Baltimore City Community College Nursing Building Hazardous Materials Survey.pdf

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CC-623-250-001 BCCC Nursing Building Renovation and Addition
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BPM058274
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Baltimore City, Maryland

About this file

This is a Hazardous Materials Survey report prepared by Geo-Technology Associates, Inc. for the Baltimore City Community College (BCCC) Nursing Building located at 2901 Liberty Heights Avenue in Baltimore, Maryland. The survey was conducted on July 20-21, 2021, and commissioned by Noelker and Hull Associates, Inc. to identify asbestos-containing materials (ACMs), lead-based paint (LBP), polychlorinated biphenyls (PCBs), and other regulated hazardous materials in the approximately 36,582 square foot, three-story academic building constructed in 1975. The survey identified significant quantities of ACMs including approximately 3,875 square feet of white 12x12 floor tiles with black streaks, approximately 745 square feet of black floor tile mastic, up to 1,400 square feet of red floor tile beneath existing white tiles, white seam mastic on silver duct insulation throughout the building, black interior window frame and pane caulking on approximately 90 windows, and resilient ceiling plaster systems in the Gaare Auditorium and stairwells totaling approximately 2,524 square feet. The XRF survey detected no lead-based paint in the building. The survey was limited to accessible areas and did not include concealed building materials, areas considered structurally unsound, or several locked rooms.

The report identifies additional regulated materials present in the building including approximately 1,800 fluorescent light tubes containing mercury, 1,200 non-PCB fluorescent light ballasts, one suspect PCB-containing electrical transformer located adjacent to the building, five refrigerant-containing units, compressed gas cylinders, fire extinguishers, liquid chemical storage containers ranging from less than one gallon to five gallons containing paints, solvents, adhesives, and medical chemicals, and a hydraulic elevator system with observed hydraulic fluid leakage. The survey recommends that friable ACM materials such as the remnant window caulking in Room 102 and ceiling plaster systems be removed by a Maryland-licensed asbestos abatement contractor prior to any disturbance during planned renovations. Non-friable floor tiles and associated mastics generally do not require abatement unless subject to sanding, grinding, cutting, or abrading during renovation activities. All asbestos removal, handling, and disposal must comply with applicable federal and state regulations enforced by the Maryland Department of the Environment.

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HAZARDOUS MATERIALS SURVEY

Baltimore City Community College Nursing Building

Baltimore, Maryland 21215

August 17, 2021

Prepared for:

Noelker and Hull Associates, Inc.

6 North East Street, Suite 300 Gaithersburg, Maryland 20878

Attn: Mr. Robert Asbury

Prepared by:

GEO-TECHNOLOGY ASSOCIATES, INC.

Geotechnical and Environmental Consultants 14280 Park Center Drive, Suite A Laurel, Maryland 20707

(410) 792-9446 or (301) 470-4470 www.gtaeng.com

GTA Project No: 31211147

GEOTECHNICAL AND

ENVIRONMENTAL CONSULTANTS

A Practicing GBA Member Firm

14280 Park Center Drive, Suite A, Laurel, MD 20707 (410) 792-9446 (301) 470-4470

Abingdon, MD Baltimore, MD Laurel, MD Frederick, MD Waldorf, MD Sterling, VA Malvern, OH Somerset, NJ NYC Metro New Castle, DE Georgetown, DE York, PA Quakertown, PA Charlotte, NC Raleigh, NC

Visit us on the web at www.gtaeng.com

August 17, 2021

Noelker and Hull Associates, Inc.

9801 Washingtonian Boulevard, Suite 310 Gaithersburg, Maryland 20878

Attn: Mr. Robert Asbury

Re: Hazardous Materials Survey Baltimore City Community College Nursing Building Baltimore, Maryland 21215

Dear Mr. Asbury:

In accordance with our agreement dated March 9, 2021, Geo-Technology Associates, Inc.

(GTA) has performed a Hazardous Materials Survey of the above-referenced site (“Site”). The results of this Hazardous Materials Survey are summarized herein.

We appreciate the opportunity to be of assistance on this project. Should you have any questions regarding this information, or should you require additional information, please contact the undersigned at your convenience.

Sincerely, GEO-TECHNOLOGY ASSOCIATES, INC.

Patrick M. Deery Environmental Scientist

Samuel J. Stevenson Vice President

PMD/KBD/SJS

31211147 S:\Project Files\2021\31211147 BCCC Nursing Building\Doc\ENV 31211147 Hazardous Materials Survey.docx

TABLE OF CONTENTS

1.0 INTRODUCTION

1.1 Purpose

1.2 Limitations

2.0 BUILDING INFORMATION

2.1 Site Location

2.2 Building Construction

2.3 Plans and Prior Reports

3.0 ASBESTOS SURVEY

3.1 History of Asbestos in Buildings

3.2 Regulatory Overview

3.3 State and Federal Regulations

3.4 Definitions

3.5 Personnel

3.6 Asbestos Survey Methodology

3.7 Asbestos Survey Findings

4.0 LEAD-BASED PAINT SURVEY

4.1 History of Lead Paint

4.2 Regulatory Overview

4.3 Federal and State Regulations

4.4 Definitions

4.5 Personnel

4.6 Lead Based Paint Survey Methodology

4.7 Lead Based Paint Survey Findings

5.0 REGULATED MATERIALS SURVEY

6.0 CONCLUSIONS AND RECOMMENDATIONS

LIST OF APPENDICES

Appendix A Figures

Figure 1 – Site Location Map (1 page, color) Figure 2 – 2019 Aerial Photograph (1 page, color)

Appendix B Site Photographs (6 pages, color) Appendix C GTA Inspector Training/Licensing Documentation (5 pages) Appendix D Tables (15 pages)

Table 1 – Asbestos Survey Results (8 pages) Table 2 – Lead-Based Paint Survey results (5 pages) Table 3 – Regulated Materials Inventory (2 pages)

Appendix E Chain of Custody Documentation and Laboratory Results (37 pages)

HAZARDOUS MATERIALS SURVEY

BALTIMORE CITY COMMUNITY COLLEGE NURSING BUILDING

BALTIMORE, MARYLAND

AUGUST 17, 2021

1.0 INTRODUCTION

1.1 Purpose

At the request of Noelker and Hull Associates, Inc. (Client), GTA performed a Hazardous

Materials Survey of an approximately 36,582 square foot, three-story academic building (“subject building”), located near the northwestern extent of the Baltimore City Community College

(BCCC) Liberty Heights campus, at 2901 Liberty Heights Avenue (“Site”), in Baltimore, Maryland. GTA understands that the subject building is proposed to be renovated under the BCCC

Learning Commons project. Therefore, GTA performed the Hazardous Materials Survey to identify and assess the physical characteristics of the asbestos-containing materials (ACMs) and lead-based paint (LBP), evaluate the potential presence of polychlorinated biphenyls (PCBs), and identify other regulated hazardous materials that will be disturbed during renovation.

