performing site reconnaissance and research to develop the report of
findings. She conducted tabletop research of topographical and aerial maps, city directories, title search, and
lien information to formulate findings concerning the property.
*Geothermal Exploration Project—Salt Lake City, Utah
Ellie worked as a field geology technician, collecting over 1000 geothermal temperature data points while
maintaining the standard methods for field sampling. She then digitized and analyzed her findings with keen
attention to detail and submitted standardized reports nightly to aid in creating a comprehensive map of
regional geothermal activity. Ellie collaborated with one other technician for 14-day shifts in remote settings.
She developed mechanical knowledge by inspecting and maintaining equipment and problem-solving with
finite resources. She worked with integrity and high self-motivation.
*Camp Davis, Rocky Mountain Field Station—Jackson, Wyoming
This project required fieldwork where Ellie and a small team designed and conducted experiments on the local
impacts from recent landslides and wildfires. She learned from experts in the field and was able to practice
field-standard methods of data collection. Responsibilities included working productively and cooperatively in
an isolated environment to produce a professional report analyzing the team’s findings and drawing
conclusions with respect to environmental, geologic, and sociopolitical factors.

Christina (Tina) Cheney
ESA Group Manager
PROFESSIONAL EXPERIENCE
Tina has 20 years of experience performing Phase I Environmental Site
Assessments (ESAs) for multiple clients, including auto shops/gasoline
stations, residential properties, dairy farms, restaurants, industrial
properties, medical facilities, retail properties, and agricultural properties
throughout multiple states. Phase I ESA report completion is often needed to
complete the sale of commercial property. For less-suspect properties, she
has performed and managed Transaction Screen Assessments and
Regulatory Database Reviews. Understanding the limits of those studies',
recommendations were sometimes needed to transition to a Phase I ESA
when Potential Environmental Conditions should be more thoroughly
researched, evaluated, and discussed. Tina has been part of the Terracon
Practice Resource Group for Due Diligence since 2018. She became an
Authorized Project Reviewer in 2021. In 2023, Tina became a Co-National
Account Manager for a large, Confidential International Nonprofit
Corporation.
Her specific expertise includes environmental site assessments and surface
and groundwater contamination assessments including prevention,
monitoring, and control. Tina also conducts risk assessments, risk reduction
recommendations, and other areas of expertise relating to hazardous
substances and waste management.
PROJECT EXPERIENCE
Salt Lake City Corporation—Salt Lake City, Utah
Tina has managed Phase I ESAs for Salt Lake City Corporation for 10 years.
She has served as a project manager and group manager. She reviewed
historical records from federal, state, and local agency databases. Tina also
conducted interviews, site inspections, and authored reports.
Salt Lake County—Salt Lake City, Utah
As a specialist in Phase I assessments, Tina has a long history of working for Salt Lake County, which included
several Brownfield Projects. She has served as a Project Manager and Group Manager on these projects. She
conducted interviews and site inspections that identified recognized environmental conditions (RECs) and
authored reports after reviewing historical and county records from federal, state, and local agency databases.
Large, Confidential International Nonprofit Corporation—Throughout the United States
Tina has managed Phase I ESAs throughout the country for this large, confidential nonprofit international
corporation. She reviewed historical records, from federal, state, and local agency databases. Tina conducted
site inspections and authored reports. She acted as an authorized project reviewer and national account
manager for reports written by other environmental professionals.

EDUCATION
Bachelor of Science, Brigham
Young University, Recreation
Management & Leisure
Services, 2002
Associate of Science, Ricks
College, Electronics Engineering
Technology, 1999
Associates of Science, Ricks
College, Computer Systems
Technology, 1999
REGISTRATIONS/
CERTIFICATIONS
Former Registered
Environmental Assessor
#30103 (2008-2012)
AHERA: Building Inspector
Union Pacific Fiber Optics
Safety Trained, 2023

Confidential—National (2019)
This project started as a multi-site portfolio for a local law firm, including Phase I ESAs on sites in thirteen
states. Tina managed the initial project and the transition as some sites progressed into soil, groundwater, soil
vapor, asbestos, and mold sampling.
