ACM LBP Survey Report.pdf

Asbestos and Lead-Based Paint Survey Report

VAMC MOUNTAIN HOME – BUILDING 13 CHAPEL

LAMONT STREET AND VETERANS WAY

JOHNSON CITY, TENNESSEE

February 25, 2021 Terracon Project No. 86207201

Prepared for:

FFE, Inc.

Cincinnati, Ohio

Prepared by:

Terracon Consultants, Inc.

Greenville, South Carolina

Inspector:

Stephen N. Ellis

TDEC License No. A-I-59148-59469 Inspected on January 12 and 13, 2021

TABLE OF CONTENTS

EXECUTIVE SUMMARY……………………………………………………………………………...i

1.0 INTRODUCTION

2.0 BUILDING DESCRIPTION

3.0 ASBESTOS SURVEY

3.1 Regulatory Overview

3.2 Previous Reports Review

3.3 Visual Assessment

3.4 Physical Assessment

3.5 Sample Collection

3.6 Sample Analysis

3.6 Findings

4.0 LEAD-BASED PAINT SURVEY

4.1 Regulatory Overview

4.2 Sampling and Analytical Protocol

4.3 Findings

5.0 RECOMMENDATIONS

6.0 GENERAL COMMENTS

LIST OF APPENDICES

APPENDIX A - FIGURE

Figure 1 – General Layout/ Sample Locations

APPENDIX B - TABLES

Table 1 - Asbestos Survey Sample Summary Table 2 – Lead-in-Paint Sample Summary (Paint Chip)

APPENDIX C – LABORATORY REPORTS

APPENDIX D – PHOTODOCUMENTATION

APPENDIX E – INSPECTOR’S CREDENTIAL

APPENDIX F – PRIOR SURVEY REPORTS

ACM and LBP Survey Report VAMC Mountain Home – Building 13 Chapel ■ Johnson City, Tennessee February 25, 2021 ■ Terracon Project No. 86207201

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EXECUTIVE SUMMARY

Terracon Consultants, Inc. (Terracon) conducted an asbestos and lead-based paint survey at VAMC Mountain Home – Building 13 Chapel at Lamont Street and Veterans Way in Johnson City, Tennessee. Our survey was conducted on January 12 and 13, 2021 in support of proposed renovations and repairs and in general accordance with the terms of our Proposal No. P86207201 dated September 23, 2020. This Executive Summary is intended as an overview for the convenience of the reader. The complete report must be reviewed in its entirety prior to making decisions regarding this site.

The asbestos-containing material (ACM) survey was performed by a Tennessee Department of Environment & Conservation (TDEC) licensed asbestos building inspector in general accordance with the sampling protocols established in Environmental Protection Agency (EPA) 40 Code of Federal Regulations (CFR) 763 (Asbestos Hazard Emergency Response Act, AHERA).

Asbestos-Containing Materials

A total of sixty-four (64) bulk samples were collected from the interior and exterior of the building.

A general layout with sample locations is included as Figure 1 in Appendix A. Sample descriptions, locations, analytical results, classification and estimated quantities are summarized in Table 1 in Appendix B. The asbestos laboratory analytical report is included in Appendix C and photographs are provided in Appendix D.

Asbestos was detected in concentrations of greater than one percent (1%) in the following materials:

§ TSI contaminated debris (40% chrysotile) in the closet under the basement stairs;

§ Silver duct mastic (2% chrysotile) on the intake duct work in the bell tower;

§ Caulking (3% chrysotile) on the exterior doors;

§ Gray mortar joint caulking (2% chrysotile) on the exterior concrete sill blocks;

§ Black mastic (6% chrysotile) on downspout connections;

§ Residual flashing mastic (5% chrysotile) on the roof; and, § Brown/gold stair tread mastic (2% chrysotile) on the stairwells to the organ loft.

Lead-Based Paint

Nineteen (19) paint-chip samples were collected from various components and submitted for laboratory analysis. The results of this analysis are summarized in Table 2 in Appendix B. A copy of the laboratory data report and chain of custody form is included in Appendix C. Lead was detected in eighteen (18) of the samples collected. Nine of the eighteen samples were analyzed to be above 0.5% by weight; therefore, these paints are considered to be lead-based paint by the EPA definition.

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Paints exceeding 0.5% by weight are summarized below.

§ White paint on metal roof caps in the bell tower;

§ White paint on wooden windowsills in the Protestant Chapel;

§ Teal paint on brick walls in the basement;

§ White paint on wooden door to the crawlspace;

§ White paint on wooden door frame to the crawlspace;

§ White paint on the wooden exterior handrails;

§ White paint on wooden roof framing;

§ White paint on wooden window frames on the bell tower; and § White paint on wooden roof framing.

In addition to the above listed painted components, lead paint was identified and reported in the report titled Project 621-05-115 conducted by E. Roberts Alley and Associates, Inc. and dated January 27, 2006. These additional paints are identified as being on all interior wooden door and window components as well any exterior wooden components.

