TEB-HAZMAT REPORT-100__SUBMISSION.pdf

ARCHITECTURAL AND ENGINEERING SERVICES CONTRACT

Hazardous Materials Survey Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

CONTRACT # 697DCK-19-D-00002

TASK ORDER # 148056472

Prepared for:

JACOBS

Submitted by:

6401 Golden Triangle Drive, #304 Greenbelt, MD 20770

March 28, 2025

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Page i

TABLE OF CONTENTS

EXECUTIVE SUMMARY ................................................................................................ ii

1.0 INTRODUCTION

2.0 ASBESTOS INSPECTION REPORT

2.1 SURVEY METHODOLOGY

2.2 ANALYTICAL PROCEDURES

2.3 INACCESSIBLE AND LIMITED-ACCESS SPACES

2.4 SURVEY LIMITATIONS

2.5 ASBESTOS INSPECTION RESULTS

2.6 ASBESTOS CONCLUSIONS AND RECOMMENDATIONS

3.0 LEAD-BASED PAINT INSPECTION REPORT

3.2 LBP INSPECTION METHODOLOGY

3.3 LBP INSPECTION RESULTS

3.4 LBP CONCLUSIONS AND RECOMMENDATIONS

4.0 POLYCHLORINATED BIPHENYL (PCB) REPORT

4.1 METHODOLOGY

4.2 PCB RESULTS AND INTERPRETATION

4.3 PCB CONCLUSIONS AND RECOMMENDATIONS

5.0 OTHER POTENTIAL HAZARDOUS & REGULATED MATERIALS

6.0 SOIL BASELINE SAMPLING

7.0 DISCLAIMER

APPENDICES:

APPENDIX 1 – ACM ANALYTICAL RESULTS

APPENDIX 2 – HOMOGENEOUS MATERIAL LIST OF SUSPECT ACM

APPENDIX 3 – ASBESTOS SAMPLE LOCATION AND EXTENT DRAWINGS

APPENDIX 4 – XRF LEAD RESULTS

APPENDIX 5 – LBP LOCATION AND EXTENT DRAWINGS

APPENDIX 6 – PCB ANALYTICAL LABORATORY REPORT

APPENDIX 7 – PCB AND LEAD SOIL SAMPLING ANALYTICAL REPORT

APPENDIX 8 – INSPECTOR CERTIFICATION(S)/LICENSE(S)

APPENDIX 9 – PANYNJ TENANT CONSTRUCTION AND ALTERATION PROCESS MANUAL

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Page ii

EXECUTIVE SUMMARY

The Federal Aviation Administration (FAA) contracted Jacobs Engineering Group, Inc.

(Jacobs) to provide Architect-Engineering Services for the demolition of the original Airport Traffic Control Tower (ATCT), its base building, and other associated outbuildings at Teterboro Airport (TEB), collectively referred to as the Facility. Jacobs retained Global Consulting, Inc. (GCI) to perform the environmental and hazardous material survey associated with the project. This report documents the survey of the Facility by certified inspectors for asbestos-containing material (ACM), lead-based paint (LBP), polychlorinated biphenyls (PCBs), and other identified hazardous materials. This report documents the two surveys of the Facility completed between the dates of July 16 and 17, 2024, and November 12 and 14, 2024, respectively.

Asbestos:

In July, GCI’s EPA-accredited Asbestos Inspectors assessed the existing building materials suspected to contain asbestos and likely to be impacted during demolition. GCI returned to the Facility in November after the FAA moved operations to the new tower to conduct destructive/invasive sampling, extrapolate confirmed ACM location and quantity, and supplemental sampling to support New Jersey’s required TEM analysis of non-friable organically bound materials (NOBs) and other materials needing further evaluation that were identified in the July inspection.

The U.S. Environmental Protection Agency (EPA), the Occupational Safety and Health Administration (OSHA), and the State of New Jersey define an asbestos-containing material as any material that contains asbestos in a concentration of 1% or greater (by weight) using Polarized Light Microscopy (PLM). TEM re-analysis of NOBs is required in New Jersey. Between the two visits, 294 bulk samples were collected from 85 suspect materials. Bulk samples were submitted to AmeriSci Richmond (VA) and the International Asbestos Testing Laboratories (iATL) in Mount Laurel, NJ. Both laboratories are accredited by the National Voluntary Laboratory Accreditation Program for their respective analysis.

Through PLM and/or TEM analyses, the following materials (all within the ATCT) were confirmed to contain asbestos:

• Firestop Cap on Telco Feeder Conduit (First Floor Elevator Machine Room)

• 12"x12" Floor Tile – Gray (6th Floor Stairwell Landing)

Note: Black Mastic associated with the Gray Floor Tile is non-detect for asbestos

• Tan Carpet Mastic (5th Floor Equipment Room)

• 12"x12" Floor Tile – Dark Gray ( 5th Floor)

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Page iii

The following building materials were not sampled (or were not fully sampled) due to sampling limitations and/or out of concern that sampling may compromise the integrity of the substrate/structure, and are presumed asbestos-containing materials (PACM):

● Piping Gaskets, Valve Packings, and Seals

● Dry-type Electrical Transformers

● Elevator Brake Pads

● Brown Mastic on Floor Tile ATCT 5th Floor Equipment Room

Details of the survey are presented in Section 2.0 – Asbestos Survey Report. Analytical results are presented in Appendix 1 – ACM Analytical Results. Appendix 2 contains the Homogeneous Material List of Suspect ACM. Asbestos Bulk Sample Collection Locations and Extent (Drawings) are presented in Appendix 3.

Abatement specifications are warranted for demolition/removal of any ACM and PACM.

All applicable federal and state regulations, as well as requirements of the Port Authority of New York and New Jersey, must be followed for the removal and disposal of these materials.

