5-4-MP27000-27041370 Limited HazMat Survey.pdf
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- Solicitation number
- MP27000
- Issued by
- Utah
About this file
This is a Limited Asbestos Survey Report prepared by R & R Environmental, Inc. for the Utah Department of Government Operations, Division of Facilities, Construction and Management (DFCM), regarding Restroom 25 at the Utah State Fairpark located at 155 North 1000 West in Salt Lake City, Utah. The survey was conducted on April 22, 2026, by certified asbestos building inspector Jamison Moss and reviewed by David C. Roskelley, MSPH, CIH, CSP. The survey consisted of visual assessment and bulk sampling of suspect asbestos-containing materials (ACM) in preparation for the scheduled roof replacement project. Six representative samples were collected from the roof materials and submitted to Eurofins Reservoirs Environmental, Inc. (NVLAP accredited laboratory) for analysis via Polarized Light Microscopy (PLM) utilizing EPA Method 600/M4-82-020.
The survey identified asbestos-containing materials in penetration tar sealant on the roof, with two samples (R-05 and R-06) testing positive for 15% and 13% Chrysotile asbestos respectively across approximately 2 square feet of material. Four additional samples from shingle roofing and tar paper tested negative for asbestos content. The identified asbestos-containing materials were assessed as undamaged and non-friable. The report concludes that identified materials must be removed prior to disturbance by a licensed abatement contractor. The survey was limited in scope and does not guarantee that all ACM present in the structure has been identified, as asbestos-containing materials can exist but remain undetected through ordinary investigative procedures. This survey supports the associated DFCM Construction project for Restroom 25 Roof Replacement with a construction cost estimate of $75,000.
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ASBESTOS (LIMITED), LEAD (LIMITED), AND HAZARDOUS MATERIALS
INSPECTION, SURVEY AND ASSESSMENT
FOR THE
UTAH STATE FAIRPARK
RESTROOM 25 ROOF
155 NORTH 1000 WEST
SALT LAKE CITY, UTAH 84116
A LIMITED ASBESTOS SURVEY AND ASSESSMENT
FOR THE
UTAH STATE FAIRPARK
RESTROOM 25 ROOF
May 15, 2026
Prepared for:
Mrs. Aubrey Stapel
Hazmat Program Manager
Utah Department of Government Operations
Division of Facilities, Construction and Management (DFCM)
Taylorsville State Office Building, 3rd Floor
4315 South 2700 West
Taylorsville, Utah 84114
PH: (801) 641-0964
Prepared by:
R & R Environmental, Inc. (R & R)
47 West 9000 South, Suite #2
Sandy, Utah 84070 steve@rrenviro.com
Phone (801) 318-5658
TABLE OF CONTENTS
ASBESTOS
1.0 INTRODUCTION
2.0 EXECUTIVE SUMMARY
3.0 SAMPLING METHODS
4.0 SURVEY RESULTS
5.0 CONCLUSIONS
6.0 LIMITATIONS AND EXCLUSION OF WARRANTY.……………………………………………………6
List of Appendices
Appendix A Sample Log
Appendix B Laboratory Report
Appendix C Photo Log
Appendix D Floor Plans
Appendix E State of Utah Certifications
Limited Asbestos Survey Report Page 1 Utah State Fairpark Restroom 25 Roof
1.0 INTRODUCTION
R & R Environmental, Inc. (R & R) was contacted to conduct a limited asbestos survey for the
Utah State Fairpark Restroom 25 Roof located at 155 North 1000 West in Salt Lake City, Utah
84116. The Restroom 25 Roof is scheduled to be replaced. The survey consisted of a visual assessment of the exterior of the residence for suspect asbestos containing materials (ACM) and bulk sampling of the materials. The fieldwork component of this survey was conducted by Mr.
Jamison Moss who is a Utah Certified Asbestos Building Inspector.
This report presents the conditions and observations noted on the visit dates.
The following general information is included in this survey report:
• Executive Summary (Section 2.0)
• Sampling Methods (Section 3.0)
• Analytical Results (Section 4.0)
• Conclusions (5.0)
• Limitations & Exclusion of Warranty (6.0)
Limited Asbestos Survey Report Page 2
Restroom 25 Roof
2.0 EXECUTIVE SUMMARY
Material(s) containing asbestos or assumed to contain asbestos were identified during this limited survey.