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ASBESTOS AND LEAD-BASED PAINT SURVEY REPORT

VAMC MOUNTAIN HOME – BUILDING 13 CHAPEL

LAMONT STREET AND VETERANS WAY

JOHNSON CITY, TENNESSEE

Project No. 86207201

1.0 INTRODUCTION

Terracon conducted an asbestos survey at VAMC Mountain Home – Building 13 Chapel at Lamont Street and Veterans Way in Johnson City, Tennessee. The survey was conducted on January 12 and 13, 2021 in general accordance with the terms of our Proposal No. P86207201 dated September 23, 2020. It is Terracon’s understanding that this survey was requested due to the proposed renovations and repairs scheduled for the structure. EPA regulation 40 CFR 61, Subpart M, National Emission Standards for Hazardous Air Pollutants (NESHAP), prohibits the release of asbestos fibers to the atmosphere during renovation/demolition activities. NESHAP requires that potentially regulated asbestos-containing materials (ACM) be identified, classified and quantified prior to planned disturbances or demolition activities.

Suspect ACM was sampled in general accordance with the sampling protocols outlined in EPA Regulation 40 CFR 763 Subpart E763.86 (Asbestos Hazard Emergency Response Act, AHERA).

Building components were surveyed and homogeneous areas of suspect ACM were visually identified and documented. Although reasonable effort was made to survey accessible suspect materials, additional suspect but un-sampled materials could be located in walls, in voids or in other concealed areas. Samples were delivered to an accredited laboratory for analysis by Polarized Light Microscopy (PLM).

Terracon also collected paint chip samples of selected components. Results from the paint chip analyses may be utilized when evaluating potential worker exposure scenarios for Occupational Safety and Health Administration (OSHA) compliance (29 CFR 1926.62).

Prior to mobilizing to the site, Terracon was provided with asbestos survey reports prepared by E.

Roberts Alley & Associates, Inc. (January 2006) and EFI Global (January 2010). Those reports were reviewed and the findings incorporated into our survey. Copies of these survey reports are provided in Appendix F.

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2.0 BUILDING DESCRIPTION

The chapel (Building 13) is a two-story building covering approximately 6,875 square feet, with a basement. The building is constructed with a heavy brick veneer with interior wood framing atop a brick foundation. The building is split into two separate chapel areas (Protestant and Catholic), with organ lofts and a bell tower over a basement/crawlspace. Interior flooring is finished with predominantly hardwood, floor tile and mastic, stair treads and mastic, and residual carpet mastic.

Interior walls are mainly plaster over wooden lathe with limited gypsum board walls in the rear of the Catholic chapel. Ceilings are open to the rafters in the chapels with a few areas of plaster ceiling or drop-in cellulose ceiling tiles. Piping where observed was insulated with either fiberglass with mastic or foam rubber. A limited area of suspect thermal system insulation was noted on piping and the floor of a closet under the basement stairs. Several commercial heating, ventilation, and air conditioning (HVAC) units were observed in the crawlspaces. HVAC ductwork was metal or flexible plastic with fiberglass wrapped over it and suspect mastic on the seams.

Suspect caulking was observed in the interior and exterior of the building on windows, doors, and mortar lines. Roofing on the building was mainly slate over felt paper, with a small area of a rubberized membrane over plywood adjacent to the bell tower.

The crawlspace area underneath the Protestant chapel was not assessed as this space was labeled as a confined space and, therefore, Terracon did not attempt to access this area as part of our survey. Based upon limited cursory observations from the crawl space door the interior of the crawlspace appeared similar to the remaining crawlspace areas.

3.0 ASBESTOS SURVEY

The asbestos survey was conducted by Mr. Stephen N. Ellis a trained and TDEC-accredited asbestos building inspector (License No. A-I-59148-59469). A copy of Mr. Ellis’ accreditation is provided in Appendix E. The survey was conducted in general accordance with the protocols established by EPA regulation 40 CFR 763, the Asbestos Hazard Emergency Response Act (AHERA). A summary of the field activities is described below.

3.1 Regulatory Overview

The asbestos NESHAP (40 CFR Part 61, Subpart M) regulates asbestos fiber emissions and asbestos waste disposal practices. It also requires the identification and classification of existing building materials prior to demolition or renovation activity. Under NESHAP, asbestos-containing building materials are classified as either friable, Category I non-friable or Category II non-friable ACM. Friable materials are those that, when dry, may be crumbled, pulverized or reduced to powder by hand pressure. Category I non-friable ACM includes packing materials, gaskets, resilient floor coverings and asphalt roofing products containing more than 1 percent (%) asbestos.

Category II non-friable ACM are non-friable materials other than Category I materials that contain more than 1% asbestos.

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Regulated Asbestos-Containing Materials are (a) friable asbestos material, (b) Category I non-friable ACM that has become friable, (c) Category I non-friable ACM that will be or has been subjected to sanding, grinding, cutting or abrading, or (d) Category II non-friable ACM that has a high probability of becoming or has become crumbled, pulverized, or reduced to powder by the forces expected to act on the material during demolition or renovation operations. RACM must be removed prior to renovation or demolition activities.

The Occupational Safety and Health Administration (OSHA) Asbestos Standard for Construction Industry (29 CFR 1926.1101) regulates workplace exposure to asbestos. The OSHA standard requires that employee exposure to airborne asbestos fibers be maintained below 0.1 asbestos fibers per cubic centimeter of air (0.1 f/cc). The OSHA standard classifies construction and maintenance activities, which could disturb ACM, and specifies work practices and precautions which employers must follow when engaging in each class of regulated work. A full copy of the OSHA asbestos standard for general industry may be found at OSHA’s website (www.osha.gov) and should be referenced for specific information.