1.2 Limitations

GTA’s conclusions regarding this Hazardous Materials Survey have been based on visual observation, testing, and physical assessment of building materials located at specific locations and on a specific date as noted herein. GTA’s determination of the condition of the identified

ACMs was inferred from the results of visual observation and physical touching of the materials.

The condition of the ACMs may not remain consistent through the passage of time. The ACM quantities provided by GTA are to be considered approximate, only. Reliance on such estimates for abatement, removal, demolition, or similar bidding or planning purposes is at the sole risk of the user. It is the responsibility of the abatement or demolition contractors (or other parties) to independently evaluate any material quantities prior to submitting cost proposals for related activities. GTA’s Asbestos Survey is intended to reduce, but cannot eliminate, the potential for conditions that result in liability for the Client.

The following limitations should be noted with respect to this Hazardous Materials Survey:

• The Hazardous Materials Survey was non-destructive and did not include visual observation, testing, and physical assessment of concealed building materials, such as

Hazardous Materials Survey BCCC Nursing Building August 17, 2021 GTA Project No. 31211147 those potentially found behind walls and ceilings (not equipped with access panels), in fire doors, or similar areas. The full thickness of the asphalt roofing matrix on the subject building could not be assessed in a non-destructive manner; therefore, the base layers of the roof were not evaluated for suspect ACMs.

• The Hazardous Materials Survey did not include areas that GTA considers structurally unsound or otherwise occupationally unsafe. The subject building was operational at the time of the Hazardous Materials Survey. Therefore, the electrical transformers, panels, and wiring, and the interior spaces of mechanical equipment were not evaluated.

• The Hazardous Materials Survey was limited to materials accessible with a 6-foot step ladder (provided by GTA).

• Several rooms were locked and inaccessible at the time of the Hazardous Materials Survey, including: Room 302K and 302I, Rooms 304A through 304I, and Room 311.

Therefore, these rooms were omitted from the Hazardous Materials Survey.

2.0 BUILDING INFORMATION

2.1 Site Location

The Site consists of a portion of the BCCC Liberty Heights campus, located at 2901 Liberty

Heights Avenue in Baltimore, Maryland. The Site consists of the Nursing Building, located near the northwestern extent of the campus. A Site Location Map is presented as Figure 1 (Appendix

A). According to online tax information obtained from the Maryland Department of Assessments and Taxation (MDAT), the Site is included within an 18.667-acre parcel owned by the Board of

Trustees of the New Community College of Baltimore. The parcel is identified on Tax Map 15, Block 3262, Lot 1.

2.2 Building Construction

The subject building encompasses approximately 36,582 square feet, consists of three above-ground floors, with a partially sub-grade ground floor, built in 1975, utilizing slab-on-grade construction, and occupies the entirety of the Site. The building framing materials include steel structural columns, metal studs, masonry block walls, and a metal roof deck supported by metal roof trusses. The exterior finishing materials include brick walls, metal window and door frames, glass pane windows, and an asphalt roofing matrix. The interior finishing materials include drywall and joint compound, ceiling plaster, vinyl floor tiles and sheet flooring, carpet, ceiling tile, cove base, window frame caulking, window pane caulking, and various construction mastics.

Fiberglass insulation was observed on heating and cooling systems.

2.3 Plans and Prior Reports

GTA requested copies of building construction drawings and prior asbestos-related surveys or abatement reports from the Client, and Mr. Abdon Chica and Ms. Katherine Dixon, representatives of the current property owner. GTA was informed that, to the knowledge of Mr.

Chica and Ms. Dixon, no prior Hazardous Materials Surveys exist for the Nursing Building. Mr.

Chica did note that sampling of suspect ACMs is occasionally performed at the subject building, prior to renovations or maintenance activities, but he was unable to provide documentation of prior

ACM sampling events.

The client provided GTA with a copy of project overview documents for the BCCC

Learning Commons program, dated July 2020, and pertaining to the subject building. These documents indicate that the subject building consists of three above-ground floors, with a partially sub-grade ground floor, totaling approximately 36,582 square feet, and constructed in 1975. The provided project documents additionally indicate that subject building lighting is comprised of T-

10 fluorescent light units. Fluorescent lighting units are typically subject to universal waste regulations under the U.S. EPA Toxic Substances Control Act (TSCA) due to the inclusion of mercury in the light fixtures. The reviewed project documents additionally indicate that electrical power for the Nursing Building is provided by a pad-mounted electrical transformer located adjacently southwest of the Site, and installed in 1975. The installation of the electrical transformer pre-dates the 1977 PCB ban established under TSCA. Accordingly, the pad-mounted electrical transformer may contain PCBs. The reviewed project documents did not include information regarding ACMs, LBP, or other similar hazardous materials, beyond the above-discussed fluorescent lighting units and electrical transformer.

3.0 ASBESTOS SURVEY

3.1 History of Asbestos in Buildings

Asbestos is the name given to a number of naturally occurring, fibrous silicate minerals that were extensively mined (especially from the late 1890s) for manufacture of building products due to their many marketable characteristics, including strength, insolubility, fire resistance, natural insulation, non-conductivity, chemical resistance, and ability to be woven. Examples of such building products include transite siding, built-up roofing, ceiling and wall plaster, fireproofing, plumbing pipeline insulation, flooring, construction mastics, and waterproof sealants.

The United States Environmental Protection Agency (USEPA) identified asbestos as a hazardous air pollutant in 1971, and began limiting the use of asbestos in some building products in 1972 as epidemiological studies increasingly identified respiratory and digestive diseases related to airborne asbestos fiber exposure, including asbestosis, mesothelioma, pleural plaques, and lung cancer. Today, some asbestos-containing building products (e.g., floor tile, pipeline wrap, transite shingles, and built-up roofing) have not been banned by the USEPA (or their bans have been repealed) and can still be manufactured and used in the United States.

