Appendix H(f) - Building 179 Hazardous Materials Report.pdf

TYNDALL AFB PRE-DEMOLITION SURVEY

W912DY-19-P-0053

Pre-Demolition Report for Asbestos, Hazardous Materials & Soil Testing

For:

Facilities Reduction Program FY19 Tyndall II Tyndall AFB, Florida

Building 179 Pavilion Hangar 2 (B180)

Prepared For:

US Army Corps of Engineers

Engineering & Support Service Center 4910 University Square, Suite 4

Huntsville, Alabama 35816-1822 Facilities Reduction Program

ATTN: CEHNC-ISF

March 2020

AQ#: 15671

ii

CERTIFICATION PAGE

Pre-Demolition Report for Asbestos, Hazardous Materials & Soils Testing

Facilities Reduction Program FY19 Tyndall II

Tyndall Air Force Base, Florida Building 179 Pavilion Hangar 2 (B180)

AirQuest Project #15671

Prepared For:

US Army Corps of Engineers Engineering & Support Service Center

4910 University Square, Suite 4 Huntsville, Alabama 35816-1822

ATTN: CEHNC-ISF

Prepared By:

AirQuest Environmental, Inc.

6851 Southwest 45th Street

Fort Lauderdale, Florida 33314

Adrian Amicucci Traci-Anne Boyle, CIH, CSP Asbestos Building Inspector FL Asbestos Consultant #AX-60

Ted Smith, PG

FL Professional Geologist No. PG1368 iii

TABLE OF CONTENTS

PAGE

1 INTRODUCTION AND SITE DESCRIPTION 1

1.1 PURPOSE 1

1.2 SITE DESCRIPTION 1

1.3 DEMOLITION OVERVIEW 1

2 ASBESTOS SURVEY 2

2.1 SURVEY METHODS 2

2.2 LABORATORY ANALYSIS 2

2.3 SUSPECT ASBESTOS-CONTAINING MATERIALS 3

3 LEAD BASED PAINT SCREENING 3

4 TCLP RCRA METALS 4

4.1 TCLP SAMPLE COLLECTION 4

4.2 TCLP SAMPLE RESULTS 4

5 PCBS 5

6 OTHER REGULATED MATERIALS INVENTORY 5

7 SOIL TESTING FOR ORGANOCHLORINE PESTICIDES 6

8 CONCLUSIONS AND RECOMMENDATIONS 6

8.1 ASBESTOS CONCLUSIONS AND RECOMMENDED RESPONSE ACTION 6

8.2 LEAD SCREENING & OSHA LEAD GUIDANCE 8

8.3 TCLP RCRA METALS / LEAD 8

8.4 PCBS 8

8.5 OTHER REGULATED MATERIALS 8

8.6 SOIL CONCLUSIONS 8

9 LIMITATIONS 9

iv

TABLES

Table 1 – Survey Information Table 2 – Asbestos Laboratory Analysis and Summary Table 3 - Lead Based Paint Screening Information Table 4 - Waste Stream Composition Table 5 – Toxicity Characteristic Leachate Procedure Results Table 6 – PCB Results Table 7 – Soil Sample Analytical Results

APPENDICES

Appendix I – Certifications

Appendix II – Sample Location Diagrams

Appendix III – Structure Demolition Overview (Diagram, Aerial Photographs, Photographs)

Appendix IV – Asbestos Laboratory Report and Chain of Custody Record

Appendix V – Suspect Asbestos Containing Material Photographs

Appendix VI – TCLP Laboratory Report and Chain of Custody Record

Appendix VII – PCB Laboratory Report and Chain of Custody Record

Appendix VIII – Soil Boring Logs and Soil Boring Location Photographs

Appendix IX – Soil Laboratory Report and Chain of Custody Record

AirQuest Project #15671 1 Building 179 Pre-Demolition W912DY-19-P-0053 Hazardous Materials & Asbestos Survey

1 INTRODUCTION AND SITE DESCRIPTION

In accordance with the Performance Work Statement (PWS) for contract W912DY-19-P-0053, AirQuest Environmental, Inc. (“AirQuest”) performed pre-demolition asbestos, hazardous materials, and soil testing for Building 179 located at Tyndall Air Force Base, Florida (“the site”).

The surveys were performed by AirQuest Project Team Members as shown in Table 1. Copies of applicable licenses and accreditations are included in Appendix I.