3.2 Previous Reports Review

Terracon additionally reviewed previous reports conducted by E. Roberts Alley & Associates, Inc.

(January 2006) and EFI Global (January 2010). Upon review of these reports brown floor tile, gray/green floor tile, stair tread mastic, and roofing (assumed) were reported as being asbestos-containing materials.

During our assessment of the building it appeared that the brown and grey/green floor tile materials had been abated from their substrate. The stair tread materials appear to still be place and in good condition. Roofing felt was found during our assessment and was sampled, with results showing that these materials did not contain asbestos.

3.3 Visual Assessment

Our survey activities began with visual observation of the interior and exterior of the building to identify apparent homogeneous areas of suspect ACM. A homogeneous area consists of building materials, which appear similar throughout in terms of color, texture and date of application.

Building materials which were not identified as concrete, glass, wood, masonry, metal or rubber were considered suspect ACM.

Terracon lifted floor coverings, where possible, and did not observe additional flooring layers unless specifically mentioned herein; however, as Terracon could not assess beneath all floor coverings in all areas, there may be isolated areas of additional suspect material present beneath existing flooring.

http://www.osha.gov/

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3.4 Physical Assessment

A physical assessment of each homogeneous area of suspect ACM was conducted to assess the friability and condition of the materials. A friable material is defined by the EPA as a material, which can be crumbled, pulverized or reduced to powder by hand pressure when dry. Friability was assessed by physically touching suspect materials.

3.5 Sample Collection

Based on the results of the visual assessment, bulk samples of suspect ACM were collected in general accordance with AHERA sample collection protocols. Random samples of suspect materials were collected in each homogeneous area. Bulk samples were collected using wet methods as applicable to reduce the potential for fiber release. Samples were placed in sealable containers and labeled with unique sample numbers using an indelible marker. The selection of sample locations and frequency of sampling was based on Terracon’s observations and the assumption that like materials in the same area are homogeneous in content. Sample locations are depicted on Figure 1 in Appendix A. A summary of the suspect ACM samples collected during the survey is presented in Table 1 in Appendix B.

3.6 Sample Analysis

Bulk samples were submitted using chain-of-custody procedures to Scientific Analytical Institute, Inc. (SAI) of Greensboro, North Carolina. SAI is accredited under the National Voluntary Laboratory Accreditation Program NVLAP (No. 200664).

Asbestos analysis was performed by PLM with dispersion staining techniques per EPA EPA/600/R- 93/116. The percentage of asbestos, where applicable, was determined by microscopical visual estimation.

3.7 Findings

A total of sixty-four (64) bulk samples were collected from the interior and exterior of the building.

A general layout with sample locations is included as Figure 1 in Appendix A. Sample descriptions, locations, analytical results, classification and estimated quantities are summarized in Table 1 in Appendix B. Asbestos laboratory analytical reports are included in Appendix C and photographs are provided in Appendix E.

Asbestos was detected in concentrations of greater than one percent (1%) in the following materials:

§ TSI contaminated debris (40% chrysotile) in the closet under the basement stairs;

§ Silver duct mastic (2% chrysotile) on the intake duct work in the bell tower;

§ Door caulking (3% chrysotile) on the exterior doors;

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§ Gray mortar joint caulking (2% chrysotile) on the exterior concrete sill blocks;

§ Black mastic (6% chrysotile) on downspout connections;

§ Residual flashing mastic (5% chrysotile) on the roof; and, § Brown/gold stair tread mastic (2% chrysotile) on the stairwells to the organ loft.

4.0 LEAD-BASED PAINT SURVEY

4.1 Regulatory Overview

For the purpose of the OSHA lead standard, lead includes metallic lead, inorganic lead compounds, and organic lead soaps. A synopsis of the OSHA regulations (29 CFR 1926.62) and the applicability are described below.

The OSHA Lead Standard for Construction (29 CFR 1926.62) applies to construction work where an employee may be occupationally exposed to lead. Work related to construction, alteration, or repair (including painting and decorating) is included. The lead-in-construction standard applies to any detectable concentration of lead in paint, as even small concentrations of lead can result in unacceptable employee exposures depending upon on the method of removal and other workplace conditions. Under this standard construction includes, but is not limited to, the following:

§ Demolition or salvage of structures where lead or materials containing lead are present;

§ Removal or encapsulation of materials containing lead;

§ New construction, alteration, repair, or renovation of structures, substrates, or portions containing lead, or materials containing lead;

§ Installation of products containing lead;

§ Lead contamination/emergency clean-up;

§ Transportation, disposal, storage, or containment of lead or materials containing lead on the site or location at which construction activities are performed; and, § Maintenance operations associated with construction activities described above.

4.2 Sampling and Analytical Protocol

The LBP sampling was conducted by collecting random paint chip samples to supplement findings to assist the demolition/abatement contractor with determining potential engineering controls or other means to insure OSHA compliance during demolition efforts.

The paint samples were collected down to the surface substrate so as to include underlying paint (if present) in the analysis. The random paint chip samples were selected based on current paint schemes and may not be inclusive of old paint systems covered with paneling, or existing painted systems. The paint chip samples were submitted to an ELLAP approved laboratory (SAI) for analysis of lead by flame atomic absorption spectroscopy EPA Method No. SW-846 3050B/7000B. Results are reported in percent (%) by weight.