3.2 Regulatory Overview

The regulation of asbestos is multi-faceted. The USEPA regulates asbestos primarily in the context of airborne releases. Accordingly, the USEPA generally considers asbestos products in buildings as best managed in-place, and only requires removal of asbestos products from buildings that are planned for renovation or demolition due to the potential for significant airborne asbestos fiber release. An asbestos survey is therefore needed prior to building renovation or demolition to determine if asbestos products are present and need to be removed. The

Occupational Safety and Health Administration (OSHA) approaches asbestos regulation from the perspective of worker exposure, resulting in a different set of guidelines for management of asbestos. Other asbestos regulatory considerations include asbestos disposal (mainly subject to disposal facility permitting) and individual state regulations, which can impose additional requirements beyond the federal statutes.

3.3 State and Federal Regulations

National Emission Standard For Hazardous Air Pollutants (NESHAP, 40 CFR Part 61) – Establishes the USEPA regulatory notification requirements and emission control practices when renovating or demolishing any institutional, commercial, public, industrial, or residential building (excluding residential buildings with four or fewer individual dwelling units).

Asbestos Hazardous Emergency Response Act (AHERA, 40 CFR Part 763) – Establishes the general requirements for the identification and characterization of ACM when conducting an asbestos survey. Applies primarily to schools, but provides a standardized survey procedure that is readily applicable to non-school projects.

Occupational Safety and Health Administration (OSHA) Asbestos in Construction Regulations (29 CFR 1926.1101) – Establishes the permissible occupational exposure limits and emission control practices required of those workers disturbing ACM during renovation and demolition activities.

Maryland Department of the Environment (MDE) Asbestos Licensing and Enforcement Program – Enforces the regulatory notification requirements and emission control practices established in NESHAP for renovation and demolition projects in Maryland. In addition, MDE enforces the licensing and training requirements for those business entities and individuals who perform asbestos projects in Maryland, including inspections and asbestos abatement. The notification, emission control, and licensing and training guidelines are amended in Code of Maryland Regulation (COMAR) 26.11.21.

MDE Solid Waste Program – Enforces the disposal requirements for asbestos-containing waste materials as amended in COMAR 26.04.07.13.

3.4 Definitions

Asbestos – the asbestiform varieties of chrysotile, crocidolite, amosite, anthophyllite, tremolite, and actinolite.

Asbestos-Containing Material (ACM) – any material or product that contains more than 1% asbestos.

Homogenous Area – an area of surfacing material, thermal system insulation, or miscellaneous material that is uniform in color and texture, and is known to have similar construction history.

Friable ACM (defined by NESHAP) – an ACM that, when dry, can be crumbled, pulverized, or reduced to powder by hand pressure.

Category I Non-Friable ACM (defined by NESHAP) – non-friable packings, gaskets, resilient floor coverings, and asphalt roofing ACMs.

Category II Non-Friable ACM (defined by NESHAP) – non-friable ACMs that are not Category I non-friable ACM.

Regulated ACM (RACM; defined by NESHAP) – consists of the following categories:

• Friable ACM.

• Category I non-friable ACM that has become friable.

• Category I non-friable ACM that will be or has been subjected to sanding, grinding, cutting, or abrading.

• 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 in the course of the renovation or demolition operations.

Abatement – the act of elimination or reduction of ACM, including removal, repair, enclosure, and encapsulation.

Positive-Stop – a laboratory method in which an individual building material sample that is identified by the laboratory analysis as ACM is assumed representative of its homogenous area, and the remaining building material samples collected from the homogenous area are not analyzed.

3.5 Personnel

The Asbestos Survey was conducted on July 20 and 21, 2021 and was subject to the limitations described in Section 1.2 of this report. Photographs taken during the Asbestos Survey are included in Appendix B. The Asbestos Survey was performed by EPA AHERA Inspector

Patrick Deery, (Accreditation #19025721, expires July 9, 2022) and EPA AHERA Inspector

Colleen McMullen (Accreditation #2000007291, expires February 28, 2021). A copy of the licensing documentation is included in Appendix C.

Due to the ongoing COVID-19 pandemic, and by executive order of the Governor of the

State of Maryland, all licenses, permits, registrations, and other authorizations issued by the State of Maryland, any agency of the State of Maryland, or any political subdivision of the State of

Maryland, including professional licenses that would otherwise expire during the state of emergency, are extended to the 30th day following the termination of the state of emergency.

3.6 Asbestos Survey Methodology

GTA personnel performed a visual survey of the subject building to identify homogenous areas of suspect ACM in accessible areas. After identifying the suspect ACMs and homogeneous areas, GTA personnel physically touched each suspect ACM to evaluate friability. GTA personnel then collected bulk samples of the suspect ACMs in general accordance with AHERA guidelines.

The bulk samples were placed in polyethylene bags, assigned unique sample numbers, and then shipped (following Chain of Custody protocol) to the Scientific Analytical Institute (SAI) in

Greensboro, North Carolina, for analysis. SAI, an American Industrial Hygiene Association accredited laboratory, analyzed the collected samples by Polarized Light Microscopy (PLM) with dispersion staining techniques.

3.7 Asbestos Survey Findings

GTA personnel collected 149 suspect ACM samples from 49 distinct homogeneous areas, which included:

• Roofing material;

• Floor tiles and vinyl sheet flooring;

• Interior window pane caulking;

• Interior window frame caulking;

• Drywall and joint compound system;

• Interior plaster ceiling material;

• Cove base;

• Ceiling tiles; and

• Various construction mastics and sealants.

Ninety-five of the suspect ACM samples were separated into two or more individual layers by the laboratory and analyzed separately. Additionally, 15 sample layers were not analyzed due to positive stop. Therefore, the laboratory analyzed a total of 231 suspect ACM sample layers. A table summarizing the results of the Asbestos Survey, including sample numbers, homogeneous area material descriptions, material condition (for ACM only), estimated quantities (for ACM only), and analytical results, is included in Appendix D. The SAI analysis report, including the

Chain of Custody document, is included in Appendix E.

The laboratory analysis identified the following sampled building materials as ACM:

• Approximately 3,875 square feet of white 12x12 floor tiles with black streaks (147-13) present in portions of Rooms 103, 104B, 105, 201A, 201C, 202A, 202B, 205, 209 and

• Approximately 745 square feet of white 12x12 floor tiles with black streaks and associated black floor tile mastic ACM (147-14) in the northwestern portion of Room 205 (ACM mastic present throughout Room 205).