University of Utah—Several locations in Utah
Tina was the Project and Group Manager for several Phase I ESAs for the University of Utah. She has reviewed
historical records from federal, state, and local agency databases, conducted interviews and co-authored the
reports.
Murray City Redevelopment Agency—Murray, Utah
As Project and Group Manager, Tina oversaw several Phase I ESAs for the City of Murray. She has reviewed
historical documents, county records, and regulatory databases. Tina conducted interviews and authored the
reports.
Windermere Real Estate—Several locations in Utah
Tina served as Project and Group Manager for several Phase I ESAs for Windermere Real Estate. She
conducted interviews and site inspections that identified RECs, and she co-authored reports.
Wadsworth Development Group—Several locations in Utah
Tina served as Project Manager and Group Manager for several Phase I ESAs for Wadsworth Development
Group. She has reviewed historical records from federal, state, and local agency databases; conducted
interviews; and authored the reports.
Sears Phase I ESAs—California and Utah
During several concurrent Phase I ESAs for Sears, Tina acted as Project Manager. Her team reviewed historical
records from federal, state, and local agency databases. They conducted interviews and co-authored the
reports. RECs were identified, and a Phase II ESA was recommended on several sites.
Ensign Group, Senior Care Facilities—Various Locations in Utah
Tina served as Project Manager for several concurrent Phase I ESAs for senior-care facilities in Utah. She
reviewed historical records from federal, state, and local agency databases, conducted interviews and
authored the reports.
Confidential Project—Downtown Salt Lake City, Utah
As Project Manager, Tina identified a former gas station at the site by reviewing historical records, and
recommended a Phase II ESA.
Parkway Commons—Murray, Utah
Tina served as Project Manager for the Phase I ESAs and limited sampling at the Parkway Commons in
Murray, Utah. Sampling included radon, lead in water, and asbestos. She reviewed historical records from
federal, state, and local agency databases.

Wells Fargo Bank—Various Locations in Utah
Wells Fargo requested several Phase I ESAs throughout Utah that needed to include visual and limited
sampling for asbestos at some sites. Tina served as Project Manager, conducting interviews, and authoring the
reports after reviewing historical documents, county records, and regulatory databases.
Cobalt Phase I ESAs—Salt Lake City, Utah
Tina identified numerous RECs, and a Phase II ESA was recommended on several industrial properties in the
Salt Lake Valley. As an assistant for several concurrent Phase I ESAs, Tina reviewed historical and county
records from federal, state, and local agency databases, conducted interviews, and co -authored the reports.
Madera High School—Madera, California
Tina provided an environmental assessment for the construction of a new high school in Madera, California.
Neil O. Anderson & Associates was the premier agent in performing the Initial Study, Preliminary
Environmental Assessment (PEA), and Removal Action (RA) Reports for the site. Tina reviewed the Initial
Study and worked with the Project Manager on the write-up of the PEA Workplan, PEA, RA Workplan, and RA
report.
Chinchiolo Stemilt Groundwater Monitoring—Stockton, California
As a staff scientist on this project, Tina was involved in quarterly and annual monitoring for the Central Valley
Regional Water Quality Control Board. Responsibilities included creating groundwater contour maps from data
collected from on-site monitoring wells, calculating the flow direction and hydraulic gradient of groundwater at
the subject property, and interpreting analytical data. Tina also compiled quarterly and annual reports.
APPENDIX F
DESCRIPTION OF TERMS AND ACRONYMS
Description of Selected General Terms and Acronyms
Facilities | Environmental | Geotechnical | Materials 1
Term/Acronym Description
ACM
Asbestos Containing Material. Asbestos is a naturally occurring mineral, three varieties of which (chrysotile,
amosite, crocidolite) have been commonly used as fireproofing or binding agents in construction materials.
Exposure to asbestos, as well as ACM, has been documented to cause lung diseases including asbestosis (scarring
of the lung), lung cancer and mesothelioma (a cancer of the lung lining).