Lead-Based Paint:

GCI’s EPA-accredited Lead Inspector (see 40 Code of Federal Regulations (CFR) Part 745) assessed the Facility for the presence of Lead-Based Paint (LBP) components using a portable X-Ray Fluorescence (XRF) Analyzer. The following building components contain lead in a concentration greater than 1.0 milligrams per square centimeter (mg/cm2), thereby meeting the definition of LBP according to the EPA:

● Parapet (Gray, Tower Cab Roof)

● Railing (Gray, Tower Cab Roof)

● Ceiling Panel (Red, Tower Cab)

● I-Beam (Red, Tower Cab)

● Hatch Frame (Red, Tower Cab)

● Fixed Ladder (Red, Tower Cab)

● Wall (Gray, Tower Cab)

● Window Frame (Black, Tower Cab)

● Window Frame (Gray, Catwalk)

● Riser (Blue, Tower Cab Stairwell)

● Tread (Blue, Tower Cab Stairwell)

● Railing (Blue, Tower Cab Stairwell)

● I-Beam (Tan, Tower Cab Stairwell)

● Stringer (Blue, 6th Floor IT Room)

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Page iv

● Shelf (Beige, 4th Floor Equipment Room)

● Beam (Beige, 5th Floor Equipment Room)

● Sink (White, Elevator Machine Room)

● Motor Support (Gray, Elevator Machine Room)

While abatement specifications are not warranted for demolition involving LBP surfaces/components, OSHA Lead-in-Construction Standards must be followed when LBP surfaces/components are disturbed during any demolition. A Toxicity Characteristic Leaching Procedure (TCLP) must be conducted on the final waste stream prior to final disposal of demolition debris. Details of the survey are presented in Section 3.0 – Lead- Based Paint Survey Report. Analytical results are presented in Appendix 4 – XRF Lead Results.

Polychlorinated Biphenyls (PCBs):

GCI’s Industrial Hygienist collected six (6) samples of materials suspected to contain PCBs.

The EPA considers the material to be PCB-containing if it contains equal to or greater than 50 parts per million (ppm) of PCBs. Laboratory analysis using EPA Method 8082A by ALS Laboratory Group of Holland, Michigan confirmed that none of the sampled materials contain detectable concentrations of PCBs above the analytical detection limit. The PCB Analytical Laboratory Report is provided in Appendix 6.

Approximately 56 fluorescent light fixtures were noted during the inspection. There is a possibility that the light ballasts in the Facility contain PCBs, and their disposal is regulated by the EPA. All fluorescent light ballasts must be managed and disposed of in accordance with the Toxic Substances Control Act (TSCA) Storage and Disposal Requirements for Fluorescent Light Ballasts as a Universal Waste.

Other Potentially Hazardous Materials:

The Facility was surveyed for other potentially hazardous materials that may be impacted by the demolition. The details of materials identified as hazardous and non-hazardous regulated materials that pose environmental concerns during building demolition are provided in Section 5.0.

Soil Baseline Sampling Report

GCI collected 16 soil samples along the exterior perimeter of the ATCT and Base Building to evaluate potential PCB and lead contamination. Two soil samples were collected within 12 inches of the exterior façade (inside the dripline) along each side of each building. The samples were hand delivered to Eurofins Edison, a New Jersey

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Page v

Environmental Laboratory Certification Program (ELCP) accredited laboratory, on the day of collection, and were analyzed for PCB and lead content. No PCBs were detected by EPA Method 8082A. Lead concentrations ranged from 20.9 milligrams per kilograms (mg/kg) to 46.5 mg/kg. The New Jersey Department of Environmental Protection (NJDEP) revised the residential soil remediation standard for lead on May 6, 2024. This revision lowered the acceptable level from 400 mg/kg to 200 mg/kg, which is in line with the new standard set by the EPA.

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Page vi

ACRONYMS

ACM Asbestos-Containing Material AHERA Asbestos Hazard Emergency Response Act AST Aboveground Storage Tank ASTM American Society for Testing and Materials ATCT Airport Traffic Control Tower CFR Code of Federal Regulations EG Emergency Generator ELCP NJ Environmental Laboratory Certification Program EPA U.S Environmental Protection Agency FAA U.S. Federal Aviation Administration GCI Global Consulting, Inc.

Jacobs Jacobs Engineering Group, Inc.

HM Homogeneous Material HUD United State Department of Housing and Urban Development LBP Lead-Based Paint LCP Lead-Containing Paint MCD Mercury-Containing Device NAD No Asbestos Detected NA/PS Not Analyzed/Positive Stop NELAC National Environmental Laboratory Accreditation Program (NELAP) NESHAP National Emission Standards for Hazardous Air Pollution NIST National Institute of Standards and Technology N.J.A.C. New Jersey Administrative Code NJDEP New Jersey Department of Environmental Protection N.J.S.A. New Jersey Statutes Annotated NOB Non-friable Organically Bound material NVLAP National Voluntary Laboratory Accreditation Program OSHA Occupational Safety & Health Administration ODS Ozone-Depleting Substances PANYNJ Port Authority of New York and New Jersey PCS Performance Characteristic Sheet PCB Polychlorinated Biphenyl PLM Polarized Light Microscopy PACM Presumed Asbestos-Containing Material RACM Regulated Asbestos-Containing Material RCRA Resource Conservation and Recovery Act RTU Rooftop Unit TCLP Toxicity Characteristic Leaching Procedure TEB Teterboro Airport TEM Transmission Electron Microscopy TSCA Toxic Substances Control Act TSI Thermal System Insulation UW Universal Waste XRF X-Ray Fluorescence Analyzer

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

1.0 INTRODUCTION

The Federal Aviation Administration (FAA) contracted Jacobs Engineering Group, Inc.

(Jacobs) to provide Architect-Engineering Services for the demolition of the original Air Traffic Control Tower (ATCT), its base building, and other associated outbuildings at Teterboro Airport (TEB), collectively referred to as the Facility. The Facility is located at 225 Fred Wehran Drive in Teterboro, NJ 07608. Jacobs retained Global Consulting, Inc.

(GCI) to perform the environmental and hazardous material survey associated with the project. This report documents the survey of the Facility by certified inspectors for asbestos-containing material (ACM), lead-based paint (LBP), polychlorinated biphenyls (PCBs), and other identified hazardous materials. The survey was limited to identifying the potentially hazardous materials and conditions likely to be impacted by the proposed project. The mutual goal of the contractor and the government is to safely achieve a quality product, within the expected timeframe and budget.

The scope of work for this limited survey consisted of the following tasks:

1. Review of available records for identified and suspect ACM, LBP, PCBs, and other hazardous and regulated materials that may be impacted by the scope of work.

2. Conduct a visual survey of the project area to identify potential location(s) of hazardous materials that may be affected by the scope of work.