• Approximately 850 square feet of orange 12x12 floor tile ACM in the central portion of the 3rd floor hallway

• Up to 1,400 square feet of red floor tile ACM, present beneath non-ACM white 12x12 floor tiles in Rooms 100, 100A, and 100B (the extent of this floor tile ACM could not be evaluated in a non-destructive manner, due to its presence beneath the white floor tile)

• White seam mastic on silver duct insulation present on ducts throughout the subject building

• Black interior window frame caulking present on approximately 90 metal frame windows

• Black interior window pane caulking on approximately 90 metal frame windows

• Remnant dark-gray/black interior window frame caulking on approximately three windows in Room 102.

Resilient ceiling plaster systems (totaling approximately 2,524 square feet) were present in the Gaare Auditorium and in parts of the subject building stairwells and could not be sampled in a non-destructive manner. Therefore, these systems were excluded from the asbestos survey. These plaster systems are considered PACM until sampling and analysis activities determine otherwise.

4.0 LEAD-BASED PAINT SURVEY

4.1 History of Lead Paint

The regulation of LBP is multi-faceted. Federal agencies began recommending the use of lead in paint in the early 1900s because of the strength and corrosion resistance it added to paint.

In the 1920s and 1930s, children were increasingly diagnosed with appetite suppressant type illness thought to be caused by the ingestion and inhalation of lead from deteriorating LBP surfaces in the home and chewing on toys and cribs covered with LBP. By the late 1940s, studies began to be funded to understand the hazards associated with LBP, especially in the home. In 1978, the

Consumer Product Safety Commission (CPSC) banned the use of paint containing more than

0.06% lead by weight on toys and furniture, and in all residential buildings, because children and fetuses absorb lead more easily than adults due to their rapid development. Because of its corrosive resistance, LBP continues to be used elsewhere in the construction industry, including on steel structures such as bridges, fire hydrants, and ships, and on safety structures such as fire hydrants and traffic and parking lines. Adults, children, and fetuses exposed to lead can develop central nervous system, cardiovascular system, reproductive system, hematological system, and kidney illnesses.

4.2 Regulatory Overview

The USEPA and State of Maryland do not require LBP to be removed prior to renovation or demolition. LBP regulations focus primarily on managing tenant exposure for residential rental properties. LBP can typically be managed-in-place by repainting or encapsulating materials coated with chipping, peeling, or flaking paint. An owner of a dwelling unit in the State of Maryland is not subject to COMAR 26.16.01 when performing lead hazard reduction treatments in the owner-occupied dwelling unit, or when a person performs maintenance, repair, or renovation work in an owner-occupied dwelling unit. As such, demolition or renovation activities in a non-rental unit do not require abatement. LBP waste should be disposed of in accordance with local, State, and

Federal regulations.

With regard to worker safety, the OSHA Lead in Construction regulations apply to construction work where an employee may be occupationally exposed to lead. Contractors involved in renovation or demolition of LBP-containing structures should follow these and any other applicable regulations.

4.3 Federal and State Regulations

NESHAP, 40 CFR Part 61 – Establishes the USEPA regulatory notification requirements and emission control practices when renovating/demolishing any institutional, commercial, public, industrial, or residential building (excluding residential buildings with four or fewer individual dwelling units).

OSHA Lead in Construction Regulations (29 CFR 1926.62) – Establishes the permissible occupational exposure limits and emission control practices required of those workers disturbing LBP/LCP during renovation/demolition activities.

MDE Lead Poisoning Prevention Program – Enforces the regulatory notification requirements and emission control practices for LBP/LCP projects in Maryland. In addition, enforces the accreditation and training requirements for those business entities and individuals who perform LBP projects in Maryland, including inspections and abatement. The notification, emission control, and accreditation and training guidelines are amended in COMAR 26.16.01.

MDE Solid Waste Program – Enforces the disposal requirements for ACM and LBP wastes as amended in COMAR 26.04.07.13.

4.4 Definitions

Lead-Based Paint (LBP) - any paint or other surface coating containing lead or lead in its compounds in any quantity exceeding 0.7 milligrams per square centimeter (mg/cm2) or containing lead in excess of 0.5% by weight.

4.5 Personnel

GTA representatives Mr. Sama Wanigasundara and Ms. Mikel Frater, State of Maryland

LBP Inspector Technicians (License Numbers: 16257 and 17187), evaluated the building materials and surfaces with respect to potential LBP issues. The painted surfaces suspect for containing lead consisted of the following: walls, ceiling, stairway systems, rail systems, and interior and exterior door systems.

4.6 Lead Based Paint Survey Methodology

The painted surfaces were analyzed for lead using a Niton XLP-300A Spectrum Analyzer

Lead Detector (Serial no. 98229), commonly referred to as an x-ray fluorescence (XRF) device.

The calibration of the XRF device was checked using manufacturer-supplied lead standards, both prior to and upon completion of the LBP survey.

4.7 Lead Based Paint Survey Findings

The XRF survey did not identify LBPs in association with the subject building.

A table summarizing the results of the lead analyses using the XRF is included in Appendix

C. Photographs taken during the Lead Paint Survey are included in Appendix E.

5.0 REGULATED MATERIALS SURVEY

GTA personnel conducted a survey on July 21, 2021 to identify and inventory regulated materials, subject to the limitations described in Section 1.2. GTA only identified those materials that were readily observable; areas within walls or ceilings were not reviewed for regulated materials. Photographs of several items are included in Appendix B. An inventory with estimated quantities of regulated materials is provided as Table 3 in Appendix D.

The potentially regulated materials identified include those materials regulated by

Maryland Department of the Environment (MDE) Oil Control Program (OCP), in addition to the

Resource Conservation and Recovery Act (RCRA), Universal Waste Rule (UWR), Toxic

Substances Control Act (TSCA), and Clean Air Act (CAA). Considerations that were not reviewed as part of the Regulated Materials Survey include, but are not limited to, mold, regulatory compliance, industrial hygiene, health and safety, and indoor air quality.

GTA personnel observed the following potentially regulated materials throughout the Site:

• Mercury-containing fluorescent tube bulbs and compact fluorescent bulbs

• Non-PCB containing light ballasts

• Refrigerant-containing equipment

• Compressed gas cylinders and fire extinguishers

• Liquid chemical storage

• Dry chemical storage

• Battery containing equipment

GTA personnel observed fluorescent lights and light ballasts where accessible in the subject building. The observed ballasts typically had labels indicating that they were free of PCBs.