Material Location Quantity % Asbestos Friable Condition Photo #
Penetration Tar Sealant Roof 2 ft2 5% Chrysotile No Undamaged 2
Limited Asbestos Survey Report Page 3
Restroom 25 Roof
UTAH STATE FAIRPARK, RESTROOM 25 ROOF
155 NORTH 1000 WEST, SALT LAKE CITY, UTAH 84116
DATE OF SURVEY: APRIL 22, 2026
NESHAP - REGULATED
ASBESTOS-CONTAINING MATERIALS (R-ACM)
1. Friable asbestos material (>1% asbestos and can be crumbled, pulverized, or reduced to powder by hand pressure)
Thermal system insulation (TSI)*
Textured ceiling material (TCM)*
Spray-on insulation or fireproofing*
Blown-in insulation*
Ceiling tiles/panels*
Plaster, gypsum board, gypsum board joint compound*
Cloth materials* (Boiler Flue Gasket)
Paper materials* (HVAC Paper Tape and Insulating Board)
Electrical wiring insulation*
Sink undercoating (loose)*
Other*
2. Category I ACM which has become friable
Packings
Gaskets
Resilient floor coverings (floor tile and sheet vinyl)
Asphalt roofing products (Dust Debris, Roofing Underlayment Debris, Flashing Material)
3. Category I ACM that will be or has been subjected to sanding, grinding, cutting, or abrading
Packings
Gaskets
Resilient floor coverings (floor tile and sheet vinyl)
Asphalt roofing products
4. Category II ACM that has a high probability of becoming or has become friable during demolition or renovation operations
Asbestos cement materials (TransiteT)*
Asphalt, tar and rubber-base ACM products other than roofing products*
Non-asphalt and non-paper roofing products*
Paint*
Fire brick and/or mortar*
Stainless steel sink undercoating (solid)*
Encapsulated TCM*
Encapsulated TSI*
Mastic for floor tile, ceiling tile, cove molding, etc.*
Other
Limited Asbestos Survey Report Page 4
Restroom 25 Roof
UTAH STATE FAIRPARK, RESTROOM 25 ROOF
155 NORTH 1000 WEST, SALT LAKE CITY, UTAH 84116
DATE OF SURVEY: APRIL 22, 2026
NESHAP NON-REGULATED
ASBESTOS-CONTAINING MATERIAL (N-R-ACM)
1. > 1% asbestos
2. Category I Non-friable (cannot be crumbled, pulverized, or reduced to powder by hand pressure)
ACM with >1% asbestos by new PLM procedure
Packings
Gaskets (Window Glazing & Caulking)
Resilient floor coverings (floor tile)
X Asphalt roofing products
3. Category II Non-friable ACM with >1% asbestos by new PLM procedure (Category includes items meeting Category I definition but not specifically listed in that category)
Asbestos cement materials (TransiteT)* (Fume hoods, counter tops, and window panels)
Asphalt, tar and rubber-base ACM products other than roofing products*
Non-asphalt and non-paper roofing products*
Paint* (Silver Paint Sealant)
Fire brick and/or mortar*
Sink undercoating (solid)*
Mastic for floor tile, ceiling tile, cove molding, etc.*
Other*
Notes:
1. (*) Denotes R&R’s interpretation of materials included in this category.
2. New PLM procedure is outlined in Appendix A, Subpart F, 40 CFR, Part 783, Section 1, Polarized Light Microscopy.
3. The Environmental Protection Agency (EPA) National Emission Standard for Hazardous Air
Pollutants (NESHAP) asbestos revision as outlined in 40 CFR, Part 61, became effective
November 20, 1990. The asbestos classification system outlined in the revision and included in this section is dynamic in nature. Asbestos materials classified as “NON-REGULATED” at the time of the survey may become “REGULATED” due to ongoing or planned maintenance, renovation, or demolition actions, which can transform a material containing greater than 1% asbestos from a “non-friable” and NON-REGULATED to a friable and REGULATED condition.
Classification of ACM in this section and in the executive summary of this report is, therefore, based on the observations of the surveyor at the time of the survey and may or may not be appropriate at later dates.
4. Maintenance, renovation, demolition, weathering, normal wear, water, or other damage can alter the “NON-REGULATED” status of materials, and necessitate precautions required for handling them as “REGULATED” asbestos-materials.
Limited Asbestos Survey Report Page 5
Restroom 25 Roof
3.0 SAMPLING METHODS
Survey procedures were based on those outlined in Title 40 Code of Federal Regulation (CFR)
Part 763, USEPA Asbestos Hazard Emergency Response Act, and the Asbestos Model
Accreditation Plan (effective April 4, 1994). The procedures included visual observation, physical inspection, bulk sample collection, and condition assessment of suspect ACM. The number of samples collected was based on the amount and accessibility of each homogeneous material, with consideration given for the type, age, and condition.
Six (6) samples were collected from the suspect materials to assess the presence of asbestos (or lack thereof) in building materials/systems. Each sample collected was placed into a sealable plastic bag or tub, marked with a unique sample identification code, and packaged for subsequent shipment to the laboratory for analysis. Individual sample identification consisted of a numeric code denoting the sampling media/location.
After packaging and labeling, samples were submitted under proper chain-of-custody to
Reservoirs Environmental, Inc., Denver, Colorado. The National Voluntary Laboratory
Accreditation Program (NVLAP), Lab Code 101896 accredits Reservoirs for asbestos analysis.
Samples were analyzed via Polarized Light Microscopy (PLM) utilizing EPA Method 600/M4-
82-020. Please note that USEPA and OSHA regulations define an ACM as a material containing more than one (1) percent asbestos, by volume, as determined by PLM analysis. In the case of multi-layer systems (e.g., floor tile/mastic layers), the laboratory analyzed and reported each layer separately.
4.0 SURVEY RESULTS
Six (6) representative samples collected were submitted for analytical determination. A summary of analytical results for samples collected and analyzed for this survey are in Appendix B
(Laboratory Results) and are discussed below by building material/system type. Photographs of the buildings where samples were taken are included as Appendix C. Floor Plans of the building where samples were taken are included in Appendix D
Limited Asbestos Survey Report Page 6
Restroom 25 Roof
5.0 CONCLUSIONS
Asbestos-containing materials were identified in the building. See Executive Summary for details.