Regulatory agencies have generally defined ACM as a material containing greater that one (1) percent asbestos,
however some states (e.g., California) define ACM as materials having 0.1% asbestos. In order to define a
homogenous material as non-ACM, a minimum number of samples must be collected from the material dependent
upon its type and quantity. Homogenous materials defined as non-ACM must either have 1) no asbestos identified
in all of its samples or 2) an identified asbestos concentration below the appropriate regulatory threshold.
Asbestos concentrations are generally determined using polarized light microscopy or transmission electron
microscopy. Point counting is an analytical method to statistically quantify the percentage of asbestos in a
sample. The asbestos component of ACM may either be friable or non-friable. Friable materials, when dry, can be
crumbled, pulverized, or reduced to powder by hand pressure and have a higher potential for a fiber release than
non-friable ACM. Non-friable ACM are materials that are firmly bound in a matrix by plastic, cement, etc. and, if
handled carefully, will not become friable.
Federal and state regulations require that either all suspect building materials be presumed ACM or that an
asbestos survey be performed prior to renovation, dismantling, demolition, or other activities that may disturb
potential ACM. Notifications are required prior to demolition and/or renovation activities that may impact the
condition of ACM in a building. ACM removal may be required if the ACM is likely to be disturbed or damaged
during the demolition or renovation. Abatement of friable or potentially friable ACM must be performed by a
licensed abatement contractor in accordance with state rules and NESHAP. Additionally, OSHA regulations for work
classification, worker training and worker protection will apply.
AHERA Asbestos Hazard Emergency Response Act
AST
Aboveground Storage Tanks. ASTs are generally described as storage tanks less than 10% of which are below
ground (i.e., buried). Tanks located in a basement, but not buried, are also considered ASTs. Whether, and the
extent to which, an AST is regulated, is determined on a case-by-case basis and depends upon tank size, its
contents and the jurisdiction of its location.
BGS Below Ground Surface
Brownfields State and/or tribal listing of Brownfield properties addressed by Cooperative Agreement Recipients or Targeted
Brownfields Assessments.
Description of Selected General Terms and Acronyms
Facilities | Environmental | Geotechnical | Materials 2
Term/Acronym Description
BTEX Benzene, Toluene, Ethylbenzene, and Xylenes. BTEX are VOC components found in gasoline and commonly used
as analytical indicators of a petroleum hydrocarbon release.
CERCLA
Comprehensive Environmental Response, Compensation and Liability Act (a.k.a. Superfund). CERCLA is the
federal act that regulates abandoned or uncontrolled hazardous waste sites. Under this Act, joint and several
liability may be imposed on potentially responsible parties for cleanup-related costs.
CERCLIS
Comprehensive Environmental Response, Compensation and Liability Information System. An EPA compilation of
sites having suspected or actual releases of hazardous substances to the environment. CERCLIS also contains
information on-site inspections, preliminary assessments, and remediation of hazardous waste sites. These sites
are typically reported to EPA by states and municipalities or by third parties pursuant to CERCLA Section 103.
CESQG Conditionally Exempt Small Quantity Generators
CFR Code of Federal Regulations
CREC
Controlled Recognized Environmental Condition is defined in ASTM E1527-21 as “a recognized environmental
condition resulting from a past release of hazardous substances or petroleum products that has been addressed
to the satisfaction of the applicable regulatory authority (for example, as evidenced by the issuance of a no
further action letter or equivalent, or meeting risk-based criteria established by regulatory authority) , with
hazardous substances or petroleum products allowed to remain in place subject to the implementation of required
controls (for example, property use restrictions, activity and use limitations, institutional controls, or engineering
controls). A condition considered by the environmental professional to be a controlled recognized environmental
condition shall be listed in the findings section of the Phase I Environmental Site Assessment report, and as a
recognized environmental condition in the conclusions section of the Phase I Environmental Site Assessment
report.”
DOT U.S. Department of Transportation
EPA U.S. Environmental Protection Agency
ERNS
Emergency Response Notification System. An EPA-maintained federal database which stores information on
notifications of oil discharges and hazardous substance releases in quantities greater than the applicable
reportable quantity under CERCLA. ERNS is a cooperative data-sharing effort between EPA, DOT, and the National
Response Center.