GTA personnel did not observe PCB-containing light ballasts in the subject building. A pad-mounted electrical transformer, suspected of containing PCBs, was observed adjacently southwest of the Site, and serves the subject building. A photo of the suspect PCB-containing electrical transformer is included in Appendix B. Quantity estimates for the observed non-PCB ballasts and associated mercury-containing fluorescent tube bulbs are included in Table 3.

Note that GTA was unable to observe light ballasts in the Gaare Auditorium (Room 201) and in the 3rd floor mechanical room (Room 305) using the 6-foot step ladder. Therefore, these areas were excluded from the survey.

In addition to fluorescent light bulbs and ballasts, GTA personnel observed stored liquid chemicals located in various locations throughout the subject building, including classrooms, janitorial closets, and mechanical rooms. The majority of the stored chemical containers ranged from less than one gallon to approximately five gallons in size, and included paints, solvents, detergents, adhesives, water treatment chemicals, and hydraulic oil. Medical chemicals/fluids were observed in several classrooms and storage areas, and included synthetic bodily fluids, isopropyl alcohol, and hydrogen peroxide. GTA personnel additionally observed one, partially-full 55-gallon drum of propylene glycol solution in the ground floor mechanical room.

Refrigerant-containing equipment was observed in several locations throughout the subject building, and included water fountains, vending machines, and components associated with the subject building HVAC systems (including the Nursing Building main HVAC system and supplemental rooftop and ground floor HVAC systems). A hydraulically-driven elevator is additionally present in the subject building. Hydraulic fluid for the elevator is stored in reservoir located in the ground floor elevator machine room. A hydraulic oil leak was observed in the elevator machine room. Several hydraulic oil-soaked rags and absorbent pads were additionally observed in the elevator machine room, and were apparently used to contain the hydraulic fluid leak.

6.0 CONCLUSIONS AND RECOMMENDATIONS

Based on GTA’s Asbestos Survey, the subject building contains approximately 5,470 square feet of 12x12 floor tile ACM located in classrooms, hallways, and offices throughout the building, approximately 745 square feet of black floor tile mastic ACM in Room 205, up to 1,400 square feet of red floor tile ACM, present beneath non-ACM floor tiles in Rooms 100, 100A, and

100B, white seam mastic on silver duct insulation throughout the subject building, black window frame caulking ACM on approximately 90 windows throughout the subject building, black window pane caulking ACM on approximately 90 windows throughout the subject building, remnant dark-gray window frame caulking on approximately three windows in Room 102, and white ceiling plaster PACM in the Gaare Auditorium and in parts of the subject building stairwells.

The remnant ACM window caulking in Room 102 is considered RACM under NESHAP, due to its friable/damaged condition. This material should be removed by a Maryland licensed asbestos abatement contractor prior to disturbance. The PACM ceiling plaster systems in the Gaare

Auditorium and in parts of the subject building stairwells are considered friable and are therefore classified as RACM with regard to disturbance. Sampling and analysis of the plaster systems could be performed to determine whether they are actually ACMs. Unless verified to be non-

ACM, these materials should be removed by a Maryland-licensed asbestos abatement contractor if they are planned to be disturbed during the pending renovations.

The remaining interior window frame caulking, interior window pane caulking, and duct seam sealant are considered Category II non-friable ACM. This category of ACM generally is not considered RACM under NESHAP and generally does not require abatement unless there is a high probability that renovation and waste management activities will subject the ACM to forces expected to crumble, pulverize, or reduce the material to powder during the course of the renovation or demolition operations.

The floor tiles and associated floor tile mastic are considered Category I non-friable ACMs.

This category of ACM generally is not considered RACM under NESHAP and generally does not require abatement unless the renovation and waste management activities subject the ACM to sanding, grinding, cutting, burning, abrading, or other actions rendering them friable.

If the ACMs are not removed, renovation and waste management activities should be performed in accordance with applicable federal and State regulations and guidelines (see Sections

2.2 and 2.3). Local agencies (e.g., Building and Health Departments) may also have regulatory guidance applicable to ACM.

Alternatively, the ACM can be removed prior to renovation. All asbestos abatement and removal activities should be performed by a licensed asbestos abatement contractor, and wastes should be properly transported and disposed, in accordance with applicable regulations.

No LBP was detected during the XRF survey of the subject building. Renovation and waste management activities related to paint containing lead below the LBP threshold should be performed in accordance with applicable Federal and State of Maryland regulations and guidelines

(see Section 4.3).

GTA identified regulated materials and equipment containing regulated materials at the

Site. Equipment and materials that are no longer needed should be properly handled, transported, and disposed in accordance with applicable regulations.

***** END OF REPORT *****

APPENDIX A

FIGURES

1. Map Copyright © ADC The Map People, (800) 829-6277

2. Permitted Use Number 21006238

GEO-TECHNOLOGY ASSOCIATES, INC.

14280 PARK CENTER DRIVE, SUITE A

LAUREL, MARYLAND 20707

(410) 792-9446 OR (301) 470-4470

FAX: (410) 792-7395

www.gtaeng.com

© Geo-Technology Associates, Inc.

500 1,0000

Notes

Approximate Scale

1 inch = 1,000 feet

BCCC NURSING BUILDING

SITE LOCATION MAP

Approximate Subject

Property Boundary

AutoCAD SHX Text

GEOTECHNICAL AND ENVIRONMENTAL CONSULTANTS

AutoCAD SHX Text

PROJECT: 31211147

AutoCAD SHX Text DATE: July 2021

AutoCAD SHX Text

SCALE: 1" = 1,000'

AutoCAD SHX Text

DESIGN BY: CMM

AutoCAD SHX Text

FIGURE: 1

AutoCAD SHX Text

REVIEW BY: KBD

AutoCAD SHX Text

BALTIMORE CITY, MARYLAND

AutoCAD SHX Text

NORTH

Notes

14280 PARK CENTER DRIVE, SUITE A

LAUREL, MARYLAND 20707

(410) 792-9446 OR (301) 470-4470

FAX: (410) 792-7395

www.gtaeng.com

© Geo-Technology Associates, Inc.

100 2000

Approximate Scale

1 inch = 200 feet

BCCC NURSING BUILDING

2019 AERIAL PHOTOGRAPH

Approximate Subject

Property Boundary

1. Base image obtained from Google Earth (©2021 Google).

AutoCAD SHX Text

GEOTECHNICAL AND ENVIRONMENTAL CONSULTANTS

AutoCAD SHX Text

PROJECT: 31211147

AutoCAD SHX Text DATE: July 2021

AutoCAD SHX Text

SCALE: 1" = 200'

AutoCAD SHX Text

DESIGN BY: CMM

AutoCAD SHX Text

FIGURE: 2

AutoCAD SHX Text

REVIEW BY: KBD

AutoCAD SHX Text

BALTIMORE CITY, MARYLAND

AutoCAD SHX Text

NORTH

APPENDIX B

SITE PHOTOGRAPHS

BCCC Nursing Building GTA Project No. 31211147 Date Photographed: June 23, July 20, and July 21, 2021 Photo Page 1

Photo 1: View of the Baltimore City Community College Nursing Building. Photo 2: View of interior finishing materials in a typical classroom.

