HAZMAT REPORT, SPECIFICATIONS,

AND DRAWINGS FOR DRIVE-THROUGH

BANK BUILDING

CITY OF SUFFOLK

GODWIN – VIRGINIAN PILOT

BUILDING RENOVATION

157 N MAIN STREET

SUFFOLK, VA 23434

PROJECT NO. 10015069.02

DOCUMENTS

27 AUGUST 2026

WOOLPERT

4433 CORPORATION LANE, SUITE 125

VIRGINIA BEACH, VIRGINIA 23462

(757) 549-3549; FAX (937) 461-0743

This Page Intentionally Left Blank This Page Intentionally Left Blank

DRIVE-THROUGH LANE 1

DRIVE-THROUGH LANE 2

RESTROOM TELLER ROOM

ARCHITECTURE ENGINEERING GEOSPATIAL│ │

4454 IDEA CENTER BOULEVARD

DAYTON, OH 45430-1500

937.461.5660

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HAZMAT GENERAL

NOTES, PHOTOS &

OVERALL FLOOR PLAN

H-101

A. A HAZARDOUS MATERIALS INSPECTION WAS PERFORMED. THE SURVEY/INSPECTION REPORT IS PROVIDED IN THE SPECIFICATIONS/CONTRACT DOCUMENT. THE WORK WILL REQUIRE THE REMOVAL OF ASSUMED ASBESTOS-CONTAINING MATERIALS (ACM). DESTRUCTIVE ACTIVITIES SUCH AS BREAKING INTO WALLS, CEILINGS AND FLOORS WERE NOT PERFORMED IN ORDER TO LOCATE MATERIALS. THEREFORE, IF DURING THE WORK SUSPECT MATERIALS ARE UNCOVERED, NOTIFY THE CONTRACTING OFFICER AND

STOP WORK UNTIL THE MATERIAL IS PROPERLY IDENTIFIED AND ADDRESSED.

B. THE CONTRACT DOCUMENTS REPRESENT CONDITIONS WITHIN THE FACILITY AT THE TIME OF THE INITIAL FIELD INVESTIGATION. REFER TO REPORT TO DETERMINE THOSE CONDITIONS. SHOULD CONDITIONS EXISTS OTHER THAN THOSE INDICATED IN THE REPORT, CONSULT THE CONTRACTING OFFICER FOR VERIFICATION.

C. CONTRACTOR MUST VISIT THE SITE TO ASCERTAIN THE EXACT NATURE AND LOCATION OF THE WORK INCLUDING THE WORK OR COST THEREOF.

D. CONTRACTOR MUST COORDINATE ALL ASPECTS OF THE WORK WITH OTHER TRADES. SEE ARCHITECTURAL, CIVIL, MECHANICAL, PLUMBING, AND ELECTRICAL DEMOLITION

DRAWINGS.

E. EXISTING PAINT WITHIN THE STRUCTURE HAS BEEN DETERMINED TO CONTAIN CONCENTRATIONS ABOVE THE LABORATORY'S MINIMUM DETECTION LIMIT OF THE FOLLOWING METALS: LEAD, CADMIUM AND CHROMIUM. EXTERIOR PAINTED SURFACES ARE LEAD-BASED PAINT. PERFORM RENOVATION WORK IN ACCORDANCE WITH SPECIFICATION SECTION 02 83 00 "LEAD REMEDIATION". CONSTRUCTION STANDARDS ESTABLISHED BY OSHA FOR CHROMIUM, CADMIUM AND LEAD ARE; CHROMIUM, 29 CFR 1926.1126;

CADMIUM, 29 CFR 1926.1127 AND LEAD, 29 CFR 1926.62

F. TOXICITY CHARACTERISTIC LEACHING PROCEDURE (TCLP) TESTING ON EXISTING PAINTED BUILDING MATERIALS, WHEN DEMOLISHED AS COMPONENTS OF AN ASSEMBLY TYPICALLY RETURN RESULTS CLASSIFYING THE WASTE AS NONHAZARDOUS. PAINTED MATERIAL REMOVED IN THE FORM OF STRIPPING, BLASTING, SCRAPING OR OTHER METHODS THAT REMOVE THE PAINT COATING FROM THE EXISTING SUBSTRATE, OR PRODUCES A WASTE RESULTING PRIMARILY OF PAINT MATERIAL, MAY RESULT IN WASTE CLASSIFIED AS HAZARDOUS. THE CONTRACTOR MUST COORDINATE THE WORK PROCEDURES TO CHARACTERIZE THE ANTICIPATED WASTE STREAM. CONTRACTOR IS RESPONSIBLE FOR ALL COSTS ASSOCIATED WITH CHARACTERIZATION AND DISPOSAL OF WASTE GENERATED FROM THE WORK.

G. ALL LIGHT BALLASTS WITHOUT "NON PCB" MARKINGS AND ALL FLUORESCENT LIGHT TUBES MUST BE REMOVED IN ACCORDANCE WITH SPECIFICATION SECTION 02 84 16. FOR BIDDING PURPOSES, ASSUME ALL FLUORESCENT LIGHT TUBES CONTAIN MERCURY VAPOR. COORDINATE WASTE DISPOSAL AND ACCUMULATION WITH THE OWNER PRIOR TO

WASTE GENERATION ACTIVITIES.

H. DISASSEMBLE, REMOVE, AND INSPECT DOORS TO BE REMOVED TO DETERMINE ASBESTOS CONTENT. THE INSPECTION MUST BE PERFORMED BY A VIRGINIA LICENSED ASBESTOS INSPECTOR. REMOVE, HANDLE, AND DISPOSE OF ASBESTOS DOORS IN ACCORDANCE WITH SPECIFICATION SECTION 02 82 00. NON-ASBESTOS DOORS MUST BE DISPOSED OF AS REGULAR CONSTRUCTION WASTE. FOR BIDDING PURPOSES, ASSUME 2 ASBESTOS-CONTAINING DOORS EXIST (TOTAL FOR PROJECT).

I. MANAGE ALL WASTE IN ACCORDANCE WITH ALL LOCAL, STATE AND FEDERAL REGULATIONS INCLUDING 40 CFR 261 AND 40 CFR 262. COMPLY WITH ALL ENVIRONMENTAL

REQUIREMENTS.

(H-101)

PHOTOGRAPH LOCATION.

KEY TO SYMBOLS

REFERENCE PHOTOGRAPH NOTES

1. EAST FACING VIEW OF THE BUILDING.

2. VIEW OF GYPSUM SACT CEILING TILE AND EXTERIOR LIGHTING. LED AND T-8 LIGHT TUBES WERE OBSERVED.

3. VIEW BEHIND LOOSE BRICKS EXPOSING PLASTIC SHEETING AS VAPOR BARRIER BEHIND BRICK VENEER.

4. VIEW OF THE BUILT-UP ROOF CURRENTLY SERVING THE BUILDING. THIS MATERIAL WAS NOT ACM.

5. VIEW OF THE ENTRYWAY/EXIT OF THE BUILDING. BROWN PAINT ON THE DOOR AND FRAME IS LEAD, CADMIUM, AND CHROMIUM CONTAINING.