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4.3 Findings

Nineteen (19) paint-chip samples were collected from various components and submitted for laboratory analysis. The results of this analysis are summarized in Table 2 in Appendix B. A copy of the laboratory data report and chain of custody form is included in Appendix C. Lead was detected in eighteen (18) of the samples collected. Nine of the eighteen samples were analyzed to be above 0.5% by weight; therefore, these paints are considered to be lead-based paint by the EPA definition.

Paints exceeding 0.5% by weight are summarized below:

§ White paint on metal roof caps in the bell tower;

§ White paint on wooden windowsills in the Protestant Chapel;

§ Teal paint on brick walls in the basement;

§ White paint on wooden door to the crawlspace;

§ White paint on wooden door frame to the crawlspace;

§ White paint on the wooden exterior handrails;

§ White paint on wooden roof framing;

§ White paint on wooden window frames on the bell tower; and § White paint on wooden roof framing.

In addition to the above listed painted components, lead paint was identified and reported in the report titled Project 621-05-115 conducted by E. Roberts Alley and Associates, Inc. and dated January 27, 2006. These additional paints are identified as being on all interior wooden door and window components as well as exterior wooden components.

5.0 RECOMMENDATIONS

Asbestos A Tennessee-accredited asbestos abatement firm should be contracted to perform the asbestos-containing material removal prior to the renovation process. The following steps should be taken for the removal of the identified ACMs prior to renovations:

1. Notify (written) TDEC-DAPC officials of the impending abatement project at the following address:

State of Tennessee Department of Environment and Conservation Division of Air Pollution Control William R. Snodgrass Tennessee Tower 312 Rosa L. Parks Avenue, 15th Floor Nashville, Tennessee 37243-1531

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2. Remove the materials from the building before any activity begins that would break up, dislodge, or similarly disturb the material. The ACMs must be manifested and disposed at a classified landfill (Tennessee) or a landfill that is certified to accept RACM and non-RACM materials (if disposed in other states).

It should be noted that suspect materials, other than those identified during the January 12 and 13, 2021, survey may exist within the structure. Should suspect materials other than those which were identified during this survey be uncovered prior to or during the upcoming project, those materials should be assumed to be asbestos-containing until sampling and analysis demonstrates otherwise. Federal, state and local regulations should be referred to in order to verify compliance before any actions are initiated on an ACM.

Lead Containing Paint Regulatory agencies, such as the US EPA and the Consumer Products Safety Commission (CPSC) have designated levels of lead in paint, below which they consider the paint to be non-lead containing. The missions of these agencies differ from OSHA's, and for that reason, OSHA cannot recognize these levels as safe under workplace situations. The OSHA lead-in-construction standard was intended to apply to detectable concentrations of lead in paint, as even small concentrations of lead can result in unacceptable employee exposures depending upon on the method of removal and other workplace conditions.

OSHA does not consider methods that rely solely on the analysis of bulk materials or surface content of lead (or other toxic material) to be acceptable for safely predicting employee exposure to airborne contaminants. Without air monitoring results or without the benefit of historical or objective data (including air sampling which clearly demonstrates that the employee cannot be exposed above the action level during any process, operation, or activity) the analysis of bulk or surface samples cannot be used to determine employee airborne exposure. A full copy of the OSHA lead standard for construction industry may be found at OSHA’s website (www.osha.gov) and should be referenced for specific information.

Building materials, equipment, and components identified in this report as being coated with lead-containing paint/primer should be properly evaluated to determine if the paint system should be abated by qualified and properly equipped personnel under the OSHA Lead Construction Standard, found at 29 CFR 1926.62. The condition of the paint systems and the demolition activities intended for them will dictate the proper course of action, in terms of whether abatement is necessary. Waste generated from any abatement activities, as well as other materials contaminated from the abatement activities, must also be evaluated in terms of the hazardous waste Toxicity Characteristic. It is not required to fully abate the lead paint from the substrate for disposal or recycling efforts; however, the deteriorated paint and disturbance of paint must be addressed in accordance with 29 CFR 1926.62 and disposed of properly, as discussed above.

http://www.osha.gov/

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6.0 GENERAL COMMENTS

This survey was conducted in a manner consistent with the level of care and skill ordinarily exercised by members of the profession currently practicing under similar conditions in the same locale. The results, findings, conclusions and recommendations expressed in this report are based on conditions observed during our survey of the building. The information contained in this report is relevant to the date on which this survey was performed and may not be relied upon to represent conditions at a later date.

This report has been prepared on behalf of and exclusively for use by FFE, Inc. for specific application to their project as discussed. Terracon does not warrant the work of regulatory agencies, laboratories or other third parties supplying information, which may have been used in the preparation of this report (including information provided in historical survey reports provided for our review). No warranty, express or implied is made.

This report is not a bidding document. Contractors or consultants reviewing this report must draw their own conclusions regarding further investigation or remediation deemed necessary.

APPENDIX A

FIGURE

Figure

GKF 86207201

Drawn By: Scale:

VAMC Mountain Home

Building 13 - Chapel Lamont Street and Veterans Way

Johnson City, Tennessee

72 Pointe Circle Greenville, SC 29615

1/14/2021 PH. (864) 292-2901 FAX. (864) 292-6361

SNE N.T.S.