Photo 3: View of interior finishing materials in the Gaare Auditorium (Room 201). Photo 4: View of typical interior finishing materials in a subject building mechanical room.

Date Photographed: June 23, July 20, and July 21, 2021 Photo Page 2

Photo 5: View of off-white 12x12 floor tiles with black streaks (147-13) on the second floor. Photo 6: View of white 12x12 floor tiles with black streaks (147-14) on the second floor.

Photo 7: View of orange 12x12 floor tiles (147-20) in the third-floor hallway. Photo 8: View of white duct seam sealant (147-44) on silver duct insulation.

Date Photographed: June 23, July 20, and July 21, 2021 Photo Page 3

Photo 9: View of windows that contain black window frame caulking (147-47) and black window pane caulking (147-48).

Photo 10: View of remnant dark gray window frame caulking (147-49) in Room 102.

Photo 11: View of typical fluorescent light units in the subject building. Photo 12: View of a typical non-PCB fluorescent light ballast associated with the building lighting system.

Date Photographed: June 23, July 20, and July 21, 2021 Photo Page 4

Photo 13: View of liquid chemical storage in a second-floor classroom. Photo 14: View of a five-pound fire extinguisher on the third floor.

Photo 15: View of the leaking elevator hydraulic system, and associated hydraulic oil-soaked absorbent pads in the elevator machine room.

Photo 16: View of the suspect PCB-containing electrical transformer and a HVAC cooling tower associated with the subject building.

APPENDIX C

GTA INSPECTOR TRAINING/

LICENSING DOCUMENTATION

Results Maryland Asbestos Accreditation Exam

Certificate Number: AIR09302020-3

First Name: Patrick Last Name:Deery

7/9/2021According to our records this test was completed on:

We administered the following asbestos certification exam: Inspector

Score: 94

Address: 14280 Park Center Drive Suit

City: Laurel State: MD Zip: 20707

Congratulations you have passed your Maryland asbestos accreditation exam. This document and your training certificate will serve as a temporary license until you receive your official license in the mail. Prior to issuing a license, MDE will verify all necessary information and submitted documents.

necessary information and submitted documents.

Your Results

Issued By_____________ 7/9/2021Date

Thank you for taking the Maryland asbestos accreditation exam. If you have any concerns or questions about the exam, including how to collect your photo ID, please direct them to the Maryland Department of the environment at (410) 537- 3200.

APPENDIX D

TABLES

TABLE 1

SUMMARY OF ASBESTOS SURVEY RESULTS

BCCC Nursing Building GTA Project No. 31211147

Description Location Condition and Friability Estimated Quantity

Gray 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Gray 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Gray 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Gray 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Gray 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Gray 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Red 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Red 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Red 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Red 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Red 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Red 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Black 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Black 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Black 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Black 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Black 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Black 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Black 4" Cove Base & Associated Mastic‐ Cove Base NAD Black 4" Cove Base & Associated Mastic‐ Mastic NAD

Black 4" Cove Base & Associated Mastic‐ Cove Base NAD Black 4" Cove Base & Associated Mastic‐ Mastic NAD

Black 4" Cove Base & Associated Mastic‐ Cove Base NAD Black 4" Cove Base & Associated Mastic‐ Mastic NAD Tan 4" Cove Base & Associated Mastic‐ Cove Base NAD Tan 4" Cove Base & Associated Mastic‐ Mastic NAD

Tan 4" Cove Base & Associated Mastic‐ Cove Base NAD Tan 4" Cove Base & Associated Mastic‐ Mastic NAD

Tan 4" Cove Base & Associated Mastic‐ Cove Base NAD Tan 4" Cove Base & Associated Mastic‐ Mastic NAD

147‐1‐3

147‐2‐1

147‐5‐1

147‐5‐2

147‐5‐3

147‐2‐2

147‐2‐3

147‐3‐1

147‐3‐2

Second and Third Floor Hallways and Stairwells, and Room 203

GTA Sample Number

Homogenous Area For ACM Only % and Type of

Asbestos

147‐1‐2

147‐1‐1

Second and Third Floor Hallways and Stairwells, and Room 203

147‐4‐1

147‐4‐2

147‐4‐3

Second and Third Floor Hallways and Stairwells

Second Floor Hallway

147‐6‐1

147‐6‐2

147‐6‐3

Second and Third Floor Hallways, Select Classrooms and Offices on the Third Floor

Room 200 Interior

147‐3‐3

GTA Inspector (s):

Patrick Deery (MD Lic. #19025721) & Colleen McMullen (MD Lic. 2000007291)

BCCC Nursing Building GTA Project No. 31211147

Description Location Condition and Friability Estimated Quantity

GTA Sample Number

Homogenous Area For ACM Only % and Type of

Asbestos

White 4" Cove Base & Associated Mastic‐ Cove Base NAD White 4" Cove Base & Associated Mastic‐ Mastic NAD

White 4" Cove Base & Associated Mastic‐ Cove Base NAD White 4" Cove Base & Associated Mastic‐ Mastic NAD

White 4" Cove Base & Associated Mastic‐ Cove Base NAD White 4" Cove Base & Associated Mastic‐ Mastic NAD Blue 4" Cove Base & Associated Mastic‐ Cove Base NAD Blue 4" Cove Base & Associated Mastic‐ Mastic NAD

Blue 4" Cove Base & Associated Mastic‐ Cove Base NAD Blue 4" Cove Base & Associated Mastic‐ Mastic NAD

Blue 4" Cove Base & Associated Mastic‐ Cove Base NAD Blue 4" Cove Base & Associated Mastic‐ Mastic NAD

White 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD White 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

White 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD White 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

White 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD White 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Tan 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Tan 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Tan 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Tan 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Tan 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Tan 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Orange‐Red 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Orange‐Red 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Orange‐Red 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Orange‐Red 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Orange‐Red 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Orange‐Red 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD Light Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Light Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Light Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Light Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