ESA Environmental Site Assessment
FRP Fiberglass Reinforced Plastic
Description of Selected General Terms and Acronyms
Facilities | Environmental | Geotechnical | Materials 3
Term/Acronym Description
Hazardous
Substance
As defined under CERCLA, this is (A) any substance designated pursuant to section 1321(b)(2)(A) of Title 33, (B)
any element, compound, mixture, solution, or substance designated pursuant to section 9602 of this title; (C) any
hazardous waste having characteristics identified under or listed pursuant to section 3001 of the Solid Waste
Disposal Act (with some exclusions); (D) any toxic pollutant listed under section 1317(a) of Title 33; (E) any
hazardous air pollutant listed under section 112 of the Clean Air Act; and (F) any imminently hazardous chemical
substance or mixture with respect to which the EPA Administrator has taken action under section 2606 of Title 15.
This term does not include petroleum, including crude oil or any fraction thereof which is not otherwise listed as a
hazardous substance under subparagraphs (A) through (F) above, and the term include natural gas, or synthetic
gas usable for fuel (or mixtures of natural gas and such synthetic gas).
Hazardous Waste
This is defined as having characteristics identified or listed under section 3001 of the Solid Waste Disposal Act
(with some exceptions). RCRA, as amended by the Solid Waste Disposal Act of 1980, defines this term as a “solid
waste, or combination of solid wastes, which because of its quantity, concentration, or physical, chemical, or
infectious characteristics may (A) cause, or significantly contribute to an increase in mortality or an increase in
serious irreversible, or incapacitating reversible illness; or (B) pose a substantial present or potential hazard to
human health or the environment when improperly treated, stored, transported, or disposed of, or otherwise
managed.”
HREC
Historical Recognized Environmental Condition is defined in ASTM E1527-21 as “a past release of any hazardous
substances or petroleum products that has occurred in connection with the property and has been addressed to
the satisfaction of the applicable regulatory authority or meeting unrestricted residential use criteria established
by a regulatory authority, without subjecting the property to any required controls (for example, property use
restrictions, activity and use limitations, institutional controls, or engineering controls). Before calling the past
release a historical recognized environmental condition, the environmental professional must determine whether
the past release is a recognized environmental condition at the time of the Phase I Environmental Site
Assessment is conducted (for example, if there has been a change in the regulatory criteria). If the EP considers
the past release to be a recognized environmental condition at the time the Phase I ESA is conducted, the
condition shall be included in the conclusions section of the report as a recognized environmental condition.”
IC/EC
A listing of sites with institutional and/or engineering controls in place. IC include administrative measures, such
as groundwater use restrictions, construction restrictions, property use restrictions, and post remediation care
requirements intended to prevent exposure to contaminants remaining on-site. Deed restrictions are generally
required as part of the institutional controls. EC include various forms of caps, building foundations, liners, and
treatment methods to create pathway elimination for regulated substances to enter environmental media or effect
human health.
Description of Selected General Terms and Acronyms
Facilities | Environmental | Geotechnical | Materials 4
Term/Acronym Description
ILP Innocent Landowner/Operator Program
LQG Large Quantity Generators
LUST Leaking Underground Storage Tank. This is a federal term set forth under RCRA for leaking USTs. Some states
also utilize this term.
MCL
Maximum Contaminant Level. This Safe Drinking Water concept (and also used by many states as a ground water
cleanup criteria) refers to the limit on drinking water contamination that determines whether a supplier can
deliver water from a specific source without treatment.
MSDS
Material Safety Data Sheets. Written/printed forms prepared by chemical manufacturers, importers and
employers which identify the physical and chemical traits of hazardous chemicals under OSHA’s Hazard
Communication Standard.
NESHAP National Emissions Standard for Hazardous Air Pollutants (Federal Clean Air Act). This part of the Clean Air Act
regulates emissions of hazardous air pollutants.
NFRAP Facilities where there is “No Further Remedial Action Planned,” as more particularly described under the Records
Review section of this report.
NOV Notice of Violation. A notice of violation or similar citation issued to an entity, company or individual by a state or
federal regulatory body indicating a violation of applicable rule or regulations has been identified.