Checked By:

Building layout and sample locations are approximated. Base drawing provided by FFE, Inc.

Project Manager: Project No.

General Layout / Sample Locations

File Name:

GKF

Approved By: Date:

APPENDIX B

TABLES

A1 PLM

A2 PLM

A3 PLM

B1 PLM

B2 PLM

B3 PLM

C1 PLM

C2 PLM

C3 PLM

D1 PLM

D2 PLM

D3 PLM

E1 PLM

E2 PLM

E3 PLM

E4 PLM

E5 PLM

E6 PLM

E7 PLM

13 03A

## PLM

F1 PLM

F2 PLM

F3 PLM

G1 PLM

G2 PLM

G3 PLM

H1 PLM

H2 PLM

H3 PLM

I1 PLM

I2 NA

I3 NA

SF40% Chrysotile Closet Under Basement Stairs TSI Contaminated Debris I TSI Friable Significantly

Damaged

PSD 30

SF

NAD Vestibule Ceiling Tile, 2' X 4'

Birdwing and Dot Pattern H Miscellaneous Friable Good LPD 100 SF

NAD

Restrooms Behind Catholic

Chapel

Ceiling Tile, 2' X 4'

Birdwing and Dot Pattern G Miscellaneous Friable Damaged PD 300

SF

NAD Pipe Organs Fabric on the Pipe Organ

Bellows F Miscellaneous Friable Good LPD 20 SF

Base - NAD

Finish - NAD

Limited Surfacing - NAD

Throughout Interior Plaster E Surfacing Friable Damaged PD 6,000

SF

Drywall - NAD

Joint Compound - NAD

Restrooms behind Catholic

Chapel and Front Walls of the

Chapel

Drywall and Joint Compound D Miscellaneous /

Surfacing Friable Good LPD 850 SF

Floor Tile - NAD

Leveler/Mastic - NAD

Restrooms behind Catholic

Chapel

12" White Streaked Floor Tile and Gray Floor Leveler C Miscellaneous Non-Friable Good LPD 320

SF

NAD Protestant Chapel and Entry Way Yellow Carpet Mastic B Miscellaneous Non-Friable Good LPD 820 SF

NAD Chaplain and Vestry Area Residual Felt Paper A Miscellaneous Friable Damaged PD 90

TABLE 1

ASBESTOS RESULTS SAMPLE SUMMARY

LAMONT STREET AND VETERANS WAY

JOHNSON CITY, TENNESSEE

Sample

Number

Analysis

Method

Estimated

Quantity Sample Location

TERRACON PROJECT NO. 86207201

Sample Description Homogeneous

Area Classification

Current

Condition

Potential for

Disturbance

Friable /

Non-Friable Analytical Results

VAMC MOUNTAIN HOME - BUILDING 13 CHAPEL

TABLE 1

ASBESTOS RESULTS SAMPLE SUMMARY

LAMONT STREET AND VETERANS WAY

JOHNSON CITY, TENNESSEE

Sample

Number

Analysis

Method

Estimated

Quantity Sample Location

TERRACON PROJECT NO. 86207201

Sample Description Homogeneous

Area Classification

Current

Condition

Potential for

Disturbance

Friable /

Non-Friable Analytical Results

VAMC MOUNTAIN HOME - BUILDING 13 CHAPEL

J1 PLM

J2 PLM

J3 PLM

K1 PLM

K2 PLM

K3 PLM

L1 PLM

L2 PLM

L3 PLM

M1 PLM

M2 PLM

M3 PLM

N1 PLM

N2 NA

N3 NA

O1 PLM

O2 PLM

O3 PLM

P1 PLM

P2 NA

P3 NA

Q1 PLM

Q2 PLM

Q3 PLM

R1 PLM

R2 PLM

R3 PLM

S1 PLM

S2 PLM

S3 PLM

SF

3% Chrysotile Exterior Doors Caulking P Miscellaneous Friable Damaged PD 4 SF

Roof Flashing at Brick and

Copper Interface Residual Flashing Mastic S Miscellaneous

Category I

Non-Friable Good LPD 200 LF

NAD

NAD

NAD

NAD

2% Chrysotile

NAD

5% Chrysotile

Basement and Crawlspace

Basement

Intake Duct Work in

Bell Tower

Chapel Windows

2% Chrysotile Exterior Concrete Sill Blocks

6% Chrysotile Downspout Connections

SF

Gray Mortar Joint Caulking Q Miscellaneous Category II

Non-Friable Good LPD 50 SF

Black Mastic R Miscellaneous Category II

Non-Friable Good LPD 12

Silver Duct Mastic N Miscellaneous Friable Significantly

Damaged

PSD 20

Light Brown Duct Mastic O Miscellaneous Non-Friable Good LPD 150

SF

M Miscellaneous Non-Friable Good LPD 150 SFFelt Paper under Subflooring

Gray Interior Window Caulking L Miscellaneous Non-Friable Good LPD 20 SF

SFCloset under Basement Stairs Black Fabric Duct Elbow J Miscellaneous Friable

Basement and Crawlspace White Mastic on Pipe Ends K Miscellaneous Non-Friable Good LPD 100 SF