6. TYPICAL INTERIOR VIEW OF THE BUILDING. NO SAMPLES COLLECTED WERE DETERMINED TO CONTAIN ASBESTOS.

HAZMAT GENERAL NOTES

PLASTIC VAPOR BARRIER

SHEETING

H-101SCALE:

REFERENCE PHOTO - NOTE 1A1 NO SCALE H-101SCALE:

REFERENCE PHOTO - NOTE 2A2 NO SCALE H-101SCALE:

REFERENCE PHOTO - NOTE 3A3 NO SCALE

H-101SCALE:

REFERENCE PHOTO - NOTE 4B1 NO SCALE H-101SCALE:

REFERENCE PHOTO - NOTE 5B2 NO SCALE H-101SCALE:

REFERENCE PHOTO - NOTE 6B3 NO SCALE

(H-101)

SCALE: 1/4" = 1'-0"

OVERALL FLOOR PLAN - HAZMAT REMOVAL

SHEET KEYNOTES XX

1. INSPECT FIRE DOORS FOR ASBESTOS CONTENT.

(H-101)

DRIVE-THROUGH LANE 1

DRIVE-THROUGH LANE 2

RESTROOM TELLER ROOM

ARCHITECTURE ENGINEERING GEOSPATIAL│ │

4454 IDEA CENTER BOULEVARD

DAYTON, OH 45430-1500

937.461.5660

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HAZMAT GENERAL

NOTES, PHOTOS &

OVERALL FLOOR PLAN

H-101

A. A HAZARDOUS MATERIALS INSPECTION WAS PERFORMED. THE SURVEY/INSPECTION REPORT IS PROVIDED IN THE SPECIFICATIONS/CONTRACT DOCUMENT. THE WORK WILL REQUIRE THE REMOVAL OF ASSUMED ASBESTOS-CONTAINING MATERIALS (ACM). DESTRUCTIVE ACTIVITIES SUCH AS BREAKING INTO WALLS, CEILINGS AND FLOORS WERE NOT PERFORMED IN ORDER TO LOCATE MATERIALS. THEREFORE, IF DURING THE WORK SUSPECT MATERIALS ARE UNCOVERED, NOTIFY THE CONTRACTING OFFICER AND

STOP WORK UNTIL THE MATERIAL IS PROPERLY IDENTIFIED AND ADDRESSED.

B. THE CONTRACT DOCUMENTS REPRESENT CONDITIONS WITHIN THE FACILITY AT THE TIME OF THE INITIAL FIELD INVESTIGATION. REFER TO REPORT TO DETERMINE THOSE CONDITIONS. SHOULD CONDITIONS EXISTS OTHER THAN THOSE INDICATED IN THE REPORT, CONSULT THE CONTRACTING OFFICER FOR VERIFICATION.

C. CONTRACTOR MUST VISIT THE SITE TO ASCERTAIN THE EXACT NATURE AND LOCATION OF THE WORK INCLUDING THE WORK OR COST THEREOF.

D. CONTRACTOR MUST COORDINATE ALL ASPECTS OF THE WORK WITH OTHER TRADES. SEE ARCHITECTURAL, CIVIL, MECHANICAL, PLUMBING, AND ELECTRICAL DEMOLITION

DRAWINGS.

E. EXISTING PAINT WITHIN THE STRUCTURE HAS BEEN DETERMINED TO CONTAIN CONCENTRATIONS ABOVE THE LABORATORY'S MINIMUM DETECTION LIMIT OF THE FOLLOWING METALS: LEAD, CADMIUM AND CHROMIUM. EXTERIOR PAINTED SURFACES ARE LEAD-BASED PAINT. PERFORM RENOVATION WORK IN ACCORDANCE WITH SPECIFICATION SECTION 02 83 00 "LEAD REMEDIATION". CONSTRUCTION STANDARDS ESTABLISHED BY OSHA FOR CHROMIUM, CADMIUM AND LEAD ARE; CHROMIUM, 29 CFR 1926.1126;

CADMIUM, 29 CFR 1926.1127 AND LEAD, 29 CFR 1926.62

F. TOXICITY CHARACTERISTIC LEACHING PROCEDURE (TCLP) TESTING ON EXISTING PAINTED BUILDING MATERIALS, WHEN DEMOLISHED AS COMPONENTS OF AN ASSEMBLY TYPICALLY RETURN RESULTS CLASSIFYING THE WASTE AS NONHAZARDOUS. PAINTED MATERIAL REMOVED IN THE FORM OF STRIPPING, BLASTING, SCRAPING OR OTHER METHODS THAT REMOVE THE PAINT COATING FROM THE EXISTING SUBSTRATE, OR PRODUCES A WASTE RESULTING PRIMARILY OF PAINT MATERIAL, MAY RESULT IN WASTE CLASSIFIED AS HAZARDOUS. THE CONTRACTOR MUST COORDINATE THE WORK PROCEDURES TO CHARACTERIZE THE ANTICIPATED WASTE STREAM. CONTRACTOR IS RESPONSIBLE FOR ALL COSTS ASSOCIATED WITH CHARACTERIZATION AND DISPOSAL OF WASTE GENERATED FROM THE WORK.

G. ALL LIGHT BALLASTS WITHOUT "NON PCB" MARKINGS AND ALL FLUORESCENT LIGHT TUBES MUST BE REMOVED IN ACCORDANCE WITH SPECIFICATION SECTION 02 84 16. FOR BIDDING PURPOSES, ASSUME ALL FLUORESCENT LIGHT TUBES CONTAIN MERCURY VAPOR. COORDINATE WASTE DISPOSAL AND ACCUMULATION WITH THE OWNER PRIOR TO

WASTE GENERATION ACTIVITIES.

H. DISASSEMBLE, REMOVE, AND INSPECT DOORS TO BE REMOVED TO DETERMINE ASBESTOS CONTENT. THE INSPECTION MUST BE PERFORMED BY A VIRGINIA LICENSED ASBESTOS INSPECTOR. REMOVE, HANDLE, AND DISPOSE OF ASBESTOS DOORS IN ACCORDANCE WITH SPECIFICATION SECTION 02 82 00. NON-ASBESTOS DOORS MUST BE DISPOSED OF AS REGULAR CONSTRUCTION WASTE. FOR BIDDING PURPOSES, ASSUME 2 ASBESTOS-CONTAINING DOORS EXIST (TOTAL FOR PROJECT).

I. MANAGE ALL WASTE IN ACCORDANCE WITH ALL LOCAL, STATE AND FEDERAL REGULATIONS INCLUDING 40 CFR 261 AND 40 CFR 262. COMPLY WITH ALL ENVIRONMENTAL

REQUIREMENTS.

(H-101)

PHOTOGRAPH LOCATION.

KEY TO SYMBOLS

REFERENCE PHOTOGRAPH NOTES

1. EAST FACING VIEW OF THE BUILDING.

2. VIEW OF GYPSUM SACT CEILING TILE AND EXTERIOR LIGHTING. LED AND T-8 LIGHT TUBES WERE OBSERVED.

3. VIEW BEHIND LOOSE BRICKS EXPOSING PLASTIC SHEETING AS VAPOR BARRIER BEHIND BRICK VENEER.

4. VIEW OF THE BUILT-UP ROOF CURRENTLY SERVING THE BUILDING. THIS MATERIAL WAS NOT ACM.

5. VIEW OF THE ENTRYWAY/EXIT OF THE BUILDING. BROWN PAINT ON THE DOOR AND FRAME IS LEAD, CADMIUM, AND CHROMIUM CONTAINING.