The identified materials must be removed prior to disturbance by a licensed abatement contractor.
6.0 LIMITATIONS AND EXCLUSION OF WARRANTY
This asbestos survey and assessment was performed using procedures and a level of diligence typically exercised by professional consultants performing similar services. However, asbestos-containing material (ACM) can be present in a structure, but not identified using ordinary investigative procedures.
No asbestos survey can completely, eliminate uncertainty regarding the presence of ACM.
R&R Environmental, Inc.’s level of diligence and investigative procedures are intended to reduce, but not eliminate, potential uncertainty regarding the presence of ACM. The procedures used for this survey attempt to establish a balance between the competing goals of limiting investigative costs, time, and building damage, and reducing the uncertainty about unknown conditions. Therefore, the determinations in this report should not be construed as a guarantee that all ACM present in the subject property has been included in this report.
This report presents R&R Environmental, Inc.’s professional determinations, which are dependent upon information obtained during performance of consulting services. R&R
Environmental, Inc. assumes no responsibility for omissions or errors resulting from inaccurate information provided by sources outside of R&R Environmental, Inc.
No warranty or guarantee, expressed or implied, is made regarding the findings, conclusions, or recommendations contained in this report. The limitations presented above supersede the requirements or provisions of all other contracts or scopes of work, implied, or otherwise, except stated or acknowledged herein.
Limited Asbestos Survey Report Page 7
Restroom 25 Roof
A LIMITED ASBESTOS SURVEY AND ASSESSMENT
OF THE
UTAH STATE FAIRPARK
RESTROOM 25 ROOF
On April 22, 2026, R & R Environmental, Inc. (R & R) of Sandy, Utah, conducted a limited asbestos survey and assessment of the Utah State Fairpark, Restroom 25 Roof located at 155 North
1000 West in Salt Lake City, Utah 84116. Bulk samples of suspect asbestos-containing materials were collected and analyzed. The condition of all friable and non-friable asbestos-containing materials was, assessed. The following accredited inspector conducted the survey and assessment.
Inspected by:
Jamison Moss Date
State of Utah, Division of Air Quality Inspector
Certification Number: ASB-6674
State of Utah Company Certification: ASBC-237
This report was reviewed by:
David C. Roskelley, MSPH, CIH, CSP Date
State of Utah, Division of Air Quality Inspector
Certification Number: ASB-1370
AHERA Inspector #5 PSI 65451 I
Certified Safety Professional #15774
Certified Industrial Hygienist #8529
State of Utah Company Certification: ASBC-237
Appendix A
Sample Log
SAMPLE LOG
Sample
Material/
Homogenous Area
Sample
Location Quantity
Lab Result
(%/Type) Assessment
R-01 Shingle Roof 2,500 ft2 None Detected Undamaged
R-02 Shingle Roof 2,500 ft2 None Detected Undamaged
R-03 Tar Paper Roof 2,500 ft2 None Detected Undamaged
R-04 Tar Paper Roof 2,500 ft2 None Detected Undamaged
R-05 Penetration Tar Sealant Roof 2 ft2 15% Chrysotile Undamaged
R-06 Penetration Tar Sealant Roof 2 ft2 13% Chrysotile Undamaged
Appendix B
Laboratory Report
April 23, 2026
Sincerely, Jeanne Spencer President
Subcontractor Number:
Laboratory Report: RES 744620-1
Project #/P.O. #: None Given
Project Description: Fairpark Restroom 25 Roof
Jamison Moss R & R Environmental 47 West 9000 South #2 Sandy, UT 84070
Dear Jamison, Eurofins Reservoirs is an analytical laboratory accredited for the analysis of Industrial Hygiene and Environmental matrices by the National Voluntary Laboratory Accreditation Program (NVLAP), Lab Code 101896-0 for Transmission Electron Microscopy (TEM) and Polarized Light Microscopy (PLM) analysis and the American Industrial Hygiene Association (AIHA LAP), Lab ID 101533 for Phase Contrast Microscopy (PCM) analysis. This laboratory is currently proficient in both Proficiency Testing and PAT programs respectively.
Eurofins Reservoirs has analyzed the following samples for asbestos content as per your request. The analysis has been completed in general accordance with the appropriate methodology as stated in the attached analysis table. The results have been submitted to your office.
RES 744620-1 is the job number assigned to this study. This report is considered highly confidential and the sole property of the customer. Eurofins Reservoirs will not discuss any part of this study with personnel other than those of the client. The results described in this report only apply to the samples analyzed, as received and with the information provided by the customer (i.e. sample volumes and areas). This report must not be used to claim endorsement of products or analytical results by NVLAP or any agency of the U.S. Government. This report shall not be reproduced except in full, without written approval from Eurofins Reservoirs. Samples will be disposed of after sixty days unless longer storage is requested. If you have any questions about this report, please feel free to call 303-964-1986.