3. Collect bulk samples of suspect ACMs; Assess painted surfaces for LBP using an XRF Analyzer; Collect bulk samples of suspect PCB-containing materials (if found);

and Inventory other visible hazardous materials.

4. Submit the bulk samples to a certified laboratory to positively identify ACM via Polarized Light Microscopy (PLM) or Transmission Electron Microscopy (TEM).

Download the XRF Analyzer results; Submit suspect PCB samples to a certified laboratory for analysis.

5. Prepare a report summarizing data, collection techniques, analysis procedures, location and quantity of ACM, existence of LBP/LCP, PCBs, and other hazardous and regulated materials observed, and detailed recommendations for any indicated response actions.

6. Abatement specifications are included in this scope of work.

2.0 ASBESTOS INSPECTION REPORT

GCI inspected the affected portions of the Facility for the presence of suspect ACM between the dates of July 16 and 17 and November 12 and 14, 2024. The field investigation was completed by EPA Asbestos Inspectors, Judi Darnell, John Fuentes, James Dolan, and Daniel Wooddell. Copies of their EPA accreditations are provided in Appendix 8. As the Facility was occupied during the July inspection, invasive/destructive

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

sampling was not conducted at that time. Invasive/destructive sampling was performed during the second inspection performed between the dates of November 12 and 14, 2024 when the Facility was vacated.

The Environmental Protection Agency (EPA) and the New Jersey Department of Labor and Workforce Development-Division of Public Safety and Occupational Safety and Health Administration are the authorities that regulate activities related to ACM within the State of New Jersey. The asbestos regulations applicable to this project include, but are not limited to:

1. EPA 40 CFR Part 61 Subparts A & M, National Emission Standards for Hazardous Air Pollutants (General Provisions & Asbestos);

2. EPA 40 CFR Part 763, Asbestos Model Accreditation Plan; Interim Final Rule;

3. "Test Method for the Determination of Asbestos in Bulk Building Materials,"

EPA/600/R-93/116, July 1993;

4. N.J.A.C. 1:1, Uniform Administrative Procedure Rules;

5. N.J.A.C. 5:23-8, Asbestos Hazard Abatement Subcode of the Uniform Construction

Code;

6. N.J.A.C. 7:26, Solid and Hazardous Waste Regulations;

7. N.J.A.C. 8:60, Asbestos Licenses and Permits.

8. N.J.S.A. 34:5A-32 et seq., Asbestos Control and Licensing Act;

9. N.J.S.A. 52:14B-1 et seq., Administrative Procedures Act;

10. OSHA 29 CFR 1910.1001, Asbestos; and

11. OSHA 29 CFR 1926.1101, Asbestos.

12. Port Authority of New York and New Jersey (PANYNJ), Tenant Construction and

Alteration Process Manual (TCAP), February 2021

Currently, New Jersey regulates four asbestos activities; (1) application, enclosure, repair, removal, or encapsulation of asbestos-containing materials (ACM), (2) approval of asbestos training providers, (3) licensing of employers, workers, and supervisors performing asbestos-related activities, and (4) asbestos in schools. In addition, the Port Authority of New York and New Jersey has project requirements within its Tenant Construction and Alteration Process Manual (February 2021) that describes procedures for work performed by all Tenants under the Tenant Alteration Application sub-process.

Instructions are provided for each of the major phases: 1) Design, 2) Construction, and 3) Close-Out & Occupancy. The PANYNJ TCAP outlines governing Codes and Standards (Security, Health and Safety, Environmental, etc.) including notifications related to Asbestos Abatement Procedure, the Phased Construction and Occupancy Procedure, the Emergency Works Procedure, and the Code Determination Procedure. The PANYNJ TCAP manual is provided in Appendix 9 with links to the relevant forms including the Tenant Alteration Application (PA-531); the Asbestos Certification Form (PA-3677); the Asbestos Abatement Permit Application (PA-3678) and the Asbestos Abatement Waiver Letter (PA-

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

3679). The general contractor's third party independent certified industrial hygienist (NJ Licensed) will need to verify the location, quantities, and condition of all hazardous/regulated materials prior to submitting his abatement plans, the PANYNJ forms, and abatement notifications to the FAA, NJDEP and EPA.

2.1 SURVEY METHODOLOGY

The ACM survey was divided into three distinct phases: pre-survey planning, survey for ACM, and development of ACM response action recommendations, if needed.

2.1.1 PRE-INSPECTION PLANNING

Jacobs provided GCI with information regarding the history and planned use of the property. Pre-survey planning consisted of reviewing the readily available history (both construction and utilization) of the Facility, historical sampling data for the buildings, planning a pre-survey strategy, and scheduling the survey work. The physical survey of Facility and collection of building material samples was focused on confirming the presence of ACM that would be impacted by demolition. It was determined that this survey should include all accessible portions of the Facility to ensure that intended demolition can be conducted in an efficient and safe manner compliant with applicable federal, state, and local regulations.

2.1.2 FIELD INSPECTION

GCI conducted an initial survey of the occupied Facility in July 2024 to sample accessible materials for initial PLM analysis. The inspection was conducted on an area-by-area basis as determined in the planning phase. GCI inspectors identified materials considered to be suspect ACM according to AHERA protocols, unless otherwise specified. No demolition was conducted to access materials because the facility was still occupied. In November 2024, GCI returned to collect samples of materials requiring further analysis by TEM, investigate concealed areas for additional suspect materials, and determine locations and quantities of previously-confirmed ACM.

Accessible suspect materials that were homogeneous in nature (i.e., uniform in color and texture, installation date) were identified, touched to determine friability, and sampled by removing a small piece. Extreme care was taken to avoid potential fiber release during the inspection/sampling process. Before sample collection, a fine mist of water was typically applied to the sample site. Samples were collected using sharpened core samplers and/or razor knives, where necessary, and immediately placed in labeled containers and sealed. Any dust generated was wet-wiped or cleaned using a High- Efficiency Particulate Air (HEPA) filtered vacuum to minimize the potential for fiber release.

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Samples were collected in a randomly distributed manner in accordance with AHERA provisions (40 CFR 763.86). The location, condition, and quantity of each homogeneous material were recorded in the inspector’s log.

Several presumed asbestos-containing materials (PACM) were not sampled (or were not fully sampled) due to sampling limitations and/or out of concern that sampling may compromise the integrity of the substrate/structure. A detailed description of those materials is provided in Section 2.4: Survey Limitations.

