Baltimore City Community College Nursing Building Hazardous Materials Survey.pdf
PDF 8 MB Posted
- Solicitation number
- BPM058274
- Issued by
- Baltimore City, Maryland
About this file
This Hazardous Materials Survey report, prepared by Geo-Technology Associates, Inc. for Noelker and Hull Associates, Inc., documents the identification and assessment of asbestos-containing materials (ACMs), lead-based paint (LBP), and regulated hazardous materials in the Baltimore City Community College Nursing Building located at 2901 Liberty Heights Avenue in Baltimore, Maryland. The survey was conducted on July 20-21, 2021, on the approximately 36,582 square-foot, three-story academic building constructed in 1975 to support the planned BCCC Learning Commons renovation project. The survey identified approximately 3,875 square feet of white 12x12 floor tiles with black streaks containing 3% chrysotile asbestos in multiple rooms, approximately 745 square feet of black floor tile mastic containing 4% chrysotile in Room 205, up to 1,400 square feet of red floor tile ACM beneath white tiles in Rooms 100, 100A, and 100B, white seam mastic on silver duct insulation throughout the building, black interior window frame and pane caulking on approximately 90 windows, remnant dark-gray window frame caulking on three windows in Room 102, and resilient ceiling plaster systems (totaling approximately 2,524 square feet) in the Gaare Auditorium and stairwells classified as presumed asbestos-containing material (PACM). The XRF survey did not detect lead-based paint in the building. Additional regulated materials identified include approximately 1,800 fluorescent light tubes containing mercury, 1,200 non-PCB light ballasts, one suspect PCB-containing pad-mounted electrical transformer installed in 1975, refrigerant-containing HVAC equipment, stored liquid and dry chemicals, compressed gas cylinders, fire extinguishers, and batteries.
The survey findings indicate that friable remnant window caulking in Room 102 is classified as Regulated Asbestos-Containing Material (RACM) under the National Emission Standards for Hazardous Air Pollutants (NESHAP) and requires removal by a Maryland-licensed asbestos abatement contractor prior to disturbance during renovation. The friable ceiling plaster systems in the Gaare Auditorium and stairwells are also classified as RACM. The floor tiles and associated mastics are Category I non-friable ACMs that generally do not require abatement unless subjected to sanding, grinding, cutting, or abrading during renovation and waste management activities, and the window caulking and duct sealant are Category II non-friable ACMs. All asbestos abatement and removal activities must comply with federal NESHAP regulations (40 CFR Part 61), the Asbestos Hazardous Emergency Response Act (40 CFR Part 763), OSHA regulations (29 CFR 1926.1101), and Maryland Department of the Environment regulations (COMAR 26.11.21 and 26.04.07.13). The survey's conclusions recommend that if ACMs are not removed prior to renovation, all disturbance and waste management activities must be performed in accordance with applicable federal and state regulations, and that equipment containing regulated materials should be properly handled, transported, and disposed in accordance with applicable regulations. The report notes significant limitations regarding non-destructive survey methodology, including inability to assess concealed materials behind walls and ceilings, evaluation of the full roof thickness, structurally unsound areas, and several locked and inaccessible rooms.
View the file
Other files
Show all 40
On GovTribe
Work with this file
- Download the original file
- Contacts named in this file
- Similar government files
- Ask GovTribe AI about this file
Text version
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…
This is the start of the file's text. The full file is on GovTribe.
File details come from the government source that posted it. Updated .