6. TYPICAL INTERIOR VIEW OF THE BUILDING. NO SAMPLES COLLECTED WERE DETERMINED TO CONTAIN ASBESTOS.

HAZMAT GENERAL NOTES

PLASTIC VAPOR BARRIER

SHEETING

H-101SCALE:

REFERENCE PHOTO - NOTE 1A1 NO SCALE H-101SCALE:

REFERENCE PHOTO - NOTE 2A2 NO SCALE H-101SCALE:

REFERENCE PHOTO - NOTE 3A3 NO SCALE

H-101SCALE:

REFERENCE PHOTO - NOTE 4B1 NO SCALE H-101SCALE:

REFERENCE PHOTO - NOTE 5B2 NO SCALE H-101SCALE:

REFERENCE PHOTO - NOTE 6B3 NO SCALE

(H-101)

SCALE: 1/4" = 1'-0"

OVERALL FLOOR PLAN - HAZMAT REMOVAL

SHEET KEYNOTES XX

1. INSPECT FIRE DOORS FOR ASBESTOS CONTENT.

(H-101)

Drive-through Bank Building & Roof Inspection

120 N. Saratoga Street Suffolk, VA

GER 130-8471

Prepared for

Woolpert 4433 Corporation Lane, Suite 125

Virginia Beach, VA 23462

Prepared by Wyatt S. Pine

VA Asbestos Inspector # 3303004643

BEQ 288

REPORT OF

HAZARDOUS MATERIALS

CONSULTING SERVICES

Southern Professional Center 1 2712 Southern Boulevard, Suite 101 Virginia Beach, Virginia 23452

(757) 463-3200 Fax (757) 463-3080 E-mail germail@geronline.com

August 26, 2026

Woolpert, Inc.

4433 Corporation Lane, Suite 125 Virginia Beach, VA 23462

Attention: Kristi Barker

Subject: Hazardous Materials Building & Roof Inspection Report Drive-through Bank Building & Roof Inspection 120 N. Saratoga Street Suffolk, Virginia GER Project # 130-8471

GeoEnvironmental Resources, Inc. has completed our hazardous materials sampling of the subject facility. This work was completed in accordance with the scope of work and fee outlined in our proposal P26-130-8398 dated July 31, 2026. This report is relevant to the date of our field work and should not be relied upon for later dates.

We appreciate the opportunity of completing this work for Woolpert, Inc. (Woolpert). If there are any questions concerning this report, please contact us.

Sincerely, GeoEnvironmental Resources, Inc.

Wyatt S. Pine H. Nelson Adcock, Jr., P.E.

Hazardous Materials Project Manager President Virginia Asbestos Inspector (#3303004643) VA Asbestos Inspector (#3303001776)

Attachments: (1) Hazardous Materials Report

(2) Laboratory Reports

(3) Sample Location Plans

(4) Photographs

(5) Licenses

Southern Professional Center I 2712 Southern Boulevard, Suite 101 Virginia Beach, Virginia 23452

(757) 463-3200 Fax (757) 463-3080 E-mail germail@geronline.com

Section 2 Laboratory Analytical Results

Section 1 Report

Section 3 Sample Location Maps

Section 4 Photographs

Section 5 Licenses

ACRONYMS

AAS Atomic absorption spectroscopy ACBM Asbestos-containing building materials ACM Asbestos-containing materials ACT Acoustical ceiling tile ADA Americans with Disability Act AHERA Asbestos Hazard Emergency Response Act ASHARA Asbestos Schools Hazard Abatement Reauthorization Act ASTM American Society of Testing and Materials CMU Cement masonry unit CFC Chlorofluoro carbons CHMM Certified Hazardous Materials Manager CFR Code of Federal Regulation CSP Certified Safety Professional DEHP Di (2-ethylhexyl) phthalate DRO Diesel Range Organics ECD Electron capture detectors EA Each EPA U.S. Environmental Protection Agency GC Gas chromatography GRO Gasoline Range Organics GWB Gypsum wall board HBM Hazardous building material HID High intensity discharge HM Homogeneous material HUD U.S. Housing and Urban Development LBP Lead-based paint LF Linear feet LS Lump sum MDL Minimum detection limit mg/cm2 Milligrams per square centimeter mg/kg Milligrams per kilogram mg/L Milligrams per Liter ND none detected NVLAP National Voluntary Laboratory Accreditation Program OSHA Occupational Safety and Health Administration PCB Polychlorinated biphenyl PLM Polarized light microscopy ppm Parts per million RCRA Resource Conservation and Recovery Act SAP Sample and Analysis Plan SF Square Feet TCLP Toxicity characteristic leaching procedure TPH Total Petroleum Hydrocarbons TSI Thermal System Insulation VAC Virginia Administration Code VOC Volatile Organic Compound XRF X-Ray Fluorescence

PROJECT DESCRIPTION

It is our understanding the current structure located at 120 N. Saratoga Street in Suffolk, VA is expected to be demolished.

The renovation/demolition will require disturbance of existing suspect hazardous materials associated with the renovation project. Prior to the demolition work, existing hazardous materials must be identified and appropriate precautions taken prior to their disturbance in order to protect workers and the environment.

At the time of our initial inspection in August 2026 the building was generally intact with interior walls and ceilings.

SAMPLING METHODOLOGIES

SUSPECT ASBESTOS-CONTAINING MATERIALS

(ACM)

The AHERA regulation, 40 Code of Federal Regulations (CFR) 763, is the primary governing regulation when performing asbestos surveys. This regulation was originally enacted for school buildings, but has since been applied to public and commercial buildings by the Asbestos School Hazard Abatement Reauthorization Act (ASHARA) in 1994 and by the Occupational Safety and Health Administration’s (OSHA) worker protection regulations in 1995, specifically 29 CFR 1926.1101(k).

The demolition of structures is also subject to 40 CFR Part 61 “National Emission Standards for Hazardous Air Pollutants” (NESHAPs).

Asbestos-Containing Material (ACM) is specifically addressed in 40 CFR 61 Subpart M “National Emission Standard for Asbestos.”

ACM is generally divided into three primary classifications as follows: (a) Surfacing material, (b) Thermal System Insulation, and (c) Miscellaneous material. These classifications are defined in 40 CFR 763.83 as provided below.

Miscellaneous material means interior building on structural components, structural members or fixtures, such as floor and ceiling tiles, and does not include surfacing material or thermal system insulation.

Surfacing material means material in a building that is sprayed-on, troweled-on, or otherwise applied to surfaces, such as acoustical plaster on ceilings and fireproofing materials on Page 5structural members, or other materials on surfaces for acoustical, fireproofing, or other purposes.

Thermal system insulation means material in a building applied to pipes, fittings, boilers, breeching, tanks, ducts, or other interior structural components to prevent heat loss or gain, or water condensation, or for other purposes.

The sampling methodologies employed to address the ACM categories described above are as follows:

Surfacing material – An accredited inspector shall collect, in a statistically random manner that is representative of the homogeneous are, bulk samples from each homogeneous area of friable surfacing material that is not assumed to be ACM, and shall collect the samples as follows:

(1) At least three bulk samples shall be collected from each homogeneous area that is 1,000 SF or less.

(2) At least five bulk samples shall be collected from each homogeneous area that is greater than 1,000 SF but less than or equal to 5,000 SF.

(3) At least seven bulk samples shall be collected from each homogeneous area that is greater than 5,000 SF.