NPDES National Pollutant Discharge Elimination System (Clean Water Act). The federal permit system for discharges of
polluted water.
NPL The NPL is the EPA’s database of uncontrolled or abandoned hazardous waste facilities that have been listed for
priority remedial actions under the Superfund Program.
OSHA Occupational Safety and Health Administration or Occupational Safety and Health Act
PACM Presumed Asbestos-Containing Material. A material that is suspected of containing or presumed to contain
asbestos but which has not been analyzed to confirm the presence or absence of asbestos.
Description of Selected General Terms and Acronyms
Facilities | Environmental | Geotechnical | Materials 5
Term/Acronym Description
PCB
Polychlorinated Biphenyl. A halogenated organic compound commonly in the form of a viscous liquid or resin, a
flowing yellow oil, or a waxy solid. This compound was historically used as dielectric fluid in electrical equipment
(such as electrical transformers and capacitors, electrical ballasts, hydraulic and heat transfer fluids), and for
numerous heat and fire sensitive applications. PCB was preferred due to its durability, stability (even at high
temperatures), good chemical resistance, low volatility, flammability, and conductivity. PCBs, however, do not
break down in the environment and are classified by the EPA as a suspected carcinogen. 1978 regulations, under
the Toxic Substances Control Act, prohibit manufacturing of PCB-containing equipment; however, some of this
equipment may still be in use today.
pCi/L picoCuries per Liter of Air. Unit of measurement for Radon and similar radioactive materials.
PLM Polarized Light Microscopy (see ACM section of the report, if included in the scope of services)
PST Petroleum Storage Tank. An AST or UST that contains a petroleum product.
Radon
A radioactive gas resulting from radioactive decay of naturally-occurring radioactive materials in rocks and soils
containing uranium, granite, shale, phosphate, and pitchblende. Radon concentrations are measured in picoCuries
per Liter of Air.Exposure to elevated levels of radon creates a risk of lung cancer; this risk generally increases as
the level of radon and the duration of exposure increases. Outdoors, radon is diluted to such low concentrations
that it usually does not present a health concern. However, radon can accumulate in building basements or similar
enclosed spaces to levels that can pose a risk to human health. Indoor radon concentrations depend primarily
upon the building's construction, design and the concentration of radon in the underlying soil and ground water.
The EPA recommended annual average indoor “action level” concentration for residential structures is 4.0 pCi/l.
RCRA Resource Conservation and Recovery Act. Federal act regulating solid and hazardous wastes from point of
generation to time of disposal (‘cradle to grave”). 42 U.S.C. 6901 et seq.
RCRA Generators
The RCRA Generators database, maintained by the EPA, lists facilities that generate hazardous waste as part of
their normal business practices. Generators are listed as either large (LQG), small (SQG), or conditionally exempt
(CESQG). LQG produce at least 1000 kg/month of non-acutely hazardous waste or 1 kg/month of acutely
hazardous waste. SQG produce 100-1000 kg/month of non-acutely hazardous waste. CESQG are those that
generate less than 100 kg/month of non-acutely hazardous waste.
RCRA
CORRACTS/TSDs
The USEPA maintains a database of RCRA facilities associated with treatment, storage, and disposal (TSD) of
hazardous materials which are undergoing “corrective action”. A “corrective action” order is issued when there is
a release of hazardous waste or constituents into the environment from a RCRA facility.
Description of Selected General Terms and Acronyms
Facilities | Environmental | Geotechnical | Materials 6
Term/Acronym Description
RCRA Non-
CORRACTS/TSDs
The RCRA Non-CORRACTS/TSD Database is a compilation by the USEPA of facilities which report storage,
transportation, treatment, or disposal of hazardous waste. Unlike the RCRA CORRACTS/TSD database, the RCRA
Non-CORRACTS/TSD database does not include RCRA facilities where corrective action is required.
RCRA
Violators List
RAATS. RCRA Administrative Actions Taken. RAATS information is now contained in the RCRIS database and
includes records of administrative enforcement actions against facilities for noncompliance.