by Camryn Baumgartner
04/23/202604/23/202604/23/202604/23/2026
Eurofins Reservoirs Environmental, Inc Eurofins Reservoirs QA Manual
Effective July 31, 2025 Q:\QAQC\Eurofins Reservoirs QA Manual.pdf
(303) 964-1986
(866) RES-IENV
https://www.eurofinsus.com/builtenv https://clients.rei.et.eurofinsus.com
4955 Yarrow St, Suite 100, Arvada, CO 80002
Laboratory Sample IDLaboratory Sample IDLaboratory Sample IDLaboratory Sample ID LLLL Asbestos ContentAsbestos ContentAsbestos ContentAsbestos Content Non-Non-Non-Non- Non-Non-Non-Non- AAAA SubSubSubSub AsbestosAsbestosAsbestosAsbestos FibrousFibrousFibrousFibrous YYYY PhysicalPhysicalPhysicalPhysical PartPartPartPart MineralMineralMineralMineral VisualVisualVisualVisual FibrousFibrousFibrousFibrous ComponentsComponentsComponentsComponents EEEE DescriptionDescriptionDescriptionDescription EstimateEstimateEstimateEstimate ComponentsComponentsComponentsComponents
Client Sample NumberClient Sample NumberClient Sample NumberClient Sample Number RRRR (%) (%) (%) (%) 744620 -744620 -744620 -744620 - R-01R-01R-01R-01 A Red/black shingle 100 NDNDNDND 10 90.0 744620 -744620 -744620 -744620 - R-02R-02R-02R-02 A Red/black shingle 100 NDNDNDND 10 90.0 744620 -744620 -744620 -744620 - R-03R-03R-03R-03 A Black fibrous resinous tar w/ black resinous material 100 NDNDNDND 15 85.0 744620 -744620 -744620 -744620 - R-04R-04R-04R-04 A Black fibrous resinous tar w/ black resinous material 100 NDNDNDND 15 85.0 744620 -744620 -744620 -744620 - R-05R-05R-05R-05 A Gray/black fibrous tar 100 ChrysotileChrysotileChrysotileChrysotile 15151515 0 85.0 744620 -744620 -744620 -744620 - R-06R-06R-06R-06 A Gray/black fibrous tar 100 ChrysotileChrysotileChrysotileChrysotile 13131313 0 87.0 TEM Analysis recommended for organically bound material (i.e. floor tile) if PLM results are <1%.
Tyler Hutchinson Analyst
Eurofins Reservoirs Environmental, Inc Eurofins Reservoirs QA Manual
Effective July 31, 2025 Q:\QAQC\Eurofins Reservoirs QA Manual.pdf
Job Number:
Client:
Client Project/P.O.:
Client Project Description:
Date Samples Received:
Analysis Type:
Turnaround:
Date Samples Analyzed:
744620-1 R & R Environmental None Given Fairpark Restroom 25 Roof April 23, 2026 EPA 600/R-93/116 - Short Report, Bulk Priority April 23, 2026
EUROFINS RESERVOIRS ENVIRONMENTAL, INC
NVLAP Lab Code 101896-0
AIHA LAP, LLC. LAB ID 101533
TABLE: I ANALYSIS: PLM BULK ANALYSIS, PERCENTAGE COMPOSITION BY VOLUME
NA = Not Analyzed NR = Not Received ND = None Detected TR = Trace; <1 % Visual Estimate Trem-Act = Tremolite-Actinolite
(303) 964-1986
(866) RES-IENV
https://www.eurofinsus.com/builtenv https://clients.rei.et.eurofinsus.com
SUBMITTED BY INVOICE TO
Client Sample ID Number
RES Job #: 744620
CONTACT INFORMATION SERIES
ASBESTOS LABORATORY REQUESTED ANALYSIS VALID MATRIX CODES LAB NOTES
CHEMISTRY LABORATORY
MICROBIOLOGY LABORATORY
**Turnaround times establish a laboratory priority, subject to laboratory volume and are not guaranteed. Additional fees apply for afterhours, weekends and holidays.**
Laboratory Analysis Instructions
(Sample ID's must be unique)
Company: R & R Environmental Company: R & R Environmental
Address: 47 West 9000 South #2 Address: 47 West 9000 South #2
Sandy, UT 84070 Sandy, UT 84070
Project Number and/or P.O. #: None Given Project Zip Code:
Project Description/Location: Fairpark Restroom 25 Roof
Contact: Jamison Moss -1 PLM Priority Phone: (801) 928-1560
Fax:
Cell: (801) 928-1560
Final Data Deliverable Email Address:
jamison@rrenviro.com (+ 3 ADDNL. CONTACTS)
PLM / PCM / TEM / NYS DTL RUSH PRIORITY STANDARD Air = A Bulk = B
Dust = D Food = F
Paint = P Soil = S
Dust RUSH PRIORITY STANDARD
*PRIOR NOTICE REQUIRED FOR SAME DAY TAT
Surface = SU Swab = SW
Tape = T Wipe = W
Metals RUSH PRIORITY STANDARD Drinking Water = DW
Waste Water = WW
Organics* SAME DAY RUSH PRIORITY STANDARD **ASTM E1792 approved wipe media only**
Viable Analysis** PRIORITY STANDARD
**TAT DEPENDENT ON SPEED OF MICROBIAL GROWTH
Medical Device Analysis RUSH STANDARD
Mold Analysis RUSH PRIORITY STANDARD
Special Instructions:
ASBESTOS CHEMISTRY MICROBIOLOGY ICO
1 R-01 X B
2 R-02 X B
3 R-03 X B
4 R-04 X B
5 R-05 X B
6 R-06 X B
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Eurofins Reservoirs Environmental, Inc establishes a unique Lab Sample ID, for each sample, by preceding each unique Client Sample ID with the laboratory RES Job Number.