Thermal system insulation - An accredited inspector shall collect the samples as follows:

(1) At least three bulk samples, in a random distributed manner from each homogeneous area

GER

Hazardous Materials Inspection Report Drive-through Bank Building & Roof Inspection

120 N. Saratoga Street Suffolk, VA

GER 130-8471

Woolpert # of thermal system insulation that is not assumed to be ACM.

(2) Collect at least one bulk sample from each homogeneous are of patched thermal system insulation that is not assumed to be ACM if the patched section is less than 6 linear or square feet.

(3) In a manner sufficient to determine whether the material is ACM or not ACM, collect bulk samples from each insulated mechanical system that is not assumed to be ACM where cement or plaster is used on fittings such as tees, elbows, or valves.

(4) Bulk samples are not required to be collected from any homogeneous area where the accredited inspector has determined that the thermal system insulation is fiberglass, foam glass, rubber, or other non-ACBM.

Miscellaneous material - An accredited inspector shall collect the samples as follows:

(1) In a manner sufficient to determine whether material is ACM or not ACM from each homogeneous area of friable miscellaneous material that is not assumed to be ACM.

Non friable suspected ACBM - An accredited inspector shall collect the samples as follows:

If any homogeneous area of non friable suspected ACBM is not assumed to be ACM, then an accredited inspector shall collect, in a manner sufficient to determine whether the material is ACM or not ACM, bulk samples from the homogeneous are of non friable suspected ACBM that is not assumed to be ACM.

LEAD BASED PAINT (LBP)

Testing of painted surfaces for lead, cadmium and chromium was conducted by collecting bulk paint chip samples from various painted surfaces. It is important to note that this inspection was not intended to meet the requirements of HUD sampling protocols for lead paint and was not a comprehensive, surface-by-surface evaluation, but rather a screening inspection of major painted components, which may contain LBP.

ANALYTICAL METHODS

SUSPECT ASBESTOS-CONTAINING MATERIALS

(ACM)

Suspect bulk ACM samples were analyzed using polarized light microscopy (PLM) and dispersion staining techniques. The analytical method was conducted in accordance with Method EPA-600/M4-82-020 and/or EPA 600/R-93/116.

Analysis was performed by EMSL Analytical, Inc., Cinnaminson, NJ NVLAP Lab Code 101048-0, AIHA-LAP, LLC-IHLAP Lab 100194, NYS ELAP

10872, NJ DEP 03036.

LEAD BASED PAINT (LBP)

Paint chip samples were analyzed for lead using inductively coupled plasma (ICP) emission spectroscopy (SW-846, 6010C). Analysis was performed by EMSL Analytical, Inc. Cinnaminson, NJ NELAP Certifications: 10896, PA 68-00367, AIHA-LAP, LLC ELLAP 100194, A2LA 2845.01.

PREVIOUS HAZARDOUS MATERIAL

REPORTS

We were not provided with any previous hazardous material reports associated with the project.

BUILDING DESCRIPTION

The building is a 1-story wood framed structure constructed of structural steel components, CMU blocks, concrete and brick. The building includes two drive through areas, and a bathroom. The exterior of the building is brick veneer. The building is heated and cooled with a single HVAC heat pump system. The date of construction is unknown. The building contains approximately 200 square feet of interior space and approximately 450 square feet of covered drive-through space.

ASBESTOS INSPECTION AND BULK

SAMPLING RESULTS

The building and roof was inspected on August 4, 2026. A visual inspection was performed to identify homogeneous areas (HAs) of suspect ACM.

Drive-through Bank Building GER 130-8471 Page 2 120 N. Saratoga Street, Suffolk, VA

GER

The following interior and exterior finishes and building materials were observed.

1. Gypsum wallboard and joint compound partition walls.

2. Ceilings were drop-in suspended acoustical ceiling tile (SACT).

3. HVAC flex ducts were observed above ceiling.

No HVAC mastic was observed on HVAC ducts.

4. The teller window did not appear to utilize frame sealant or glazing putty.

5. The exterior door incorporated frame sealant.

6. The floors were covered with vinyl tiles and carpet.

7. The roof was an asphalt built-up roof.

8. The exterior covered area ceiling and soffit areas utilized gypsum suspended ceiling tile.

The following suspect material HAs were identified:

1. Grey 4-inch vinyl covebase with tan mastic.

2. Brown 4-inch vinyl covebase with tan mastic.

3. Grey carpet with yellow mastic.

4. Gypsum wallboard joint compound

5. Gypsum wallboard.

6. 12-inch white vinyl floor tile and tan mastic.

7. 2’x2’ SACT crater pattern.

8. Gypsum ceiling tile, vinyl backed.

9. EFIS exterior finish.

10. Built-up asphalt roofing.

11. White sink undercoating mastic.

12. Brown door frame sealant.

Twenty-four (24) bulk samples of suspect ACM were collected from the HAs.

The attached Table 1 in Section 2 lists the sample materials, sample locations, and laboratory results.

Drawings showing the approximate sample locations are attached in Section 3.

The following homogeneous materials sampled during the inspection were determined or assumed to contain asbestos:

1. Fire rated doors are assumed to contain

ACM.

ASBESTOS DISCUSSION

The EPA defines ACM as any material which contains greater than 1% asbestos by weight.

Laboratory analysis of bulk samples collected during the field investigation identified ACM in the building. The ACM is categorized as follows:

Assumed Friable ACM Fire Doors - Destructive techniques were not used to determine whether the existing fire rated doors contained ACM. The inspection techniques would have voided the doors fire rating. The fire rated doors are assumed to contain asbestos until proven otherwise.

Estimated Quantity: 2 Each.

If during the project unexpected materials are identified or uncovered they must be assumed to be ACM until proven otherwise. Exercise extreme caution when opening concealed areas to prevent any inadvertent ACM fiber releases.

Any disturbance of ACM must be performed by a Virginia Licensed Asbestos Abatement Contractor.

Friable ACM or material that may be rendered friable must be removed prior to demolition.

Removal of Category I & II non-friable ACM is not required, prior to demolition, if the material is in good condition and is not friable. However, wet methods must be used during the demolition process and personal and area monitoring should be performed. Additionally, all demolition debris must be considered asbestos containing and be taken to a landfill that accepts Category I and II non-friable ACM. Therefore recycling will not be permitted, unless the ACM is abated prior to demolition.

If asbestos abatement work is necessary due to unforeseen conditions, it must be performed in accordance with local, state and Federal regulations including but not limited to:

29CFR1926.1101 - Asbestos 40CFR61 - National Emission Standards for Hazardous Air Pollutants.

9VAC 20-81 - Virginia Solid Waste Management Regulations.

18VAC 15-20 - Virginia Asbestos Licensing Regulations.

Drive-through Bank Building GER 130-8471 Page 3

PAINT SAMPLING

Two (2) paint chip samples were collected from painted surfaces in the building. One sample was collected from a white interior wall. Another sample was collected from the brown exterior door and frame. The attached Table 2 summarizes the samples collected and their laboratory results. The laboratory analytical results are contained in Section 2. The purpose of our sampling was to obtain representative data on the concentrations of lead, cadmium and chromium in the existing painted surfaces scheduled to be disturbed by the work. Paint samples were collected from painted surfaces that may be disturbed by the planned renovation work.