RCRIS Resource Conservation and Recovery Information System, as defined in the Records Review section of this report.
REC
Recognized Environmental Conditions are defined by ASTM E1527-21 as 1) the presence of hazardous substances
or petroleum products in, on, or at the subject property due to a release to the environment; (2) the likely
presence of hazardous substances or petroleum products in, on, or at the subject property due to a release or
likely release to the environment; or (3) the presence of hazardous substances or petroleum products in, on, or
at the subject property under conditions that pose a material threat of a future release to the environment. A de
minimis condition is not a recognized environmental condition.
SCL State “CERCLIS” List (see SPL/State Priority List, below).
SPCC
Spill Prevention, Control and Countermeasures. SPCC plans are required under federal law (Clean Water Act and
Oil Pollution Act) for any facility storing petroleum in tanks and/or containers of 55-gallons or more that when
taken in aggregate exceed 1,320 gallons. SPCC plans are also required for facilities with underground petroleum
storage tanks with capacities of over 42,000 gallons. Many states have similar spill prevention programs, which
may have additional requirements.
SPL
State Priority List. State list of confirmed sites having contamination in which the state is actively involved in
clean up activities or is actively pursuing potentially responsible parties for clean up. Sometimes referred to as a
State “CERCLIS” List.
SQG Small Quantity Generator
SWF/LF State and/or Tribal database of Solid Waste/Landfill facilities. The database information may include the facility
name, class, operation type, area, estimated operational life, and owner.
TPH Total Petroleum Hydrocarbons
TRI
Toxic Release Inventory. Routine EPA report on releases of toxic chemicals to the environment based upon
information submitted by entities subject to reporting under the Emergency Planning and Community Right to
Know Act.
Description of Selected General Terms and Acronyms
Facilities | Environmental | Geotechnical | Materials 7
Term/Acronym Description
TSCA
Toxic Substances Control Act. A federal law regulating manufacture, import, processing, and distribution of
chemical substances not specifically regulated by other federal laws (such as asbestos, PCBs, lead-based paint,
and radon). 15 U.S.C 2601 et seq.
USACE United States Army Corps of Engineers
USC United States Code
USGS United States Geological Survey
USNRCS United States Department of Agriculture-Natural Resource Conservation Service
UST
Underground Storage Tank. Most federal and state regulations, as well as ASTM E1527-21, define this as any
tank, incl., underground piping connected to the tank, that is or has been used to contain hazardous substances
or petroleum products and the volume of which is 10% or more beneath the surface of the ground (i.e., buried).
VCP State and/or Tribal facilities included as Voluntary Cleanup Program sites.
VOC Volatile Organic Compound
Wetlands
Areas that are typically saturated with surface or ground water that creates an environment supportive of wetland
vegetation (i.e., swamps, marshes, bogs). The Corps of Engineers Wetlands Delineation Manual (Technical Report
Y-87-1) defines wetlands as areas inundated or saturated by surface or ground water at a frequency and duration
sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically
adapted for life in saturated soil conditions. For an area to be considered a jurisdictional wetland, it must meet
the following criteria: more than 50 percent of the dominant plant species must be categorized as Obligate,
Facultative Wetland, or Facultative on lists of plant species that occur in wetlands; the soil must be hydric; and,
wetland hydrology must be present.
The federal Clean Water Act which regulates “waters of the US,” also regulates wetlands, a program jointly
administered by the USACE and the EPA. Waters of the U.S. are defined as: (1) waters used in interstate or
foreign commerce, including all waters subject to the ebb and flow of tides; (2) all interstate waters including
interstate wetlands; (3) all other waters such as intrastate lakes, rivers, streams (including intermittent streams),
mudflats, sandflats, wetlands, sloughs, prairie potholes, wet meadows, playa lakes, or natural ponds, etc., which
the use, degradation, or destruction could affect interstate/foreign commerce; (4) all impoundments of waters
otherwise defined as waters of the U. S., (5) tributaries of waters identified in 1 through 4 above; (6) the
territorial seas; and (7) wetlands adjacent to waters identified in 1 through 6 above. Only the USACE has the
authority to make a final wetlands jurisdictional determination.