Eurofins Reservoirs Environmental, Inc will analyze incoming samples based on information received and will not be responsible for errors or omissions in calculations resulting from the inaccuracy of original data. By signing, client/company representative agrees that submission of the following samples for requested analysis as indicated on this Chain of Custody shall consitute an analytical services agreement with payment terms of NET30. Failure to comply with payment terms may result in a 18% APR finance charge.
Relinquished By:
Jamison Moss Date/Time: 04/22/2026 15:45:47 Sample Condition: Acceptable
Received By:
Emily Creasey Date/Time: 04/23/2026 10:46:33 Carrier: Fed-Ex
Eurofins Reservoirs Environmental, Inc Eurofins Reservoirs QA Manual
Effective July 31, 2025 Q:\QAQC\Eurofins Reservoirs QA Manual.pdf
(303) 964-1986
(866) RES-IENV
https://www.eurofinsus.com/builtenv https://clients.rei.et.eurofinsus.com
Appendix C
Photo Log
PHOTO 1: Utah State Fairpark, Restroom 25
Roof
PHOTO 2: Penetration Tar Sealant contains asbestos
R & R Environmental, Inc.
47 West 9000 South, Suite #2, Sandy, Utah 84070
(801) 352-2380 • Fax: (801) 352-2381
SITE PHOTOGRAPHS
A LIMITED ASBESTOS SURVEY AND
ASSESSMENT
OF THE
UTAH STATE FAIRPARK
RESTROOM 25 ROOF
PROJECT NO:
DESIGNED BY:
SCALE:
REVIEWED BY:
DRAWN BY:
DATE:
FILE:
Appendix D
Floor Plan
N
UTAH STATE FAIR PARK
RESTROOM 25
155 NORTH 1000 WEST
SALT LAKE CITY, UT 84116
APRIL 2026
ROOF
ASBESTOS FLOORPLAN
= ASBESTOS SAMPLE NUMBER & LOCATION##
= ASBESTOS CONTAINING PENETRATION TAR SEALANT
Appendix E
State of Utah Certifications
Utah Asbestos Certification
State of Utah
SPENCER J. COX
Governor
DETORE HENDERSON
Lieutenant Governor
February 27, 2026
Jamison Moss R&R Environmental
Depa1tment of Environmental Quality
Tim Davis fa:ec11tive Direc/01·
DIVISION OF AIR QUALITY
Bryce C. Bird
Director
47 West 9000 South, Suite 2 Sandy, UT 84070
Dear Mr. Moss:
Re: Utah Asbestos Program Individual Certification Card
Jamison Moss
ASB-6674
"'" Inspector (Eitp:" 02/20/2027)
Project oeMner'(Exp. 01/12/2027) it V .
4U~hD-~~fA.'Q 1· Director, ta IvIs1on o ir ua 1ty
DAQA-001-26
The Utah Division of Air Quality (DAQ) has reviewed your Utah Asbestos Program Certification Application for Individuals and we are pleased to inform you that your application has been approved. Your new asbestos program individual certification card is enclosed with this letter and this card is the sole method of individual certification documentation that you will receive from the DAQ.
Please check the information on your asbestos program certification card carefully. Please confirm that the photograph, name, and certification discipline(s) are correct. Also, please remember to keep your current asbestos program certification card with you at all times when you are performing regulated asbestos work activities.
Please contact Barbara Perkins at (801) 536-0221 or at bperkins@utah.gov if you have any questions regarding this letter or the enclosed asbestos program certification card.
Sincerely, Leonard Wrlgll (Feht2026 09:17:31 Msn
Leonard Wright, Manager Air Toxics, Lead-Based Paint, and Asbestos Section
LW:BP:rh
195 North 1950 Wes1 • Sah Lakll Chy, UT Mailing Address: P.O. Box 144820 • Sall Lake City, UT 84114-4820
Telephone (80 I) 536-4000 • flax (80 I) 536-4099 • T.D.D. 800 346-3128 www.1l1111,111ul,,Mo11 l'rinlcd on 100¼ recycled p11pcr
Utah Lead-Based Paint Certification
State of Utah
SPENCER J. COX
Go,·tmor
DEIDRE HENDERSON
litutenant Gol'limor
February 11, 2025
Steve Smith
Department of Environmental Quality
Kimberly D. Shelley Exec11tfre Director
DIVISION OF AIR QUALITY
Bryce C Bird
Director
R&R Environmental, Inc.
4 7 West 9000 South, #2 Sandy, UT 84070
Dear Mr. Smith:
Re: Utah Lead-Based Paint Program Individual Certification Card
Inspector l Risk Aue
-4~;_·~
Director, Utah D1v1sion of Air Quality
DAQA-002-25
The Utah Division of Air Quality (DAQ) has reviewed your Utah Lead-Based Paint (LBP)
Program Certification Application for Individuals and we are pleased to inform you that your application has been approved. Your new LBP program individual certification card is enclosed with this letter and this card is the sole method of individual certification documentation that you will receive from the DAQ.
Please check the information on your LBP program certification card carefully. Please confirm that the photograph, name, and certification discipline(s) are correct. Also, please remember to keep your current LBP program certification card with you at all times when you are performing regulated LBP work activities.
Please contact Barbara Perkins at (80 l) 536-0221 or at bperkins@utah.gov if you have any questions regarding this letter or the enclosed LBP program certification card.