LEAD, CADMIUM, & CHROMIUM PAINT

DISCUSSION

There are two frequently used standards to define lead-based paint, the Consumer Product and Safety Commission (CPSC) and the Department of Housing and Urban Development (HUD). In 1978, the CPSC, acting under the authority of the Consumer Product Safety Act, banned the sale of paint containing more than 0.06% lead by weight to consumers. The Consumer Product Safety Improvement Act of 2008 lowered the concentration of lead in paint that is permissible from 0.06% (600 ppm) to the new limit of 0.009% (90ppm), for specific paints and products. Paint which contains more than 0.009% lead by weight is defined as lead containing paint (LCP).

The Department of Housing and Urban Development (HUD) defines Lead-based paint (LBP) as any paint, varnish, shellac, or other coating that contains lead equal to or greater than

1.0 mg/cm2 as measured by X-ray fluorescence (XRF) analyzer or laboratory analysis, or 0.5% by weight as measured by laboratory analysis.

The Occupational Safety and Health Administration (OSHA) Lead in Construction Standard (29 CFR 1926.62) does not define lead-based paint.

However, to comply with OSHA, all painted surfaces with a lead concentration at or above the laboratory’s minimum detection limit (MDL) should be considered lead containing. Compliance with this standard is required even for paints with less than 0.5% or

0.009% lead by weight. Therefore, painted surfaces exceeding the MDL should not be disturbed without taking the appropriate precautions when performing certain high risk tasks. Activities such as scraping, sanding, welding/torching and disturbance of painted surfaces could potentially release leaded dust.

OSHA has categorized the following high risks tasks into three groups:

Group 1: manual demolition manual scraping heat-gun applications power tool cleaning with dust collection system spray paint with lead-based paints

Group 2: lead burning using lead-containing mortar power tool cleaning without dust collection system rivet blasting cleanup activities where dry expendable abrasives are used movement and removal of abrasive blasting enclosures

Group 3: abrasive blasting welding, cutting and burning on steel structures

Analytical results for lead paint indicate that one of the samples collected and analyzed was found to have a lead concentration above the laboratory's minimum detection limit. The samples were not identified as LBP.

Therefore, all existing painted surfaces scheduled for renovation/demolition should be considered lead containing for the purposes of complying with 29 CFR 1926.62 in order to protect workers and the environment.

Paints containing cadmium and chromium are often found as protective coatings on structural steel or exterior coatings on metal surfaces. These paints tend to be red, yellow or orange and are typically the first layer. The bulk paint chip samples were also analyzed for cadmium and chromium.

One of the samples collected and analyzed was found to have cadmium concentrations above the laboratory's minimum detection limit. Both of the samples collected and analyzed were found to have chromium

Drive-through Bank Building GER 130-8471 Page 4 concentrations above the laboratory's minimum detection limit.

The National Institute for Occupational Safety and Health (NIOSH) identifies chromium and cadmium as a confirmed carcinogen. Construction Standards established by OSHA for cadmium and lead are:

Chromium 29 CFR 1926.1126 Cadmium 29 CFR 1926.1127 Lead 29 CFR 1926.62

The permissible exposure limits (PEL) established by OSHA are 5 ug/m3 for cadmium, 5 ug/m3 for chromium (chromates) and 50 ug/m3 for lead. If the PEL is exceeded, appropriate measures must be taken to reduce the hazard and provide training and personal protective equipment.

The PEL is an airborne measurement to address worker exposure. There is no direct correlation between lead, cadmium, and chromium concentrations in paint and worker exposure. Only when these concentrations are below the laboratory’s MDL, is worker exposure not an issue.

Therefore, all existing painted surfaces scheduled for demolition should be considered lead, cadmium, and chromium containing for the purposes of complying with 29 CFR 1926.62, 29 CFR 1926.1127, and 29 CFR 1926.1126, and in order to protect workers and the environment.

Appropriate precautions should be taken during the disturbance of all painted surfaces to ensure protection of workers and the environment.

All paint disturbance work shall be performed in accordance with all local, state and Federal regulations to protect workers and the environment, including but not limited to:

29CFR 1926.62 - Lead.

29CFR 1926.1126 - Chromium.

29CFR 1926.1127 - Cadmium.

9VAC 20-60 - Virginia Hazardous Waste Management Regulations.

9VAC 20-81 - Virginia Solid Waste Management Regulations.

18VAC 15-30 - Virginia Lead-Based Paint Activity Regulations.

WASTE CLASSIFICATION FOR PAINTED

BUILDING COMPONENTS

Building components and demolition waste streams which are painted must be properly characterized prior to disposal. The EPA RCRA regulations establish the limits for RCRA leachable metals.

Leachable metals means the concentration of metals likely to leach from the waste into the surrounding soil/groundwater system of a landfill.

The leachable concentration of chemicals in a waste stream is determined by an analytical method named TCLP. Waste stream TCLP concentrations that equal or exceed the RCRA limits shown in Table A are hazardous and must be transported to a hazardous waste treatment, storage, or disposal facility. Precautions should be implemented to prevent the storage of any hazardous waste for more the 90 days. Specific permits are necessary to store hazardous waste in excess of 90 days.

The contractor must be required to characterize the waste stream generated during the project to ensure the waste stream is nonhazardous. If the waste stream is determined to be hazardous, special management procedures will be required.

0.2Hg 5.0Ag 1.0Se 5.0Pb 5.0Cr 1.0Cd

100.0Ba 5.0As

TCLPAnalyte (Metal)

Table A - RCRA TCLP Regulatory Threshold (mg/L)

All waste management and disposal shall be performed in accordance with local, state and Federal regulations including but not limited to:

29CFR 1926.62 - Lead.

29CFR 1926.1126 - Chromium.

29CFR 1926.1127 - Cadmium.

9VAC 20-60 - Virginia Hazardous Waste Management Regulations.

9VAC 20-81 - Virginia Solid Waste Management Regulations.

Drive-through Bank Building GER 130-8471 Page 5

FLUORESCENT LIGHTS AND

POLYCHLORINATED BIPHENYLS

On January 1, 1979, the Environmental Protection Agency (EPA) banned the manufacturing of light ballasts which contain PCB’s and phased out most PCB uses. Therefore, all light ballasts manufactured prior to January 1, 1979 without “Non-PCB” markings must be considered PCB containing. The EPA’s actions subjects all substances containing over 50 ppm PCBs to regulatory control (with the exception of PCB-contaminated waste oil which is prohibited at any level).

Our field investigation of existing light fixtures indicated the fixtures inside the building were T-8 fluorescent lamps, as well as LED fixtures. 12 T-8 fluorescent lamps were observed inside and outside the building. 48 T-8 fluorescent light tubes were observed inside and outside of the building. T-8 fixtures generally contain electronic ballasts which are not PCB containing. Ballasts observed were labeled “non-PCB”.

Any non-electronic ballast not marked “No PCB’s” must be considered to contain PCB’s.

All PCB work shall be performed in accordance with all local, state and Federal regulations to protect workers and the environment, including but not limited to:

40CFR273 - Standards for Universal Waste Management.

40CFR761 - Polychlorinated Biphenyls (PCBs) Manufacturing, Processing, Distribution In Commerce, and Use Prohibitions.

9VAC 20-60 - Virginia Hazardous Waste Management Regulations.

9VAC 20-81 - Virginia Solid Waste Management Regulations.