Light Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Floor Tile NAD Light Blue 12x12 Speckled Floor Tile & Associated Mastic‐ Mastic NAD

147‐9‐1

Room 200A Interior

Room 202 Interior

147‐12‐1

147‐12‐2

147‐12‐3

Room 202 Interior

Room 202 Interior

Room 202 Interior

147‐7‐1

147‐7‐2

147‐7‐3

147‐8‐1

147‐8‐2

147‐8‐3

147‐9‐2

147‐9‐3

147‐11‐3

147‐10‐1

147‐10‐2

147‐10‐3

147‐11‐1

147‐11‐2

Rooms 200 and 200A Interior

BCCC Nursing Building GTA Project No. 31211147

Description Location Condition and Friability Estimated Quantity

GTA Sample Number

Homogenous Area For ACM Only % and Type of

Asbestos

Off‐White 12x12 Floor Tile w/Black Streaks & Associated Mastic‐ Floor Tile 3% Chrysotile Off‐White 12x12 Floor Tile w/Black Streaks & Associated Mastic‐ Mastic NAD

Off‐White 12x12 Floor Tile w/Black Streaks & Associated Mastic‐ Floor Tile Positive Stop Off‐White 12x12 Floor Tile w/Black Streaks & Associated Mastic‐ Mastic NAD

Off‐White 12x12 Floor Tile w/Black Streaks & Associated Mastic‐ Floor Tile Positive Stop Off‐White 12x12 Floor Tile w/Black Streaks & Associated Mastic‐ Mastic NAD

White 12x12 Floor Tile w/Black Streaks & Associated Mastic #2‐ Floor Tile 3% Chrysotile White 12x12 Floor Tile w/Black Streaks & Associated Mastic #2‐ Mastic 4% Chrysotile

White 12x12 Floor Tile w/Black Streaks & Associated Mastic #2‐ Floor Tile Positive Stop White 12x12 Floor Tile w/Black Streaks & Associated Mastic #2‐ Mastic Positive Stop

White 12x12 Floor Tile w/Black Streaks & Associated Mastic #2‐ Floor Tile Positive Stop White 12x12 Floor Tile w/Black Streaks & Associated Mastic #2‐ Mastic Positive Stop

Red‐Brown 4" Cove Base & Associated Mastic‐ Cove Base NAD Red‐Brown 4" Cove Base & Associated Mastic‐ Mastic NAD

Red‐Brown 4" Cove Base & Associated Mastic‐ Cove Base NAD Red‐Brown 4" Cove Base & Associated Mastic‐ Mastic NAD

Red‐Brown 4" Cove Base & Associated Mastic‐ Cove Base NAD Red‐Brown 4" Cove Base & Associated Mastic‐ Mastic NAD

Dark Gray 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Dark Gray 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Dark Gray 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Dark Gray 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Dark Gray 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Dark Gray 12x12 Floor Tile & Associated Mastic‐ Mastic NAD Dark Gray 4" Cove Base & Associated Mastic‐ Cove Base NAD Dark Gray 4" Cove Base & Associated Mastic‐ Mastic NAD

Dark Gray 4" Cove Base & Associated Mastic‐ Cove Base NAD Dark Gray 4" Cove Base & Associated Mastic‐ Mastic NAD

Dark Gray 4" Cove Base & Associated Mastic‐ Cove Base NAD Dark Gray 4" Cove Base & Associated Mastic‐ Mastic NAD

White 12x12 Floor Tile w/Tan Streaks & Associated Mastic‐ Floor Tile NAD White 12x12 Floor Tile w/Tan Streaks & Associated Mastic‐ Mastic NAD

White 12x12 Floor Tile w/Tan Streaks & Associated Mastic‐ Floor Tile NAD White 12x12 Floor Tile w/Tan Streaks & Associated Mastic‐ Mastic NAD

White 12x12 Floor Tile w/Tan Streaks & Associated Mastic‐ Floor Tile NAD White 12x12 Floor Tile w/Tan Streaks & Associated Mastic‐ Mastic NAD

Portions of Rooms 300, 301, 302, and 306

Interior of Rooms 300 and 301

Portions of Rooms 300, 301, 302, and 306

147‐17‐3

147‐18‐1

147‐18‐2

147‐18‐3

147‐15‐2

147‐15‐3

Interior of Room 201

147‐16‐1

147‐16‐2

147‐16‐3

147‐17‐1

147‐17‐2

147‐14‐3

Northwestern Portion of Room 205, (Mastic throughout Room 205)

Nonfriable/ Good 745 SF[1]

147‐15‐1

147‐14‐1

147‐14‐2

Portions of Rooms 103, 104B, 105, 201A, 201C, 202A, 202B, 205, 209 and 310

Nonfriable/ Good 3,875 SF

147‐13‐1

147‐13‐2

147‐13‐3

BCCC Nursing Building GTA Project No. 31211147

Description Location Condition and Friability Estimated Quantity

GTA Sample Number

Homogenous Area For ACM Only % and Type of

Asbestos

Burnt Orange 12x12 Floor Tiles w/light Orange Streaks & Associated Mastic‐ Floor Tile

NAD

Burnt Orange 12x12 Floor Tiles w/light Orange Streaks & Associated Mastic‐ Mastic

NAD

Burnt Orange 12x12 Floor Tiles w/light Orange Streaks & Associated Mastic‐ Floor Tile

NAD

Burnt Orange 12x12 Floor Tiles w/light Orange Streaks & Associated Mastic‐ Mastic

NAD

Burnt Orange 12x12 Floor Tiles w/light Orange Streaks & Associated Mastic‐ Floor Tile

NAD

Burnt Orange 12x12 Floor Tiles w/light Orange Streaks & Associated Mastic‐ Mastic

NAD

Orange 12x12 Floor Tiles & Associated Mastic‐ Floor Tile 2% Chrysotile Orange 12x12 Floor Tiles & Associated Mastic‐ Mastic NAD

Orange 12x12 Floor Tiles & Associated Mastic‐ Floor Tile Positive Stop Orange 12x12 Floor Tiles & Associated Mastic‐ Mastic NAD

Orange 12x12 Floor Tiles & Associated Mastic‐ Floor Tile Positive Stop Orange 12x12 Floor Tiles & Associated Mastic‐ Mastic NAD Brown 4" Cove Base & Associated Mastic‐ Cove Base NAD Brown 4" Cove Base & Associated Mastic‐ Mastic NAD

Brown 4" Cove Base & Associated Mastic‐ Cove Base NAD Brown 4" Cove Base & Associated Mastic‐ Mastic NAD