Sincerely, ~ Sl1J~ Leonard Wright (Feb 7, 2025 12:09 MST)
Leonard Wright, Manager Air Toxics, Lead-Based Paint, and Asbestos Section
LW:BP:lr
195 Nonh 1950 Wes,, 4~' Hoor • Sall Lake City, Ur Mailing Addrm l' 0 llo"< 144820 • Suh Lnl.c Cny. UT 84114-1820
'I elephone (80 I) 536-4000 • l·a"< (801) 536-4099 ·TDD (80 I) 536-1-11-1 ~• u ,, di:tJ mnh gm•
P11111cd on I00~. 1ccycled papc, LIMITED LEAD-BASED PAINT INSPECTION
UTAH STATE FAIRPARK
RESTROOM 25 ROOF
Utah Department of Government Operations
Division of Facilities, Construction and Management (DFCM)
Taylorsville State Office Building, 3rd Floor
4315 South 2700 West
47 West 9000 South, Suite #2
Sandy, Utah 84070
LIMITED LEAD-BASED PAINT INSPECTION
TABLE OF CONTENTS
TITLE PAGE
1.0 Introduction
2.0 Building Description
3.0 Lead-based Paint Definition
4.0 Procedures
4.1 Paint Sampling Methods
4.2 XRF Calibration
4.3 Field Documentation
5.0 Findings
6.0 Results and Recommendation
8.0 Limitations and Exclusion of Warranty
Appendices
A. Data Tables
Table 1 – Building Component with Lead Levels at 0.1 mg/cm2 and above
Table 2 – Building Component with Lead Levels at below 0.1 mg/cm2
B. Photograph Log
Utah State Fairpark Limited Lead-Based Paint Inspection
Restroom 25 Roof Page 1
Limited Lead-Based Paint Inspection
1.0 INTRODUCTION
On April 22, 2026, a limited lead-based paint (LBP) survey was conducted for the Utah
State Fairpark, Restroom 25 Roof. The purpose of the survey was to identify lead in paint on the roof of the building. Measurements for lead in paint were made using a SciApps
X550 X-ray Fluorescence (XRF) Spectrum Analyzer. No chip sampling or laboratory analysis was performed for confirmation of XRF measurements.
The survey work was overseen by David Roskelley with R & R Environmental, Inc. in
Sandy, Utah. David Roskelley has completed Lead Inspector Training through the
University of Utah, Rocky Mountain Center for Occupational and Environmental Health
(RMCOEH), an EPA-sponsored Regional Lead Training Center, and is certified by the
State of Utah, Division of Environmental Quality, as a Lead Inspector.
The U.S. Department of housing and Urban Development (HUD) Guidelines for the
Evaluation and Control of Lead-Based Paint Hazards in housing (HUD Guidelines), Chapter7: Lead-Based Paint Inspection, 1997 Revision, was generally followed for this survey, with modifications appropriate for a non-residential building.
The following accredited and certified inspector oversaw the inspection, collected the samples and made assessment:
May 15, 2026
David C. Roskelley, MSPH, CIH, CSP Date
Lead-Based Paint Inspector
Certification Number: PB-1041
This report was reviewed by:
David C. Roskelley, MSPH, CIH, CSP Date
Lead-Based Paint Inspector
Certification Number: PB-1041
Restroom 25 Roof Page 2
2.0 BUILDING DESCRIPTION
Building Identification
Building Name ................................ Utah State Fairpark, Restroom 25 Roof
Building Address .............155 North 1000 West, Salt Lake City, UT 84116
Building Construction
Building Construction Date ..................................................................... NA
Building Type ................................................................................ Restroom
Building Total Sq. Ft........................................................................ 2,500 ft2
Structural System ................................................................................. Wood
Exterior Wall Construction ................................................................... Brick
Floor Deck Construction .......................................................................... NA
Roof Construction ............................................................................. Shingle
Floors Above Grade
Floors Below Grade ................................................................................. NA
Interior Finishes
Floors ....................................................................................................... NA
Walls ........................................................................................................ NA
Attic.......................................................................................................... NA
Crawl space .............................................................................................. NA
Building Mechanical
Heating Plant ............................................................................................ NA
Main Heating Distribution ....................................................................... NA
Cooling Plant ........................................................................................... NA
Main A / C Distribution ........................................................................... NA
Restroom 25 Roof Page 3
3.0 LEAD-BASED PAINT DEFINITIONS
HUD defines “lead-based paint” as any coating that has a lead concentration of 1.0 milligram of lead per square centimeter (1.0 mg/cm2) or greater, or if the lead concentration is greater than 0.5% by weight. The Consumer Product Safety Commission (CPSC) currently considers paint to be lead-containing if the concentration of lead exceeds 600 ppm (0.06% by weight). In 1978, the CPSC banned the sale of lead-based paint to consumers, and banned its application in areas where consumers have direct access to painted surfaces. Both the CPSC and HUD definitions of lead-containing paint are aimed at protecting the general population from exposure to lead in the residential setting.
By contrast, the mission of the Occupational Safety and Health Administration (OSHA) with respect to lead-containing paint, is to protect workers during construction activities that may generate elevated airborne lead concentrations. OSHA states that construction work (including renovation, maintenance, and demolition) carried-out on structures coated with paint have lead concentrations lower than the HUD or CPSC can still result in airborne lead concentrations in excess of regulatory limits. For this reason, OSHA has not defined lead-containing paint, but states that paint having any measurable level of lead may pose a substantial exposure hazard during construction work, depending upon the work performed.