MERCURY CONTAINING EQUIPMENT

Mercury containing equipment in buildings can sometimes be found in fluorescent light tubes, HVAC thermostats, etc. We performed an inspection for obvious mercury containing equipment in the building.

48 Fluorescent light tubes were observed in the building. All fluorescent light tubes should be considered to be mercury containing and disposed of as universal waste.

The thermostat observed in the building did not appear to contain mercury.

All mercury work shall be performed in accordance with all local, state and Federal regulations to protect workers and the environment, including but not limited to:

9VAC 20-60 - Virginia Hazardous Waste Management Regulations.

9VAC 20-81 - Virginia Solid Waste Management Regulations.

LIMITATIONS

This report has been prepared for the exclusive use of Woolpert and/or their agents. This service was performed in accordance with generally accepted environmental practices. No other warranty, expressed or implied, is made. Our conclusions and recommendations are based, in part, upon information provided to us by others and our site observations. We have not verified the completeness or accuracy of the information provided by others, unless otherwise noted. Our observations and recommendations are based upon conditions readily visible at the time of our site visit in August 2026, and upon current industry standards. During our inspection, accessible areas were visually inspected for the presence of asbestos and lead based paints. The findings at these locations area assumed to be representative throughout the impacted areas of the building.

Inaccessible areas, such as inside HVAC equipment and ducts were not visually inspected. Areas inspected for the above-referenced materials were limited to those designated by the client. The inspection did not include the entire building and was limited to the areas described in the report on the first and second floor.

Under this scope of services, GER assumes no responsibility regarding response actions (e.g. O&M Plans, Remediation, Notifications, etc.) initiated as a result of these findings. GER assumes no liability for the duties and responsibilities of the Client with respect to compliance with local, state and Federal regulations. Compliance with regulations and response actions are the sole responsibility of the Client and should be conducted in accordance with local, state and Federal regulations and should be

Drive-through Bank Building GER 130-8471 Page 6 performed by appropriately licensed personnel, as warranted.

Drive-through Bank Building GER 130-8471 Page 7

SECTION 2

Bulk Sample Results / Laboratory Analysis Sheets

Table 1 - Asbestos Sample Results

Table 2 - Paint Sample Results

Drive-through Bank Building & Roof Inspection GER 130-8471

NO. HA SAMPLE LOCATION SAMPLE MATERIAL % & TYPE OF ASBESTOS

1 1 Teller room Grey covebase & tan mastic None detected

2 1 Teller room Grey covebase & tan mastic None detected

3 2 Restroom Brown covebase & tan mastic None detected

4 2 Restroom Brown covebase & tan mastic None detected

5 3 Teller room Grey carpet & tan mastic None detected

6 3 Teller room Grey carpet & tan mastic None detected

7 4 Teller room Gypsum joint compound None detected

8 4 Teller room Gypsum joint compound None detected

9 5 Teller room Gypsum wallboard None detected

10 5 Teller room Gypsum wallboard None detected

11 6 Restroom 12" white vinyl floor tile & tan mastic None detected

12 6 Restroom 12" white vinyl floor tile & tan mastic None detected

13 7 Restroom 2'x2' SACT, crater pattern None detected

14 7 Teller room 2'x2' SACT, crater pattern None detected

15 8 Exterior soffit 2'x4' SACT, gypsum None detected

16 8 Exterior soffit 2'x4' SACT, gypsum None detected

17 9 Exterior soffit EFIS exterior coating None detected

18 9 Exterior soffit EFIS exterior coating None detected

19 10 Roof Built-up roofing None detected

20 10 Roof Built-up roofing None detected

21 11 Restroom White sink undercoating None detected

22 11 Restroom White sink undercoating None detected

23 12 Exterior door Brown door frame sealant None detected

24 12 Exterior door Brown door frame sealant None detected

Table 1 - Asbestos Bulk Sample Results

EMSL Analytical, Inc.

10801 Southern Loop Blvd Pineville, NC 28134

Tel/Fax: (704) 525-2205 / (704) 525-2382 http://www.EMSL.com / charlottelab@emsl.com

412605846EMSL Order:

Customer ID: GEOE25

Customer PO:

Project ID:

Attention: Phone:Wyatt Pine (757) 463-3200

Fax:GeoEnvironmental Resources (757) 463-3080

Received Date:2712 Southern Blvd. 08/07/2026 10:25 AM

Analysis Date:Suite 101 08/11/2026

Collected Date:Virginia Beach, VA 23452

Project: ATM BLDG

Test Report: Asbestos Analysis of Bulk Materials via AHERA Method 40CFR 763 Subpart E

Appendix E supplemented with EPA 600/R-93/116 using Polarized Light Microscopy

Sample Description Appearance % Fibrous % Non-Fibrous

Non-Asbestos Asbestos

% Type

1-Cove Base

412605846-0001

None DetectedCa Carbonate

Non-fibrous (Other)

15%

85%

Gray

Non-Fibrous

Homogeneous

Grey 4" Cove Base

1-Mastic

412605846-0001A

None DetectedCa Carbonate

Non-fibrous (Other)

5%

95%

Tan

Non-Fibrous

Homogeneous

Grey 4" Cove Base

2-Cove Base

412605846-0002

None DetectedCa Carbonate

Non-fibrous (Other)

15%

85%

Gray

Non-Fibrous

Homogeneous

Grey 4" Cove Base

2-Mastic

412605846-0002A

None DetectedCa Carbonate

Non-fibrous (Other)

5%

95%

Tan

Non-Fibrous

Homogeneous

Grey 4" Cove Base

3-Cove Base

412605846-0003

None DetectedCa Carbonate

Non-fibrous (Other)

15%

85%

Brown/Gray

Non-Fibrous

Homogeneous

Brown 4" Cove Base

3-Mastic

412605846-0003A

None DetectedCa Carbonate

Non-fibrous (Other)

5%

95%

Tan

Non-Fibrous

Homogeneous

Brown 4" Cove Base

4-Cove Base

412605846-0004

None DetectedCa Carbonate

Non-fibrous (Other)

15%

85%

Brown/Gray

Non-Fibrous

Homogeneous

Brown 4" Cove Base

4-Mastic

412605846-0004A

None DetectedCa Carbonate

Non-fibrous (Other)

5%

95%

Tan

Non-Fibrous

Homogeneous

Brown 4" Cove Base

5-Carpet

412605846-0005

None DetectedCa Carbonate

Non-fibrous (Other)

10%

10%

Synthetic80%Gray/Tan/White

Fibrous

Homogeneous

Carpet & Mastic

5-Mastic

412605846-0005A

None DetectedCa Carbonate

Non-fibrous (Other)

2%

98%

Tan

Non-Fibrous

Homogeneous

Carpet & Mastic

6-Carpet

412605846-0006

None DetectedCa Carbonate

Non-fibrous (Other)

10%

5%

Synthetic85%Gray/Tan/White

Fibrous

Homogeneous

Carpet & Mastic

6-Mastic

412605846-0006A

None DetectedCa Carbonate

Non-fibrous (Other)

2%

98%

Tan

Non-Fibrous

Homogeneous

Carpet & Mastic

412605846-0007

None DetectedCa Carbonate

Non-fibrous (Other)

60%

40%

White

Non-Fibrous

Homogeneous

Joint Compound

412605846-0008

None DetectedCa Carbonate

Non-fibrous (Other)