2.2 ANALYTICAL PROCEDURES

GCI collected 161 suspect ACM samples from 64 homogeneous materials during the July 16 and 17, 2024 inspection. Samples were packaged and delivered under strict chain of custody procedures to AmeriSci Richmond, located in Midlothian, VA. AmeriSci is accredited under the National Institute of Standards and Technology (NIST) National Voluntary Laboratory Accreditation Program (NVLAP Lab Code 101904-0) program for bulk asbestos identification using Polarized Light Microscopy (PLM) in accordance with EPA Method 600/R-93/116.

An additional 133 suspect ACM samples were collected between the dates of November 12 and 14, 2024, including samples from 21 additional homogeneous materials. The samples collected during the November survey were packaged and delivered under strict chain of custody procedures to iATL International, located in Mount Laurel, NJ. iATL is accredited under the NIST (NVLAP Lab Code 101165-0) program for bulk asbestos identification. The samples were analyzed using PLM in accordance with EPA Method 600/R-93/116 and then upgraded to TEM in accordance with the New York State Department of Health Method 198.4, 2009, which is accepted under New Jersey regulations for non-friable organically bound (NOB) materials. Fourteen samples did not have the initial PLM analysis completed because of a laboratory misunderstanding but had the more definitive TEM analysis completed. GCI did not request the missing PLM examinations because it considers the more accurate TEM analysis validation of asbestos content.

The EPA, OSHA, and the State of New Jersey define asbestos-containing material as any material that contains asbestos in a concentration of 1% or greater (by weight) using PLM.

Transmission Electron Microscopy (TEM) analysis of NOBs is the standard of care that is implemented to remove the restriction/limitation in asbestos surveys using PLM only.

TEM uses 10,000x magnification (compared to 400x magnification for PLM) and can detect and identify even the smallest asbestos fibers. While TEM re-analysis of NOBs demonstrating negative asbestos content by PLM is not mandated by the EPA or OSHA, it is required by the State of New Jersey.

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

2.3 INACCESSIBLE AND LIMITED-ACCESS SPACES

Every reasonable attempt was made to locate ACM present in the Facility, and to identify ACM as thermal system insulation (TSI), surfacing material, or “other” miscellaneous materials in the areas surveyed. Limited access areas (i.e., beneath fixed walls, under wall-to-wall carpeting, below raised floors, or above fixed ceilings with small access hatches) were investigated as feasible, and, as a result, conclusions regarding the presence or absence of asbestos might be of limited accuracy.

2.4 SURVEY LIMITATIONS

GCI did not inspect live electrical panels, components, and transformers. Piping systems and their flexible gaskets, packings, and sealing components were not sampled. As a result, the following building materials were not sampled (or were not fully sampled) due to sampling limitations and/or out of concern that sampling may compromise the integrity of the substrate/structure, and are presumed asbestos-containing materials

(PACM):

● Piping Gaskets, Valve Packings, and Seals

● Live Electrical Components and Dry-type Electrical Transformers

● Elevator Control Panels and Brake Pads

● Any materials not fully analyzed by the laboratory, such as HM#85 Brown Mastic on underlying floor tile in ATCT 5th Floor Equipment Room.

Any other suspect materials uncovered during demolition activities not identified within this report must be assumed to be asbestos-containing and managed appropriately until bulk sampling and laboratory analysis confirms otherwise.

2.5 ASBESTOS INSPECTION RESULTS

Within the interior and exterior portions of the Facility, GCI identified 85 specific suspect homogenous building materials from which a total of 288 bulk samples were collected and submitted for laboratory analysis.

All identified asbestos-containing materials and laboratory analytical results from the analysis of the bulk sample layers that contain asbestos are summarized in Table 1.

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

TABLE 1: ASBESTOS-CONTAINING MATERIALS LIST

HM # MATERIAL SAMPLE

LOCATION QUANTITY PHOTO

12"X12" FLOOR

TILE – GRAY AND

ASSOCIATED

MASTICS

6TH FLOOR

EQUIPMENT

ROOM AND

STAIRWELL

LANDING

~450 SF

FIRESTOP CAP

ON TELCO

FEEDER

CONDUIT

ATCT 1ST

FLOOR

ELEVATOR

MACHINE

ROOM

<1 SF

74 UNDERLYING

FLOOR TILE

ATCT - 5TH

FLOOR

EQUIPMENT

ROOM

~250 SF

12"X12" FLOOR

TILE – DARK

GRAY AND

ASSOCIATED

MASTICS

ATCT 5TH

FLOOR

EQUIPMENT

ROOM AND

STAIRWELL

LANDING

~450 SF

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

TABLE 1: ASBESTOS-CONTAINING MATERIALS LIST

HM # MATERIAL SAMPLE

LOCATION QUANTITY PHOTO

CARPET MASTIC

ADHESIVE

(MUSTARD/TAN)

ASSOCIATED

WITH 12”X12”

GRAY FLOOR

TILE/CARPET

ATCT ALL

EQUIPMENT

ROOMS

~810 SF

KEY: HM= Homogeneous Material

Asbestos bulk sample laboratory analytical data and chain of custody documentation are provided as Appendix 1. All materials sampled for suspect ACM and laboratory analytical results are summarized in a table provided as Appendix 2. The sample collection area locations and extent are presented on the drawings in Appendix 3.

2.6 ASBESTOS CONCLUSIONS AND RECOMMENDATIONS

Regulated asbestos-containing material (RACM) is defined as friable or non-friable ACM that will be, or has been, subjected to sanding, grinding, cutting, or abrading or has crumbled, pulverized, or reduced to powder during demolition or demolition operations.

Both presumed and positively identified ACM must be treated as RACM. OSHA regulates employee exposure to asbestos under 29 CFR 1926.1101 and 29 CFR 1910.1001. Work associated with known, suspect, or presumed ACMs must be conducted according to these regulations in addition to the noted EPA regulations.

Materials presented in Table 1 and the PACM listed in Section 2.4 are RACM. These materials shall be removed and disposed of in accordance with all applicable state and federal regulations and Port Authority of NY & NJ requirements. Asbestos abatement specifications are warranted based upon the scope of work for the Facility demolition and the RACM that will be disturbed. The specifications describe the scope of work, RACM quantities, means and methods to properly remove and dispose of RACM, and regulatory requirements.