4.0 PROCEDURES
4.1 Paint Sampling Methodologies
Direct measurements of lead in paint were made using a SciApps X550 X-ray Fluorescence
(XRF) Spectrum Analyzer. The SciApps X550 X-ray Fluorescence (XRF) Spectrum
Analyzer non-destructively measures lead concentrations of painted surfaces, regardless of the number of layers present. These instruments were developed specifically for addressing lead-based paint issues in housing and their use in identifying potential exposure hazards for renovation or construction work must be augmented by selective collection and analysis of physical paint chip samples.
The newer XRF instruments are capable of identifying lead in paint at concentrations of about 0.01 milligram per square centimeter (mg/cm2) or greater. When lead concentrations are lower than this, the instruments are not capable of making accurate, reliable measurements, and the reported lead concentration may underestimate or overestimate the actual lead concentration in the paint. Therefore, an XRF readings of 0.01 mg/cm2 or greater may be considered lead-containing from an OSHA perspective, and any readings of 0.0mg/cm2 or less should be confirmed by the collection and laboratory analysis of paint chip samples, or assumed to be positive for lead.
Where paint chip samples are necessary, samples are collected according to the protocol specified in the HUD Guidelines. The samples are then submitted to a laboratory recognized under the EPA’s National Lead Laboratory Accreditation Program (NLLAP) for analysis by flame atomic absorption spectrophotometry according to American Society of Testing and Materials (ASTM) method ASTM E 1645.
Restroom 25 Roof Page 4
4.2 XRF Calibration
Before beginning the testing and after the testing was completed, the internal calibration of the LPA-1 was checked by taking two consecutive measurements on a National Institute for Standards and Technology (NIST) standard with a known concentration of lead. Three more readings were taken on a lead-free wood block. These calibration checks are reported within the XRF data tables found in Appendix A of this report and are maintained in a file at R & R Environmental, Inc. to detect changes in instrument performance over time.
4.3 Lead Paint Inspection Data Tables
The XRF instrument generates a unique set of data tables for each inspection and can be exported into Microsoft Excel Spreadsheet format .xls. The Sequential Report lists the measurements made throughout the property in sequential order, from the first measurement to the last. The Data table is maintained in a file at R & R Environmental, Inc.
5.0 FINDINGS
The XRF instrument indicated that lead is not present on the roof surfaces. These surfaces are listed in Table 1 “positive” building components (Measurements of 0.01 mg/cm2 and above) in Appendix A of this report.
If lead was detected in some of the building’s painted surfaces, the OSHA Lead in
Construction Standard (29 CFR 1926.62) will apply to any construction work (including renovation and demolition) that may disturb those surfaces. The standard requires, among other things, the following:
• Initial training on the hazards of lead exposure, proper work practices, respiratory protection, and other topics;
• An initial exposure assessment, by air monitoring, to determine the lead exposure assessment, until sample analysis indicates exposures below the
Permissible Exposure Limit;
• Hand washing facilities, designated clean change areas, and designated eating areas.
In addition to the above considerations, the presence of lead in demolition debris has the potential to impose limitations on where and how the debris may be disposed. The
Resource Conservation and Recovery Act (RCRA), Subtitles C and D, require that the waste must be analyzed to determine the amount of leachable lead present. The type of test to be performed on the waste is the Toxicity Characteristic Leaching Procedure (TCLP) for lead, and the results of this test will determine whether the material must be handled and disposed of as hazardous waste. For structures containing large amounts of lead-containing paint, significant potential for failing the TCLP exists.
Restroom 25 Roof Page 5
6.0 RESULTS AND RECOMMENDATIONS
Lead-based paint was not detected on the roof surfaces during this limited survey.
7.0 LIMITATIONS AND EXCLUSIONS OF WARRANTY
This lead inspection was performed using procedures and a level of diligence typically exercised by professional consultants performing similar services. However, lead-based paint (LBP) can be present in a surface, but not identified using ordinary investigative procedures.
No lead inspection can completely eliminate uncertainty regarding the presence of LBP. R
& R Environmental, Inc. level of diligence and investigative procedures are intended to reduce, but not eliminate, potential uncertainty regarding the presence of LBP. The procedures used for this survey attempt to establish a balance between the competing goals of limiting investigative costs, time, and building damage, and reducing the uncertainty about unknown conditions. Therefore, the determinations in this report should not be construed as a guarantee that all LBP present in the subject property has been included in this report.
This report presents R & R Environmental, Inc.’s professional determinations, which are dependent upon information obtained during performance of consulting services. R &R
Environmental, Inc. assumes no responsibility for omissions or errors resulting from inaccurate information provided by sources outside of R & R Environmental, Inc.
No warranty or guarantee, expressed or implied, is made regarding the findings, conclusions, or recommendations contained in this report. The limitations presented above supersede the requirements or provisions of all other contracts or scopes of work, implied or otherwise, except those stated or acknowledged herein.