60%

40%

White

Non-Fibrous

Homogeneous

Joint Compound

412605846-0009

None DetectedNon-fibrous (Other)90%Cellulose10%Brown/Gray

Fibrous

Homogeneous

Gypsum Wallboard

412605846-0010

None DetectedNon-fibrous (Other)90%Cellulose

Glass

10%

<1%

Brown/White

Fibrous

Homogeneous

Gypsum Wallboard

Initial report from: 08/11/2026 13:43:48

Page 1 of 3ASB_PLM_0008_0002 - 2.31 Printed: 8/11/2026 1:43 PM

Tel/Fax: (704) 525-2205 / (704) 525-2382 http://www.EMSL.com / charlottelab@emsl.com

412605846EMSL Order:

Customer ID: GEOE25

Customer PO:

Project ID:

Test Report: Asbestos Analysis of Bulk Materials via AHERA Method 40CFR 763 Subpart E

Appendix E supplemented with EPA 600/R-93/116 using Polarized Light Microscopy

Sample Description Appearance % Fibrous % Non-Fibrous

Non-Asbestos Asbestos

% Type

11-Floor Tile

412605846-0011

None DetectedCa Carbonate

Non-fibrous (Other)

40%

60%

White/Beige

Non-Fibrous

Homogeneous

12" White FT & M

11-Mastic

412605846-0011A

None DetectedCa Carbonate

Non-fibrous (Other)

10%

90%

Cellulose<1%White/Yellow

Non-Fibrous

Heterogeneous

12" White FT & M

Result includes a small amount of inseparable attached leveler.

12-Floor Tile

412605846-0012

None DetectedCa Carbonate

Non-fibrous (Other)

40%

60%

White/Beige

Non-Fibrous

Homogeneous

12" White FT & M

12-Mastic

412605846-0012A

None DetectedCa Carbonate

Non-fibrous (Other)

10%

90%

Cellulose<1%Gray/Tan

Non-Fibrous

Heterogeneous

12" White FT & M

Result includes a small amount of inseparable attached leveler.

412605846-0013

None DetectedPerlite

Non-fibrous (Other)

20%

20%

Cellulose60%White/Beige

Fibrous

Homogeneous

2x2 SACT Crater

412605846-0014

None DetectedPerlite

Non-fibrous (Other)

20%

20%

Cellulose60%White/Beige

Fibrous

Homogeneous

2x2 SACT Crater

412605846-0015

None DetectedNon-fibrous (Other)90%Cellulose

Glass

10%

<1%

Brown/Gray

Fibrous

Homogeneous

2x4 SACT Gypsum

412605846-0016

None DetectedNon-fibrous (Other)90%Cellulose

Glass

10%

<1%

Brown/White

Fibrous

Homogeneous

2x4 SACT Gypsum

17-White Coat

412605846-0017

None DetectedQuartz

Non-fibrous (Other)

30%

70%

White/Green

Non-Fibrous

Homogeneous

EFIS

17-Gray Coat

412605846-0017A

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

5%

15%

70%

Glass10%Gray/Tan

Fibrous

Heterogeneous

EFIS

18-White Coat

412605846-0018

None DetectedQuartz

Non-fibrous (Other)

30%

70%

White

Non-Fibrous

Homogeneous

EFIS

18-Gray Coat

412605846-0018A

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

10%

15%

65%

Glass10%Gray/Tan

Fibrous

Heterogeneous

EFIS

412605846-0019

None DetectedQuartz

Non-fibrous (Other)

<1%

95%

Glass5%Brown/Black

Non-Fibrous

Homogeneous

Build-Up Roofing

412605846-0020

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

<1%

5%

90%

Glass5%Black

Fibrous

Homogeneous

Build-Up Roofing

412605846-0021

None DetectedCa Carbonate

Non-fibrous (Other)

15%

75%

Cellulose10%White/Beige

Non-Fibrous

Homogeneous

Sink Undercoat, White

412605846-0022

None DetectedCa Carbonate

Non-fibrous (Other)

15%

75%

Cellulose10%White/Beige

Non-Fibrous

Homogeneous

Sink Undercoat, White

412605846-0023

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

<1%

<1%

100%

Gray/Tan/White

Non-Fibrous

Homogeneous

WHITE D.F Sealant

412605846-0024

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

<1%

<1%

100%

Gray/Tan/White

Non-Fibrous

Homogeneous

WHITE D.F Sealant

Page 2 of 3ASB_PLM_0008_0002 - 2.31 Printed: 8/11/2026 1:43 PM

Tel/Fax: (704) 525-2205 / (704) 525-2382 http://www.EMSL.com / charlottelab@emsl.com

412605846EMSL Order:

Customer ID: GEOE25

Customer PO:

Project ID:

Analyst(s)

David Zalewski (17)

Ingrid Patrick (17)

Lee Plumley, Laboratory Manager or Other Approved Signatory

EMSL maintains liability limited to cost of analysis. Interpretation and use of test results are the responsibility of the client. This report relates only to the samples reported above, and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. The report reflects the samples as received.

Results are generated from the field sampling data (sampling volumes and areas, locations, etc.) provided by the client on the Chain of Custody. Samples are within quality control criteria and met method specifications unless otherwise noted. The above analyses were performed in general compliance with Appendix E to Subpart E of 40 CFR (previously EPA 600/M4-82-020 “Interim Method”) but augmented with procedures outlined in the 1993 (”final”) version of the method. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Estimation of uncertainty is available on request.

Samples analyzed by EMSL Analytical, Inc. Pineville, NC NVLAP Lab Code 200841-0, VA 3333 00312

Page 3 of 3ASB_PLM_0008_0002 - 2.31 Printed: 8/11/2026 1:43 PM

OrderID: 412605846

OrderID: 412605846

Drive-through Bank Building & Roof Inspection GER 130-8471

NO. SAMPLE LOCATION SAMPLE MATERIAL

LEAD

CHROMIUM

CADMIUM

P1 Teller room White wall <0.00020 0.00036 <0.000040

P2 Exterior door Brown door frame 0.0017 0.00057 0.00047

NOTES:

1. D - Dilution Sample required a dilution which was used to calculate final results.

2. BOLD results indicate the sample is Lead Based Paint (LBP).

3. All YELLOW HIGHLIGHTED samples exceed the laboratory reporting limit (RL).

Table 2 - Paint Sample Results

Project Name:

Customer PO:

EMSL Sales Rep:

Reported:

EMSL Analytical, Inc.

6340 Castleplace Drive, Indianapolis, IN, 46250

Telephone: 317.803.2997 Fax:317.803.3047 www.emsl.com

Attention:

Received: 08/10/2026 10:23

08/13/2026 17:41

Jason McDonald

EMSL Order ID: 162659613

LIMS Reference ID: CE59613

EMSL Customer ID: GEOE25

ATM BLDGWyatt Pine

GeoEnvironmental Resources [GEOE25]

2712 Southern Blvd., Suite 101

Virginia Beach, VA 23452

(757) 463-3200 wpine@geronline.com

Analytical Results

Analyte Results RL Q DF Analysis Date

& AnalystWeight Prep Date

& Tech

Analytical

MethodPrep Method

Client Sample ID: P1 White Int. Wall Date Sampled: 08/04/26

Matrix: Solid LIMS Reference ID: CE59613-01

1Cadmium 08/13/26 JW 08/13/26 JW<0.000040 % wt 0.000040 % wt SW-846 6010D0.505 g SW846 3050B

1Chromium 08/13/26 JW 08/13/26 JW0.00036 % wt 0.000099 % wt SW-846 6010D0.505 g SW846 3050B

1Lead 08/13/26 JW 08/13/26 JW<0.00020 % wt 0.00020 % wt SW-846 6010D0.505 g SW846 3050B

Client Sample ID: P2 Brown Door Frame Date Sampled: 08/04/26

Matrix: Solid LIMS Reference ID: CE59613-02

1Cadmium 08/13/26 JW 08/13/26 JW0.00047 % wt 0.000040 % wt SW-846 6010D0.5027 g SW846 3050B

1Chromium 08/13/26 JW 08/13/26 JW0.00057 % wt 0.000099 % wt SW-846 6010D0.5027 g SW846 3050B

1Lead 08/13/26 JW 08/13/26 JW0.0017 % wt 0.00020 % wt SW-846 6010D0.5027 g SW846 3050B

[TOC_1]Sample Results[TOC]

EMSL Sales Rep:

Reported:

EMSL Analytical, Inc.