If additional suspect materials are identified during demolition that will be disturbed by the proposed work, and they have not been tested to determine asbestos content, those materials should be protected from impact until further investigated.

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

All quantities must be field verified by a licensed asbestos abatement contractor(s) prior to demolition.

3.0 LEAD-BASED PAINT INSPECTION REPORT

This section describes the assessment of the buildings for the presence of Lead-Based Paint (LBP) surfaces and/or components. The survey was conducted between the dates of July 16 and July 17, 2024, by GCI’s EPA-accredited Lead Inspector Technician, Mr. Daniel Wooddell (Refresher Certificate #10461). Mr. Wooddell’s training certifications are provided in Appendix 8.

3.1 LBP REGULATIONS

The Toxic Substances Control Act (TSCA) of 1976 provides EPA with authority to require reporting, record-keeping and testing requirements, and restrictions relating to chemical substances and/or mixtures. TSCA addresses the production, importation, use, and disposal of specific chemicals including polychlorinated biphenyls (PCBs), asbestos, radon and lead-based paint.

The EPA and NJ define lead-based paint (40 CFR § 745.103 and New Jersey Administrative Code § 5:28A-1.2) as paint or other surface coatings that contain lead equal to or in excess of 1.0 milligram per square centimeter or 0.5 percent by weight. OSHA identifies in the Construction Standard (Title 29 CFR Part 1926.62) that any concentration of detectable lead requires worker protections to be implemented.

3.2 LBP INSPECTION METHODOLOGY

The testing for lead content in paints and coatings was performed with the Thermo Scientific Niton XLp (model # XLp 300) X-ray fluorescence (XRF) Spectrum Analyzer (serial number 18595). The XRF contains a small sealed-source radioactive isotope and operates on the principle of x-ray fluorescence, whereby lead atoms in a surface coating are stimulated to emit characteristic x-rays, which are then detected by the instrument.

Levels of lead are reported in units of milligrams per square centimeter (mg/cm2). The XRF can measure surface or non-surface concentrations of lead with 95% accuracy at the U.S. Department of Housing and Urban Development action level of 1.0 mg/cm2. The XRF can accurately detect a concentration as low as 0.1 mg/cm2 of lead.

The XRF was checked for calibration before and after the survey. The calibration was checked against a NIST Standard Reference Material (1.04 mg/cm2 SRM #2573) supplied by the XRF manufacturer. The composition of the building substrate (e.g., wood, metal, etc.) to be tested was determined by the lead inspector, and subsequently logged into

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

the XRF analyzer. The Niton XLP XRF automatically performs a substrate correction to ensure that this factor does not result in false negative readings. The XRF classifies coated surfaces as “positive,” “negative,” or “null” for lead content based on the action level, which was set to 1.0 mg/cm2, and the performance characteristics of the XRF.

Positive: Lead is present at or above the action level of 1.0 mg/cm2 on one or more of the components tested.

Negative: Lead is not present at or above the action level of 1.0 mg/cm2 on any of the components tested.

Null: Insufficient data was collected by the XRF during the sample time to determine if the surface is positive or negative (i.e. – premature removal or instrument slippage, terminating the test).

At the end of each sampling session, a calibration re-check is performed to ensure that the instrument has maintained accuracy and precision during the measurement period.

The instrument is also calibrated each time it is turned off, or on, and typically at four (4) hour intervals during the workday for the same reasons. The use of the XRF was in general accordance with the Performance Characteristic Sheet (PCS) methodology for the specific instrument. XRF instrument calibration checks were performed according to the PCS.

The XRF data was downloaded directly to a computer to generate a report detailing the date/time, materials sampled, location, substrate and lead content. This inspection included only painted, varnished, or glazed surfaces. The XRF data download is presented in Appendix 4.

3.3 LBP INSPECTION RESULTS

Within the Facility, GCI tested many painted surfaces/components and collected 332 XRF readings, excluding calibration test readings. Surfaces/components identified to meet the State of New Jersey’s LBP threshold are summarized in Table 2.

Table 2: Description of Lead-Based Paint Surfaces/Components Description Assessment Photo

Gray Parapet

Max. detected concentration via XRF 7.1 mg/cm2

Condition Fair

Location Tower Cab Roof

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Description Assessment Photo

Gray Railing concentration via XRF 6.4 mg/cm2

Location Tower Cab Roof

Red Ceiling Panel concentration via XRF 2.4 mg/cm2

Location Tower Cab

Red I-Beam concentration via XRF 7.2 mg/cm2

Condition Intact

Red Hatch Frame concentration via XRF 3.7 mg/cm2

Red Fixed Ladder concentration via XRF 3.5 mg/cm2

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Description Assessment Photo

Gray Wall

Max. detected concentration via

XRF

4.5 mg/cm2

Black Window Frame

Max. detected concentration via

2.7 mg/cm2

Gray Window Frame

Max. detected concentration via

3.0 mg/cm2

Location Catwalk

Blue Riser

Max. detected concentration via

3.9 mg/cm2

Stairwell

Blue Tread

Max. detected concentration via

2.0 mg/cm2

Stairwell

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Description Assessment Photo

Blue Railing

Max. detected concentration via

2.9 mg/cm2

Stairwell

Tan I-Beam

Max. detected concentration via

3.6 mg/cm2

Stairwell

Blue Stringer

Max. detected concentration via

4.8 mg/cm2

Stairwell

Beige Shelf

Max. detected concentration via

3.6 mg/cm2

Location 4th Floor

Equipment Room

Beige Beam

Max. detected concentration via

4.4 mg/cm2

Location 5th Floor

Equipment Room

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Description Description Description

White Sink

Max. detected concentration via

7.7 mg/cm2

Location Elevator Machine Room

Gray Motor Support

Max. detected concentration via

2.9 mg/cm2

Location Elevator Machine Room

Several building components/surfaces were determined to be LCP. Details of these components may be found in the results provided in Appendix 4. Lead-based paint drawings may be found in Appendix 5.

Any paint found during demolition that is not identified within this report should be assumed to contain LBP, and managed accordingly, or tested to determine otherwise.

3.4 LBP CONCLUSIONS AND RECOMMENDATIONS

OSHA defines lead-containing paint as any paint that contains a detectable amount of lead. If lead paint-containing components will not to be abated prior to general demolition, then OSHA lead safe construction practices must be followed. The OSHA Lead in Construction Standard (29 CFR 1926.62) must be followed during demolition for all identified painted surfaces/components containing any detectable concentration of lead.