Good LPD 3

TABLE 1

ASBESTOS RESULTS SAMPLE SUMMARY

LAMONT STREET AND VETERANS WAY

JOHNSON CITY, TENNESSEE

Sample

Number

Analysis

Method

Estimated

Quantity Sample Location

TERRACON PROJECT NO. 86207201

Sample Description Homogeneous

Area Classification

Current

Condition

Potential for

Disturbance

Friable /

Non-Friable Analytical Results

VAMC MOUNTAIN HOME - BUILDING 13 CHAPEL

T1 PLM

T2 PLM

T3 PLM

Notes:

N/A N/A Brown/Gold Stair Tread Mastic 13A-12** Miscellaneous Category II

Non-Friable Good LPD 60 SF

Felt Paper under Slate T Miscellaneous Non-Friable Good LPD 6,875 SF

2% Chrysotile Stairwells to Organ Loft

NAD Slate Roof

NA - Not Analyzed

NAD - No Asbestos Detected

PLM - Polarized Light Microscopy

TEM - Transmission Electron Microscopy

PACM - Presumed Asbestos Containing Material

1) Quantities listed above are estimates to be used for inspection purposes only and should be field-verified for all other uses.

2) A general overview of the site is depicted on Figure 1.

** - Previously sampled and identified in the report Project 621-05-115 conducted by E. Roberts Alley & Associates, Inc. dated January 27, 2006

## - Sample 13 03A was collected as part of the survey in report Comprehensive Asbestos-Containing Materials Inspection conducted EFI Global dated January 2010.

LPD - Low potential for disturbance

PD - Potential for disturbance

PSD - Potential of significant disturbance

SF - square feet

LF - linear feet

CF - cubic feet

Sample ID

No.

Area Substrate Component Color

Lead

Concentration

PC-1 BellTower Metal Roof Cap White 17.0

PC-2 Chaplain's Office Plaster Wall White 0.160

PC-3 Chaplain's Office Plaster Ceiling White 0.150

PC-4 Protestant Chapel Wood Door Frame Tan <0.0075

PC-5 Protestant Chapel Plaster Wall White 0.130

PC-6 Catholic Chapel Wood Door White 0.170

PC-7 Catholic Chapel Wood Door Frame White 0.230

PC-8 Entryway Wood Door Tan 0.110

PC-9 Vestibule Wood Newel Post Tan 0.077

PC-10 Vestibule Wood Stair Tread Gray 0.240

PC-11 Proestant Chapel Wood Windowsill White 0.86

PC-12 Basement Brick Wall Teal 2.2

PC-13 Basement Wood Floor Joist Teal 0.150

PC-14 Crawlspace Wood Door White 19

PC-15 Crawlspace Wood Door Frame White 1.4

PC-16 Exterior Wood Handrail White 27

PC-17 Exterior Wood Roof Framing White 19

PC-18 Exterior Bell Tower Wood Window Frame White 32

PC-19 Exterior Wood Roof Framing White 4.9

Notes:

1) Values above the analytical method detection limit are indicated in bold type.

2) Values equal to or greater than 0.500 percent are bolded and shaded.

TABLE 2

LEAD IN PAINT SAMPLE SUMMARY (PAINT CHIP)

VAMC MOUNTAIN HOME - BUILDING 13 CHAPEL

JOHNSON CITY, TENNESSEE

TERRACON PROJECT NO. 86207201

LAMONT STREET AND VETERANS WAY

APPENDIX C

LABORATORY REPORTS

Bulk Asbestos Analysis By Polarized Light Microscopy

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

None Detected A1

Residual Felt Paper Black Fibrous Homogeneous

Teased, Dissolved71958030PLM_1

Cellulose Other 70% 30%

None Detected A2

Residual Felt Paper Black Fibrous Homogeneous

Teased, Dissolved71958030PLM_2

Cellulose Other 70% 30%

None Detected A3

Residual Felt Paper Black Fibrous Homogeneous

Teased, Dissolved71958030PLM_3

Cellulose Other 70% 30%

None Detected B1

Yellow Carpet Mastic mixed mastic

Brown, Yellow Non Fibrous Heterogeneous

Dissolved71958030PLM_4

Other 100%

None Detected B2

Yellow Carpet Mastic mixed mastic

Brown, Yellow Non Fibrous Heterogeneous

Dissolved71958030PLM_5

Other 100%

None Detected B3

Yellow Carpet Mastic mixed mastic

Brown, Yellow Non Fibrous Heterogeneous

Dissolved71958030PLM_6

Other 100%

None Detected C1 - A

White Floor Tile and Gray Leveler floor tile

White Non Fibrous Homogeneous

Dissolved71958030PLM_7

Other 100%

None Detected C1 - B

White Floor Tile and Gray Leveler mastic/leveling compound

Gray, Yellow Non Fibrous Heterogeneous

Dissolved71958030PLM_65

Other 100%

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

Byron Stroble (76)