Appendix A
Lead Paint Inspection Data Tables
Table 1
Building Components with Lead Levels at 0.01 mg/cm2 and Above
Room
Floor
(2)
Number
Lead
Level
(mg/cm2)
Component
Side (1)
Substrate
Color
Condition
3 1 CALIBRATION
1 1.1 CALIBRATION
2 1.1 CALIBRATION
18 1.1 CALIBRATION
19 1.1 CALIBRATION
20 1.1 CALIBRATION
*Side: A=North, B=East, C=South, D=West
Table 2
Building Components with Lead Levels Below 0.01 mg/cm2
Room
Floor (2)
Number
Lead
Level
(mg/cm2)
Component
Side (1)
Substrate
Color
Condition
EXTERIOR EXTERIOR 4 0 GUTTER A METAL WHITE INTACT
EXTERIOR EXTERIOR 5 0 GUTTER B METAL WHITE INTACT
EXTERIOR EXTERIOR 6 0 GUTTER C METAL WHITE INTACT
EXTERIOR EXTERIOR 7 0 GUTTER D METAL WHITE INTACT
EXTERIOR EXTERIOR 8 0 FLASHING A METAL WHITE INTACT
EXTERIOR EXTERIOR 9 0 FLASHING B METAL WHITE INTACT
EXTERIOR EXTERIOR 10 0 FLASHING C METAL WHITE INTACT
EXTERIOR EXTERIOR 11 0 FLASHING D METAL WHITE INTACT
ROOF ROOF 12 0 SKYLIGHT ROOF METAL BROWN INTACT
ROOF ROOF 13 0 SKYLIGHT ROOF METAL BROWN INTACT
ROOF ROOF 14 0 SKYLIGHT ROOF METAL BROWN INTACT
ROOF ROOF 15 0 PIPE ROOF METAL SILVER INTACT
ROOF ROOF 16 0 PIPE ROOF METAL SILVER INTACT
ROOF ROOF 17 0 PIPE ROOF METAL SILVER INTACT
*Side: A=North, B=East, C=South, D=West
Appendix B
Photograph Log
PHOTO 1: Utah State Fairpark, Restroom 25
Roof
R & R Environmental, Inc.
47 West 9000 South, Suite #2, Sandy, Utah 84070
(801) 352-2380 • Fax: (801) 352-2381
SITE PHOTOGRAPHS
A LIMITED LEAD BASED PAINT INSPECTION
OF THE
PROJECT NO:
DESIGNED BY:
SCALE:
REVIEWED BY:
DRAWN BY:
DATE:
FILE:
HAZARDOUS MATERIALS INSPECTION
UTAH STATE FAIRPARK
RESTROOM 25 ROOF
Utah Department of Government Operations
Division of Facilities, Construction and Management (DFCM)
Taylorsville State Office Building, 3rd Floor
4315 South 2700 West
47 West 9000 South, Suite #2
Sandy, Utah 84070
Utah State Fairpark Hazardous Material Inspection
Hazardous Materials Inspection
Salt Lake City, Utah 84116
On April 22, 2026, Jamison Moss of R & R Environmental, Inc., conducted a hazardous materials inspection of the Utah State Fairpark, Restroom 25 Roof located at 155 North
1000 West in Salt Lake City, Utah 84116. The purpose of this survey was to identify the existence, extent, and condition of hazardous materials. The inspection was conducted based on an agreement with Aubrey Stapel with Utah DFCM.
Hazardous materials requiring proper removal and disposal were identified at the Utah
State Fairpark, Restroom 25 Roof, Salt Lake City, Utah as follows:
Material Location Quantity Unit Cost
NA NA NA NA
The State of Utah’s DFCM policy requires the items above to be removed and disposed of at a facility approved to accept such waste prior to demolition. This may or may not be applied to the city of Salt Lake City in Salt Lake County, but R & R Environmental, Inc.
recommends removal and proper disposal of these components prior to any demolition activities.
The cost estimate to remove and dispose of these hazardous materials is estimated at approximately $0.00. This cost estimate does not include transportation, removal, design, or management fees associated with dismantling and packaging the materials.
| DFCM_Utah State Fairpark_RR25_Limited Hazmat_April 2026.pdf |
| TABLE OF CONTENTS |
| Appendix A |
| SAMPLE LOG |
| Appendix B |
| 744620-1.pdf |
| DFCM_Utah State Fairpark_RR25_Limited Hazmat_April 2026 |
| TABLE OF CONTENTS |
| SAMPLE LOG |
| Appendix C |
| Appendix D |
| UT State Fairpark Restroom 25.pdf |
| DFCM_Utah State Fairpark_RR25_Limited Hazmat_April 2026 |
| TABLE OF CONTENTS |
| SAMPLE LOG |
| Appendix E |
| Jamison Feb 2027.pdf |
| 2026 SBS : DCR ACM LBP.pdf |
| DAQ Card exp Sept 17 2026.pdf |
| 2025 SBS : DCR ACM LBP.pdf |
| SBS LBP Cert Exp Jan 2028.pdf |
| 2025 DCR ACM LBP.pdf |
| DCR DAQ Card Exp Sept 2026.pdf |
| 2025 SBS : DCR ACM LBP |
| DFCM_Utah State Fairpark_RR25_Limited Hazmat_April 2026 |
| TITLE PAGE |
| Appendices |
| 1.0 INTRODUCTION |
| 2.0 BUILDING DESCRIPTION |
| 3.0 LEAD-BASED PAINT DEFINITIONS |
| 4.0 PROCEDURES |
| Appendix A |
| Appendix B |
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