LBP materials on metal substrates should be segregated from the demolition waste and recycled as metal scrap in accordance with federal, state, and local regulations. The contractor must remove the materials as a whole component to the greatest extent possible. Recycled painted components do not require testing prior to recycling.

For construction and demolition debris that is not segregated for metal recycling, EPA regulation (40 CFR 261.11) requires that a generator of lead-containing waste determine if that waste is hazardous by performing testing in accordance with the American Society for Testing and Materials (ASTM) E-1908 “Standard Practice for Sample Selection of

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Debris Waste from a Building Renovation or Lead Abatement Project for Toxicity Characteristic Leaching Procedure (TCLP) Testing for Leachable Lead (Pb)” procedure.

The TCLP by Method SW-846 1311 includes a specific list of organic and inorganic compounds, as well as regulatory levels for each compound. If the waste stream passes the EPA landfill criteria as determined by the TCLP, it may be disposed of as normal construction waste in a facility licensed to accept the materials. If the TCLP determines that the waste stream is hazardous, the waste must be handled and disposed of in accordance with EPA Hazardous Waste regulations (40 CFR Parts 239 through 282). For any waste with a known high lead content, the generator may assume that the waste is hazardous and comply with the hazardous waste regulations. The disposal and/or recycling facility may require additional testing for determination of disposal.

The demolition contractor must provide third-party testing of the disposal waste stream for TCLP in accordance with the EPA and the New Jersey Department of Environmental Protection (NJDEP). The regulations set forth at N.J.A.C. 7:26G state that it is the responsibility of the waste generator to determine whether the waste generated is hazardous in accordance with the definition stated in N.J.A.C. 7:26G-5.1 et seq. All third-party TCLP testing of the waste stream(s) in accordance with the above standards and practices shall be identified in the contractor's sampling plan to be approved by the FAA prior to implementation. In addition, the specifications shall stipulate that all environmental samples are to be submitted to a NJDEP Environmental Laboratory Certification Program (ELCP) as detailed in N.J.A.C. 7:18 (as amended September 4, 2018) Regulations Governing the Certification of Laboratories and Environmental Measurements.

4.0 POLYCHLORINATED BIPHENYL (PCB) REPORT

Polychlorinated biphenyls (PCBs) are organic chlorine compounds with the formula C12H10−xClx. Polychlorinated biphenyls were once widely used in dielectric and coolant fluids in electrical apparatus, building materials, and in heat transfer fluids. The Monsanto Company marketed PCBs under the trade name Aroclors from 1930 to 1977. These were sold under trade names followed by a four-digit number. In general, the first two digits refer to the product series as designated by Monsanto (e.g., 1200 or 1100 series); the second two numbers indicate the percentage of chlorine by mass in the mixture. With the discovery of the environmental toxicity of PCBs and classification as persistent organic pollutants, their production was banned by United States federal law in 1978.

https://en.wikipedia.org/wiki/Toxicity https://en.wikipedia.org/wiki/Persistent_organic_pollutant https://en.wikipedia.org/wiki/Persistent_organic_pollutant

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

4.1 METHODOLOGY

The inspection included a visual inspection of the buildings for potential sources of PCBs and the bulk sampling of hydraulic fluid and caulking materials. Six bulk samples of suspect PCB-containing bulk materials were submitted under strict chain of custody to ALS Group USA, Corp. (ALS) of Holland, Michigan. EPA Method 8082A was used to determine the concentrations of various Aroclors using dual capillary columns with electron capture detectors.

4.2 PCB RESULTS AND INTERPRETATION

The analytical results and chain of custody are provided as Appendix 6. The concentration of PCBs in the six sampled materials were non-detect for PCBs as noted in the table below:

Table 3: Description of PCB Samples

Sample # Description Concentration Reported (mg/kg=ppm)

FF102-TEB-34A GRAY PUTTY -ATCT CATWALK Non-Detect

FF102-TEB-50A CREAM/GRAY CAULK -EXTERIOR OF GENERATOR

STORAGE BLDG Non-Detect

FF102-TEB-52A BLACK/GRAY PUTTY -GENERATOR STORAGE BLDG Non-Detect

FF102-TEB-54A BROWN EXTERIOR CAULK-SMOKING SHED Non-Detect

FF102-TEB-58A EXTERIOR EXPANSION JOINT SEALANT ALONG FLUTED

PANELS - BASE BLDG ROOF Non-Detect

FF102-TEB-63A GRAY LOUVER CAULKING -GENERATOR STORAGE BLDG Non-Detect

GCI noted the presence of approximately 56 fluorescent light fixtures with an estimated 103 light ballasts in the buildings. GCI inspected 10 light ballasts that were labeled as “No PCBs”, however a PCB-containing ballast may still be present within the facility.

4.3 PCB CONCLUSIONS AND RECOMMENDATIONS

All fluorescent light ballasts encountered during demolition must be segregated, managed and disposed in accordance with TSCA Storage and Disposal Requirements for Fluorescent Light Ballasts. The fluorescent light systems may contain PCB ballasts that are regulated under current EPA regulations and require special handling and disposal under EPA 40 CFR 761 (PCBs) and/or 40 CFR 239-282 (Resource Conservation and Recovery Act (RCRA)).

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

5.0 OTHER POTENTIAL HAZARDOUS & REGULATED MATERIALS

The buildings were surveyed for other potentially hazardous materials that may be impacted by the planned demolition. In 1996, under the Solid Waste Recycling Regulations, New Jersey adopted its Universal Waste Rule (N.J.A.C. 7:26A-7 et. Seq) that incorporated the Federal Listed Universal Waste (UW) (Batteries, Mercury-containing Devices, Pesticides, Hazardous Lamps) and added Consumer Electronics and Oil-based Finishes. The following building materials, conditions, or components were observed within the buildings that would be recognized environmental concerns, pose potential exposure concerns, or be regulated:

• A 500-gallon aboveground diesel fuel oil tank and 25-gallon day tank supply the Emergency Generator (EG) at the facility. The aboveground storage tank (AST) features a secondary containment with integral overfill protection device and anti-siphon device. The AST has an automated tank monitoring system (Veeder Root TLS-300). All piping systems are double walled systems or contained within structure. The AST and all ancillary equipment must be removed and properly disposed after the EG is removed from site. Most towns require a $100-$200 permit to remove above-ground and underground heating oil tanks in New Jersey.