P-F-002 r15 1/16/2021

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

None Detected C2 - A

White Floor Tile and Gray Leveler floor tile

White Non Fibrous Homogeneous

Dissolved71958030PLM_8

Other 100%

None Detected C2 - B

White Floor Tile and Gray Leveler mastic/leveling compound

Gray, Yellow Non Fibrous Heterogeneous

Dissolved71958030PLM_66

Other 100%

None Detected C3 - A

White Floor Tile and Gray Leveler floor tile

White Non Fibrous Homogeneous

Dissolved71958030PLM_9

Other 100%

None Detected C3 - B

White Floor Tile and Gray Leveler mastic/leveling compound

Gray, Yellow Non Fibrous Heterogeneous

Dissolved71958030PLM_67

Other 100%

None Detected D1

Drywall and Joint Compound drywall: none detect; joint compnd: none detect

Brown, White Non Fibrous Heterogeneous

Teased71958030PLM_10

Cellulose Other 10% 90%

None Detected D2

Drywall and Joint Compound drywall: none detect; joint compnd: none detect

White, Brown Non Fibrous Heterogeneous

Teased71958030PLM_11

Cellulose Other 10% 90%

None Detected D3

Drywall and Joint Compound drywall: none detect; joint compnd: none detect

Brown, White Non Fibrous Heterogeneous

Teased71958030PLM_12

Cellulose Other 10% 90%

None Detected E1 - A

Plaster surfacing

White Non Fibrous Homogeneous

Teased71958030PLM_13

Other 100%

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

None Detected E1 - B

Plaster finish

White Non Fibrous Homogeneous

Crushed71958030PLM_68

Other 100%

None Detected E1 - C

Plaster base

Gray Non Fibrous Homogeneous

Crushed71958030PLM_69

Other 100%

None Detected E2 - A

Plaster surfacing

White Non Fibrous Homogeneous

Teased71958030PLM_14

Other 100%

None Detected E2 - B

Plaster finish

White Non Fibrous Homogeneous

Teased71958030PLM_70

Other 100%

None Detected E2 - C

Plaster base

Gray Non Fibrous Homogeneous

Crushed71958030PLM_71

Other 100%

None Detected E3 - A

Plaster finish

White Non Fibrous Homogeneous

Teased71958030PLM_15

Other 100%

None Detected E3 - B

Plaster base

Gray Non Fibrous Homogeneous

Crushed71958030PLM_72

Other 100%

None Detected E4 - A

Plaster finish

White Non Fibrous Homogeneous

Teased71958030PLM_16

Other 100%

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

None Detected E4 - B

Plaster base

Gray Non Fibrous Homogeneous

Crushed71958030PLM_73

Other 100%

None Detected E5 - A

Plaster finish

White Non Fibrous Homogeneous

Teased71958030PLM_17

Other 100%

None Detected E5 - B

Plaster base

Gray Non Fibrous Homogeneous

Crushed71958030PLM_74

Other 100%

None Detected E6 - A

Plaster surfacing

White Non Fibrous Homogeneous

Teased71958030PLM_18

Other 100%

None Detected E6 - B

Plaster single layer

Gray Non Fibrous Homogeneous

Crushed71958030PLM_75

Other 100%

None Detected E7 - A

Plaster finish

White Non Fibrous Homogeneous

Crushed71958030PLM_19

Other 100%

None Detected E7 - B

Plaster base

Gray Non Fibrous Homogeneous

Crushed71958030PLM_76

Other 100%

None Detected F1

Pipe Bellow Fabric Beige Non Fibrous Heterogeneous

Ashed71958030PLM_20

Cellulose Other 40% 60%

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

None Detected F2

Pipe Bellow Fabric Green Non Fibrous Heterogeneous

Ashed71958030PLM_21

Synthetic Fibers Cellulose

Other 30% 10%

60%

None Detected F3

Pipe Bellow Fabric Beige Fibrous Heterogeneous

Ashed71958030PLM_22

Cellulose Synthetic Fibers

Other 30% 20%

50%

None Detected G1

Ceiling Tile, Birdwing and Dot Pattern

Gray Fibrous Homogeneous

Teased, Ashed71958030PLM_23

Cellulose Mineral Wool

Other 45% 45%

10%

None Detected G2

Ceiling Tile, Birdwing and Dot Pattern

Gray Fibrous Homogeneous

Teased, Ashed71958030PLM_24

Cellulose Mineral Wool

Other 45% 45%

10%

None Detected G3

Ceiling Tile, Birdwing and Dot Pattern

Gray Fibrous Homogeneous

Teased, Ashed71958030PLM_25

Cellulose Mineral Wool

Other 45% 45%

10%

None Detected H1

Ceiling Tile, Pinhole and Dot Pattern

Gray, Pink Fibrous Homogeneous

Teased, Ashed71958030PLM_26

Cellulose Mineral Wool

Other 45% 45%

10%

None Detected H2

Ceiling Tile, Pinhole and Dot Pattern

Gray, Pink Fibrous Homogeneous

Teased, Ashed71958030PLM_27

Cellulose Mineral Wool

Other 45% 45%

10%

None Detected H3

Ceiling Tile, Pinhole and Dot Pattern

Gray, Pink Fibrous Homogeneous

Teased, Ashed71958030PLM_28

Cellulose Mineral Wool

Other 45% 45%

10%

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

40% Chrysotile

I1 TSI Debris

Gray Fibrous Homogeneous

Teased71958030PLM_29