Brown 4" Cove Base & Associated Mastic‐ Cove Base NAD Brown 4" Cove Base & Associated Mastic‐ Mastic NAD

Light Gray 12x12 Speckled Floor Tiles & Associated Mastic‐ Floor Tile NAD Light Gray 12x12 Speckled Floor Tiles & Associated Mastic‐ Mastic NAD

Light Gray 12x12 Speckled Floor Tiles & Associated Mastic‐ Floor Tile NAD Light Gray 12x12 Speckled Floor Tiles & Associated Mastic‐ Mastic NAD

Light Gray 12x12 Speckled Floor Tiles & Associated Mastic‐ Floor Tile NAD Light Gray 12x12 Speckled Floor Tiles & Associated Mastic‐ Mastic NAD

147‐23‐1 NAD

147‐23‐2 NAD

147‐23‐3 NAD

Nonfriable/ Good 850 SF

Throughout Interior of Subject Building

Portions of Rooms 300, 301, 302, and 307

Central Portion of Third Floor Hallway

Interior of Room 302

Interior of Room 102 and Portions of the Third Floor Hallway

147‐19‐3

147‐20‐1

147‐20‐2

147‐20‐3

White Seam Mastic on Fiberglass Insulation

147‐22‐2

147‐22‐3

147‐21‐2

147‐21‐3

147‐19‐1

147‐19‐2

147‐22‐1

147‐21‐1

BCCC Nursing Building GTA Project No. 31211147

Description Location Condition and Friability Estimated Quantity

GTA Sample Number

Homogenous Area For ACM Only % and Type of

Asbestos

Dark Orange 12x12 Floor Tiles w/White & Gray Streaks & Associated Mastic‐ Floor Tile

NAD

Dark Orange 12x12 Floor Tiles w/White & Gray Streaks & Associated Mastic‐ Mastic

NAD

Dark Orange 12x12 Floor Tiles w/White & Gray Streaks & Associated Mastic‐ Floor Tile

NAD

Dark Orange 12x12 Floor Tiles w/White & Gray Streaks & Associated Mastic‐ Mastic

NAD

Dark Orange 12x12 Floor Tiles w/White & Gray Streaks & Associated Mastic‐ Floor Tile

NAD

Dark Orange 12x12 Floor Tiles w/White & Gray Streaks & Associated Mastic‐ Mastic

NAD

Burgundy 12x12 Floor Tiles & Associated Mastic‐ Floor Tiles NAD Burgundy 12x12 Floor Tiles & Associated Mastic‐ Mastic NAD

Burgundy 12x12 Floor Tiles & Associated Mastic‐ Floor Tiles NAD Burgundy 12x12 Floor Tiles & Associated Mastic‐ Mastic NAD

Burgundy 12x12 Floor Tiles & Associated Mastic‐ Floor Tiles NAD Burgundy 12x12 Floor Tiles & Associated Mastic‐ Mastic NAD

Light Gray 12x12 Floor Tile w/White and Dark Gray Streaks & Associated Mastic‐ Floor tile

NAD

Light Gray 12x12 Floor Tile w/White and Dark Gray Streaks & Associated Mastic‐ Mastic

NAD

Light Gray 12x12 Floor Tile w/White and Dark Gray Streaks & Associated Mastic‐ Floor tile

NAD

Light Gray 12x12 Floor Tile w/White and Dark Gray Streaks & Associated Mastic‐ Mastic

NAD

Light Gray 12x12 Floor Tile w/White and Dark Gray Streaks & Associated Mastic‐ Floor tile

NAD

Light Gray 12x12 Floor Tile w/White and Dark Gray Streaks & Associated Mastic‐ Mastic

NAD

Dark Blue 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Dark Blue 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Dark Blue 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Dark Blue 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

Dark Blue 12x12 Floor Tile & Associated Mastic‐ Floor Tile NAD Dark Blue 12x12 Floor Tile & Associated Mastic‐ Mastic NAD

147‐24‐3

Interior of Room 304

Third Floor Hallway, Adjacent to Room 307

147‐24‐1

147‐24‐2

147‐27‐3

147‐25‐1

147‐25‐2

147‐25‐3

147‐26‐1

147‐26‐2

147‐26‐3

147‐27‐1

Interior of Rooms 313 and 315

In and Adjacent to the North Entrance to Room 202

147‐27‐2

BCCC Nursing Building GTA Project No. 31211147

Description Location Condition and Friability Estimated Quantity

GTA Sample Number

Homogenous Area For ACM Only % and Type of

Asbestos

147‐28‐1 NAD

147‐28‐2 NAD

147‐28‐3 NAD

Tan Vinyl Sheet Flooring w/Leaf Pattern & Associated Mastic‐ Sheet Flooring NAD Tan Vinyl Sheet Flooring w/Leaf Pattern & Associated Mastic‐ Mastic NAD

Tan Vinyl Sheet Flooring w/Leaf Pattern & Associated Mastic‐ Sheet Flooring NAD Tan Vinyl Sheet Flooring w/Leaf Pattern & Associated Mastic‐ Mastic NAD

Tan Vinyl Sheet Flooring w/Leaf Pattern & Associated Mastic‐ Sheet Flooring NAD Tan Vinyl Sheet Flooring w/Leaf Pattern & Associated Mastic‐ Mastic NAD

Tan Vinyl Sheet Flooring‐ Sheet Flooring NAD Tan Vinyl Sheet Flooring‐ Mastic NAD

Tan Vinyl Sheet Flooring‐ Sheet Flooring NAD Tan Vinyl Sheet Flooring‐ Mastic NAD

Tan Vinyl Sheet Flooring‐ Sheet Flooring NAD Tan Vinyl Sheet Flooring‐ Mastic NAD

147‐31‐1 NAD

147‐31‐2 NAD

147‐31‐3 NAD

147‐32‐1 NAD

147‐32‐2 NAD

147‐32‐3 NAD

White 12x12 Floor Tiles w/Blue Streaks & Associated Mastic‐ Floor Tile NAD White 12x12 Floor Tiles w/Blue Streaks & Associated Mastic‐ Yellow Mastic NAD White 12x12 Floor Tiles w/Blue Streaks & Associated Mastic‐ Floor Tile NAD

White 12x12 Floor Tiles w/Blue Streaks & Associated Mastic‐ Yellow Mastic NAD White 12x12 Floor Tiles w/Blue Streaks & Associated Mastic‐ Floor Tile…

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