A licensed and insured contractor must remove the tank in coordination with NJ Department of Environmental Protection, all utilities, and contractors working at that time. It is estimated that there is approximately 350 gallons of diesel within the fuel system to be reused or properly disposed. The disposal of the fuel must be properly documented by the contractor.

• Approximately 300 small battery back-up systems were identified in electronic alarm and surveillance components, rack systems, fire protection panels, and 40 emergency egress lighting systems. The small sealed-battery systems must be properly managed to recycle the batteries under the EPA “Universal Waste” regulations or disposed as hazardous waste. In addition, the FAA operates one large wet-cell battery rack system and equipment rack system batteries that must be removed prior to demolition. The FAA should re-use or recycle these batteries.

• Mercury-containing device (MCD) disposal is regulated by state and federal laws that affect property owners and managers, as well as public and privately owned municipal solid waste facilities, transfer stations and construction and demolition landfills. MCDs include lamps containing mercury, mercury thermostats and thermometers. Examples of lights containing mercury are fluorescent lamps including compact fluorescent lamps, ultraviolet lights, neon lights and high intensity discharge lights. The existing original lighting systems have an elevated potential to contain mercury-containing fluorescent, compact fluorescent, or high intensity light bulbs, and must be disposed of in accordance with the EPA Universal

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Waste (UW) Regulations 40 CFR 273. GCI estimates that there are approximately 400 fluorescent and high intensity lamps within the Facility.

• NJ requires all UW Handlers to:

• Label/mark UW containers / materials properly.

• Accumulate UW within one year.

• Maintain records to prove material was accumulated within one year.

• Ship off-site UW to another handler or a destination facility.

• Contain and clean-up all UW releases/spills.

• Determine resulting release/spill is a hazardous waste and manage appropriately.

There are additional management and reporting requirements for Small and Large Quantity UW Handlers as outlined in New Jersey’s Solid Waste Recycling Regulations in N.J.A.C. 7:26A-7 et. seq..

• Section 608 of the Clean Air Act prohibits the known release of refrigerants and

Ozone Depleting Substances (ODS) during the maintenance, service, repair, or disposal of air-conditioning and refrigeration equipment. The EPA requires proper refrigerant management practices by owners and operators of refrigeration and air-conditioning systems, technicians, and others. The refrigerants must be managed and disposed of in accordance with 40 CFR 82 and applicable federal, state, and local regulations. GCI identified several drinking water fountains and water coolers, air-conditioning and/or refrigeration systems that may contain an ODS in the Facility.

The following small systems had legible equipment labels:

Table 4 – Refrigerant Summary Equipment Quantity Refrigerant Type Recovery Tank 1 x 40 Lbs. R-22

GE Window AC Unit, 18,000 BTU 1 x 35.28 oz R-410A

Frigidaire/Electrolux Window AC Unit, 10,000 BTU 2 x 31.16 oz. R-410A

Trane ProSpace PTAC 12,000 BTU 4 x 35.4 oz. R-410A

Trane ProSpace PTAC 15,000 BTU 6 x 35.4 oz. R-410A

LG PTAC 10,000 BTU 1 x 31.7 oz R-410A

LG PTAC 12,000 BTU 2 x 32.1 oz R-410A

Trane Roof Top Unit (RTU)-1 1 x 18.3 lbs. R-22

Cab Refrigerator Embraco EM45HHR 1 x 5.75 oz R-134A

Water Dispenser, 1 x 1.27 oz R-134A

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Table 4 – Refrigerant Summary Equipment Quantity Refrigerant Type Maytag Refrigerator 1 x 5 oz R-134A

Mitsubishi Split System Heat Pump 12,000 BTU 1 x 41 oz R-410A

Mitsubishi Mr. Slim Inverter HP-01 12,000 BTU 1 x 44.1 oz R-410A

Guardian III wet Chemical Extinguisher System 1 x 58 oz Ansulex Low pH

GCI recommends that all refrigerant sources be evacuated and reclaimed by a licensed contractor prior to demolition.

• GCI estimates that there are approximately 30 smoke detectors within the Facility that may contain a small sealed-source of radioactive material. These devices must be segregated prior to demolition activities and repurposed within the Facility or disposed in accordance with the U.S. Nuclear Regulatory Commission (NRC) and EPA regulations.

• Approximately 50 portable Class ABC fire extinguishers and one Class K fire extinguisher for Kitchen Use were observed within the Facility. These 10 to 20-pound extinguishers should be relocated by the FAA or recycled when no longer necessary for service.

• Miscellaneous Stored Products were observed in the buildings. These materials contain chemicals regulated under EPA RCRA for disposal. The following is a representative list of the items identified:

EMERGENCY GENERATOR BUILDING

MATERIAL/LOCATION QUANTITY

Emergency Generator Coolant/Antifreeze 5 gal Used Oil 2 gal Interstate Batteries, Lead Acid 12v 2 units Day Tank, #2 Diesel Fuel Oil 25 gal

500 GAL #2 Diesel Fuel Oil Aboveground Storage Tank on pad outdoors ~350 gal

FLAMMABLE CABINET

Denatured Alcohol, 16 oz 2 bottles Interior/Exterior Paint, 32 oz 2 cans Acetone, 32 oz 1 bottle Pro Lube Aerosol Lubricant, 12.5 oz 1 can Isopropyl Alcohol, 16 oz 5 bottles Flex Seal Liquid, 32 oz 1 can Nu-Calgon A/C Easy Seal 5 ounces Loctite Spray Adhesive,13.5 ounces 1 can