6340 Castleplace Drive, Indianapolis, IN, 46250

Telephone: 317.803.2997 Fax:317.803.3047 www.emsl.com

Attention:

Received: 08/10/2026 10:23

08/13/2026 17:41

Jason McDonald

EMSL Order ID: 162659613

LIMS Reference ID: CE59613

EMSL Customer ID: GEOE25

ATM BLDGWyatt Pine

GeoEnvironmental Resources [GEOE25]

2712 Southern Blvd., Suite 101

Virginia Beach, VA 23452

(757) 463-3200 wpine@geronline.com

CertificationsAnalyte

Certified Analyses included in this Report

SW-846 6010D in Solid

16-A2LA ChemistryCadmium

16-A2LA ChemistryChromium

16-A2LA ChemistryLead

[TOC_1]Certified

Analyses[TOC]

List of Certifications

Code Description Number Expires

16-MO 10180Missouri Drinking Water 03/31/2029

16-NYDOH 12130New York Potable Water, Metals Solid and Hazardous Waste - Asbestos 04/01/2027

16-AIHA ELLAP 157245American Industrial Hygiene Association (AIHA LAP, LLC) - ELLAP 08/01/2027

16-AIHA IHLAP 157245American Industrial Hygiene Association (AIHA LAP, LLC) - IHLAP 08/01/2027

16-CA ELAP 2575California Metals in DW, Chemistry and Bulk Asbestos in Hazardous Waste 06/30/2027

16-A2LA Food 2845.11A2LA Food Microbiology 01/31/2028

16-A2LA Chemistry 2845.25A2LA Environmental and Chemistry 01/31/2028

16-IN Metals/Asbestos C-49-09Indiana Lead and Metals and Asbestos in Drinking Water 12/31/2026

16-OHDOH E10040Ohio - Lead in Paint Chips, Wipes, Soil and Air 05/03/2027

16-FLDOH E871170Florida Asbestos and Metals in Drinking Water, PCBs 06/30/2027

16-NJDEP IN002New Jersey Metals, Organics and Inorganics in DW PCBs 06/30/2027

16-IN Colilert/HPC M-49-06Indiana Colilert and HPC 12/31/2026

Please see the specific Field of Testing (FOT) on www.emsl.com <http://www.emsl.com> for a complete listing of parameters for which EMSL is certified.

[TOC_1]Certifications[TOC]

Notes and Definitions

Item Definition

(Dig) For metals analysis, sample was digested.

[2C] Reported from the second channel in dual column analysis.

DA Direct Analysis

DF Dilution Factor

MDL Method Detection Limit.

ND Analyte was NOT DETECTED at or above the reporting limit, or the mdl if provided.

NR Spike/Surrogate showed no recovery.

Q Qualifier

RCS Respirable Crystalline Silica

RL Reporting Limit

Wet Sample is not dry weight corrected.

Measurement of uncertainty and any applicable definitions of method modifications are available upon request. Per EPA NLLAP policy, sample results are not blank corrected.

[TOC_1]Qualifiers, Definitions and Disclaimer[TOC]

EMSL Sales Rep:

Reported:

EMSL Analytical, Inc.

6340 Castleplace Drive, Indianapolis, IN, 46250

Telephone: 317.803.2997 Fax:317.803.3047 www.emsl.com

Attention:

Received: 08/10/2026 10:23

08/13/2026 17:41

Jason McDonald

EMSL Order ID: 162659613

LIMS Reference ID: CE59613

EMSL Customer ID: GEOE25

ATM BLDGWyatt Pine

GeoEnvironmental Resources [GEOE25]

2712 Southern Blvd., Suite 101

Virginia Beach, VA 23452

(757) 463-3200 wpine@geronline.com

Aleks Kuchenbrod Laboratory Manager or other approved signatory

EMSL maintains liability limited to cost of analysis. Interpretation and use of test results are the responsibility of the client. This report relates only to the samples reported above and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. The report reflects the samples as received. Results are generated from the field sampling data (sampling volumes and areas, locations, etc.) provided by the client on the Chain of Custody.

QC sample results are within quality control criteria and met method specifications unless otherwise noted. All results for soil samples are reported on a dry weight basis, unless otherwise noted.

SECTION 3

Sample Location Plans

1,2

3,4

5,6

8 9

19*

20*

21 22 P1

P223

DRIVE-THROUGH LANE 1

DRIVE-THROUGH LANE 2

RESTROOM TELLER ROOM

POSITIVE SAMPLE LOCATION FOR ASBESTOS

NEGATIVE SAMPLE LOCATION FOR ASBESTOS

NOTE: THE LOCATION FROM WHICH THE SAMPLES

WERE OBTAINED IS APPROXIMATE AND SHOULD NOT

BE INTERPRETED AS THE ONLY LOCATION WHERE

THE MATERIAL EXISTS. SAMPLES DENOTED WITH " * "

WERE COLLECTED FROM ROOF LEVELS.

KEY TO SYMBOLS

PAINT SAMPLE LOCATIONL1

Environmental • Groundwater • Hazardous Materials • Geotechnical • Industrial • Consulting Engineers 2712 Southern Boulevard, Suite 101, Virginia Beach, VA. 23452 (757) 463-3200 FAX (757) 463-3800 esources, Inc.EGeo nvironmental R of 1

120 N. SARATOGA ST. SUFFOLK, VA 23434

DRIVE-THROUGH BANK BUILDING & ROOF INSPECTION

HAZMAT SAMPLE LOCATION PLAN

1130-8471

NOT TO SCALE

A

08/26/2026

08/26/2026

H. N. ADCOCK

W. S. PINE

SECTION 4

Photographs

Project: Drive-through Bank Building & Roof Inspection

Suffolk, Virginia 23434

Number: 130-8471

Photographs

Photo 1: Typical exterior view of the building at 120 N Saratoga street in Suffolk, VA.

Photo 2: Typical interior view of the building. None of the materials sampled were determined to contain asbestos.

Photo Sheet 1

Suffolk, Virginia 23434

Number: 130-8471

Photographs

Photo 3: View of covebase and vinyl floor tile found in the restroom. No materials sampled were determined to contain asbestos.

Photo 4: View of suspended ceiling tile and T-8 fluorescent light tubes.

Ballasts were labeled "non-PCB".

Photo Sheet 2

Suffolk, Virginia 23434

Number: 130-8471

Photographs

Photo 5:…