Cellulose Other 20% 40%

Not Analyzed I2

TSI Debris

71958030PLM_30

Not Analyzed I3

TSI Debris

71958030PLM_31

None Detected J1

Fabric Duct Elbow Black, Beige Fibrous Heterogeneous

Teased, Dissolved71958030PLM_32

Cellulose Other 60% 40%

None Detected J2

Fabric Duct Elbow Black, Beige Fibrous Heterogeneous

Teased, Dissolved71958030PLM_33

Cellulose Other 60% 40%

None Detected J3

Fabric Duct Elbow Black, Beige Fibrous Heterogeneous

Teased, Dissolved71958030PLM_34

Cellulose Other 60% 40%

None Detected K1

White Mastic on Pipe Ends Beige Non Fibrous Homogeneous

Dissolved71958030PLM_35

Wollastonite Other 10% 90%

None Detected K2

White Mastic on Pipe Ends Beige Non Fibrous Homogeneous

Dissolved71958030PLM_36

Wollastonite Other 10% 90%

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

None Detected K3

White Mastic on Pipe Ends Beige Non Fibrous Homogeneous

Dissolved71958030PLM_37

Wollastonite Other 10% 90%

None Detected L1

Gray Window Caulking Gray Non Fibrous Homogeneous

Ashed71958030PLM_38

Other 100%

None Detected L2

Gray Window Caulking Gray Non Fibrous Homogeneous

Ashed71958030PLM_39

Other 100%

None Detected L3

Gray Window Caulking Gray Non Fibrous Homogeneous

Ashed71958030PLM_40

Other 100%

None Detected M1

Felt Paper on Subflooring Black Fibrous Homogeneous

Teased, Dissolved71958030PLM_41

Cellulose Other 80% 20%

None Detected M2

Felt Paper on Subflooring Black Fibrous Homogeneous

Teased, Dissolved71958030PLM_42

Cellulose Other 80% 20%

None Detected M3

Felt Paper on Subflooring Black Fibrous Homogeneous

Teased, Dissolved71958030PLM_43

Cellulose Other 80% 20%

2% Chrysotile

N1 Silver Duct Mastic

Silver Non Fibrous Homogeneous

Dissolved71958030PLM_44

Other 98%

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

Not Analyzed N2

Silver Duct Mastic

71958030PLM_45

Not Analyzed N3

Silver Duct Mastic

71958030PLM_46

None Detected O1

Lt Brown Duct Mastic Brown Non Fibrous Homogeneous

Dissolved71958030PLM_47

Other 100%

None Detected O2

Lt Brown Duct Mastic Brown Non Fibrous Homogeneous

Dissolved71958030PLM_48

Other 100%

None Detected O3

Lt Brown Duct Mastic Brown Non Fibrous Homogeneous

Dissolved71958030PLM_49

Other 100%

3% Chrysotile

P1 Exterior Door Caulking

Gray Non Fibrous Homogeneous

Ashed71958030PLM_50

Other 97%

Not Analyzed P2

Exterior Door Caulking

71958030PLM_51

Not Analyzed P3

Exterior Door Caulking

71958030PLM_52

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

2% Chrysotile

Q1 Gray Mortar Joint Caulking

Gray Non Fibrous Homogeneous

Ashed71958030PLM_53

Other 98%

Not Analyzed Q2

Gray Mortar Joint Caulking

71958030PLM_54

Not Analyzed Q3

Gray Mortar Joint Caulking

71958030PLM_55

6% Chrysotile

R1 Downspout Mastic

Black Non Fibrous Homogeneous

Dissolved71958030PLM_56

Cellulose Other 14% 80%

Not Analyzed R2

Downspout Mastic

71958030PLM_57

Not Analyzed R3

Downspout Mastic

71958030PLM_58

5% Chrysotile

S1 Residual Flashing Mastic

Gray, Black Non Fibrous Homogeneous

Dissolved71958030PLM_59

Other 95%

Not Analyzed S2

Residual Flashing Mastic

71958030PLM_60

Disclaimer: Due to the nature of the EPA 600 method, asbestos may not be detected in samples containing low levels of asbestos. We strongly recommend that analysis of floor tiles, vermiculite, and/or heterogeneous soil samples be conducted by TEM for confirmation of “None Detected” by PLM. This report relates only to the samples tested and may not be reproduced, except in full, without the written approval of SAI. This report may not be used by the client to claim product endorsement by NVLAP or any other agency of the U.S. government. Analytical uncertainty available upon request. Scientific Analytical Institute participates in the NVLAP Proficiency Testing program. Unless otherwise noted blank sample correction was not performed. Estimated MDL is 0.1%.

Approved SignatoryAnalyst

Scientific Analytical Institute, Inc. 4604 Dundas Dr. Greensboro, NC 27407 (336) 292-3888

EPA Method: 600/R-93/116 and 40 CFR, Part 763, Subpart E, App.E

VAMC Bldg 13 Chapel 86207201Project:

Sample ID

Lab Sample ID

Description

Lab Notes Asbestos Fibrous

Components Non-Fibrous Components

Attributes

Treatment

Stephen Ellis George Flores

Attn:Customer: Terracon 72 Pointe Circle Greenville, SC 29615

Analysis ID: 71958030_PLM

Date Reported: 1/21/2021

Date Received: 1/18/2021

Lab Order ID: 71958030

Not Analyzed S3

Residual Flashing Mastic

71958030PLM_61

None Detected T1

Felt Paper under Slate…