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Skilcraft Pro Lube II Aerosol Lubricating Oil, 12.5 oz 11 cans 3M Fiberglass Resin 1 quart Oatey PVC Primer and Glue, 8 oz 2 cans Pro Lube II Aerosol Lubricating Oil, 12.5 oz 14 cans Super Tect Aerosol Lubricating Oil, 12 oz 1 can Lord 304 Two Part Epoxy, 2 lb cans 1 kit Great Stuff Foam, 32 oz aerosol 2 cans Detergent, general purpose, 16 oz 1 bottle So Sure Corrosion Preventive Aerosol, 14.5 oz 1 can Shell Rotella 15w-40 oil, 1 gal 1 bottle Engine Oil15w-30, 1 qt 1 bottle Sherman Williams DTM Acrylic Paint, 120 oz 2 cans Armstrong Ceilings Stains Away Aerosol, 16 oz 3 cans Aerosol Spray Paint, 16 – 18.5 oz 7 cans Flex Seal Aerosol, 16 oz 1 can Chainsaw Bar Oil, 1 gal 1 bottle Jasco Acetone, 1 qt 1 can Sherman Williams ProMar Latex Paint, 120 oz 1 can Glidden Premium Latex Paint, 124 oz 3 cans Klean Strip Acetone, 1 gal 1 can Mix Fuel Gas Can, 2 gal 1 can Chainsaw with mixed fuel/bar oil, 1 qt 1 saw

EMERGENCY GENERATOR BUILDING (FLOOR)

Battery Back-up, wall mount 1 unit Advance Light Ballasts in box 12 units Compressed Gas Cylinder 1-Yellow Fertilizer 1 gal Clorox Bleach, 1 gal 4 bottles Nu-Calgon Foam Brite Coil Cleaner, 1 gal 1 bottle 3M Scotchcast Electrical Insulating Resin 20 kits ZEP Pressure Washing Concentrate, 1 gal 1 bottle Heat Ice Melt Granules, 1 lb 1 bottle SigmasTek Sealed Lead Acid Batteries (12v18AH) 8 batteries

Halogen Lamps, atop equipment 4 bulbs Fire Extinguisher 10# ABC, wall mount 1 unit Fire Extinguisher 20# ABC, floor 1 unit Fire Extinguisher 20# Wet, floor 1 unit Isolatex Heat-Shield Adhesive, 5 gal bucket, floor 1 unit R-22 Recovery Tank, 40 Lbs, floor 1 cylinder

Miscellaneous Smoke Detectors 2 units Fluorescent Lamps, 4 ft 8 units Fluorescent Light Ballasts 4 units Egress Lights 2 units Oil-filled Hydraulic Door Closing Systems, 5 oz 2 units

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

AIRPORT TRAFFIC CONTROL TOWER

MATERIAL/LOCATION QUANTITY

Suspect Mold, 2nd Floor Equipment Room Exterior Wall ~5 sf Suspect Mold, Elevator Machine behind conduits and column ~5 sf Elevator Maintenance Supplies – Grease, 1 lb can 1 can Lubricant Rail Oil, 1 gal jugs 3 gal Lubricant, Oil, 1 qt spray bottle 1 bottle Grease, 32 oz can 1 can Dispenser Cleaning Chemicals (Concentrate) Buckeye Eco® Muscle Cleaner E14 3 gal Buckeye Eco® Neutral Disinfectant E23 S23 2 gal Buckeye Eco® Multi-Purpose Glass Cleaner E13 1 gal Buckeye Eco® Hydrogen Peroxide Cleaner E15 S15 2gal Spray bottles (32 oz) of various cleaning solutions 8 bottles Hand Pump Sprayer with E14, 5 gal 4 gal Multi-Surface Cleaner, 1 gal bottles 12 gal Floor Cleaner, 5 gal bucket 1 bucket Aerosol Glass Cleaner, 16 oz 12 cans Lysol Disinfectant Spray Aerosol, 12.5 oz 6 cans Windex Spray Aerosol, 19.7 oz 3 cans Dishwashing Liquid Detergent, 32 oz 1 bottle Toilet Bowl Cleaner, 32 oz 14 bottles Aerosol Spray Paint Cans, 20 oz 7 cans Klean Strip Paint Stripper, 32 oz can 1 can Spectracide Wasp and Hornet Killer Aerosol, 28 oz 4 cans Liquid Hand Soap, 8 oz pump 3 bottles Hand Sanitizer, 12 oz pump 5 bottles

AIRPORT TRAFFIC CONTROL TOWER (CONTINUED)

Triple S Air Freshener Aerosol, 18 oz 1 can Staples Compressed Gas Duster Aerosol – 10 oz 4 cans Liquid Hand Soap, 64 oz 1 bottle Wizard Bathroom Spray, 8 oz 1 bottle Klean Strip Paint Stripper, 1 quart (Outdoors) 1 can Klean Strip Acetone Solvent, 5 gal 1 can

Rechargeable Batteries, Lead-acid, Lithium Ion – various sizes 180 units Lead-Acid Battery Back-up System 12 cells APC Battery Backup Units 15 units Rack Battery Backup Systems 25 units Large Capacitors on equipment & storage 30 units

Refrigerants GE Window AC Unit, 18,000 BTU - R-410A 35.28 oz 2 - Frigidaire/Electrolux Window AC Unit, 10,000 BTU - R-410A - 15.58 oz ea 31.16 oz 4 - Trane ProSpace PTAC 12,000 BTU, R-410A – 35.4 oz ea 247.8 oz 1 - LG PTAC 10,000 BTU, R-410A – 31.7 oz 31.7 oz

Teterboro Airport

D23286024-TERMINAL FAC MODERN & REPLACE

Miscellaneous Smoke Detectors 14 units Fluorescent Lamps, 4 ft 171 units Fluorescent Light Ballasts 56 units ABC Fire Extinguishers, 10 – 20# 34 cylinders Egress Lights 14 units Oil-filled Hydraulic Door Closing Systems, 5 oz 15 units

Tower Cab Rechargeable Battery Flashlights/ 2 units Strobe 1 unit Hand Soap, 8 oz 1 bottles Purell Hand Sanitizer, 12 oz 1 unit Hand Rx Sanitizer, 16.8 oz 1 unit First Aid Kit 1 unit Lysol Disinfectant Spray Aerosol, 12.5 oz 1 can Battery Backup Systems 4 units Triple S Baby Powder Air Freshener, 12 oz 1 can Assured Instant Hand Sanitizer, 10 oz 1 bottle

Trane RTU-1, R-22 18.3 lbs Cab Refrigerator Embraco EM45HHR, R134A 5.75 oz

STORAGE SHED

Suspect Mold, Roof ~50 sf BETCO Advanced Alcohol Gel Sanitizer, 1 gal 8 bottles ABC Fire Extinguisher, 20 lbs 3 units

BASE BUILDING

Emergency…