Table 1 – Survey Information

Survey Name Survey Date

Asbestos Adrian Amicucci 22 November 2019

TCLP Waste Stream Travis Holland 02 December 2019

PCB Waste Stream Jason Cronin 02 December 2019

Other Regulated Materials Spencer Estebanez 22 November 2019

Soil Sample Collection Ted Smith 23 November 2019

TCLP – Toxicity Characteristic Leachate Procedure PCB – Polychlorinated Biphenyl

1.1 PURPOSE

The purpose of this survey was to identify asbestos-containing materials (ACM) within the interior, exterior and roof of the building; to determine if Other Regulated Materials (ORM) materials were present; to complete a waste stream analysis for Toxicity Characteristic Leachate Procedure (TCLP) Resource Conservation and Recovery Act (RCRA)-8 metals and Polychlorinated Biphenyls (PCBs); and to collect soil samples for organochlorine pesticides (OCP) for each structure. Diagrams depicting sampling locations are provided in Appendix II.

The investigation was conducted to facilitate the repairs at Tyndall Air Force Base following Hurricane Michael.

1.2 SITE DESCRIPTION

Building 179 Pavilion Hangar 2 (B180) was a 500 square foot, single-story structure built in 1981. The structure consisted of a concrete slab foundation with a metal roof that was supported by wood beams.

1.3 DEMOLITION OVERVIEW

A diagram illustrating the general layout of the site was prepared using files provided by the client if available or drawn onsite by the AirQuest inspector. AirQuest prepared aerial photographs and photographed an overview of the interior and exterior of the building for purposes of assisting contractors in evaluation of the demolition requirements. The diagram and photographs are included in Appendix III.

AirQuest Project #15671 2 Building 179 Pre-Demolition W912DY-19-P-0053 Hazardous Materials & Asbestos Survey

2 ASBESTOS SURVEY

A pre-demolition asbestos survey suitable to meet the requirements of the National Emissions Standard for Hazardous Air Pollutants (NESHAPs) and State of Florida regulations was performed at the site.

2.1 SURVEY METHODS

The sampling protocol used generally followed Asbestos Hazard Emergency Response Act (AHERA) guidelines. AHERA was promulgated by the United States Environmental Protection Agency (EPA) in 1987 and regulated public schools.

Suspect materials were differentiated into three categories: surfacing material, thermal system insulation, or miscellaneous material. Surfacing material is anything that is sprayed or troweled onto a surface; thermal system insulation is material used to insulate HVAC pipes, tanks, etc., and miscellaneous material is any other type of material.

A homogeneous area is defined as an area of surfacing material, thermal system insulation material, or miscellaneous material that is uniform in color and texture. A homogeneous area is not limited to only a room but can be found in several rooms. Sample selection in the building was determined by identifying the homogeneous areas and basing sampling locations upon these areas.

In conducting the building inspection in compliance with local, state, and federal regulations, all suspected ACM which were accessible to the inspector, were either sampled to confirm the actual presence of asbestos or assumed to contain asbestos.

2.2 LABORATORY ANALYSIS

Analysis was performed using Polarized Light Microscopy (PLM) with dispersion staining. The laboratory is rated proficient through National Institute of Standards and Technology- National Voluntary Laboratory Accreditation Program (NIST-NVLAP) for bulk asbestos analysis.

NESHAP defines ACM as containing more than 1% asbestos as determined using PLM (as specified in Appendix E, Subpart E, 40 CFR part 763, Section 1, Polarized Light Microscopy).

NESHAP defines friable ACM as any material containing more than 1% asbestos that, when dry, can be crumbled, pulverized or reduced to a powder by hand pressure. If the asbestos content of a friable material is less than ten (10) percent as determined by a method other than point counting by PLM, the client may elect to verify the asbestos content by point counting using PLM.

Because of the inherent limitations of PLM bulk sample analysis, any friable sample reported as <2% asbestos by PLM was automatically analyzed by the PLM point count method to determine whether it may be regulated under the asbestos NESHAP.

Estimates of quantities of ACM were based upon the identification of suspect materials. Where suspect ACM were located behind walls, above ceilings, beneath carpeting, or other concealed conditions and the quantities cannot be verified, the estimate is based upon the conditions present during the survey. These estimates are not to be considered absolute and should be verified when the ACM is exposed.

AirQuest Project #15671 3 Building 179 Pre-Demolition W912DY-19-P-0053 Hazardous Materials & Asbestos Survey

2.3 SUSPECT ASBESTOS-CONTAINING MATERIALS

Homogenous areas (HA) of suspect material were identified and samples were collected and submitted under chain of custody to EMSL Analytical, Inc. (“EMSL”) for laboratory analysis of asbestos by PLM. If identified, friable samples with <2% asbestos were further analyzed by the PLM point count method to confirm the PLM results. A copy of the laboratory report and chain of custody record is included in Appendix IV.

Sample descriptions and laboratory results are summarized in Table 2. Photographs of each HA are included in Appendix V.

Table 2 – Asbestos Laboratory Analysis and Summary

HA Sample Number

Description of Suspect Material

Location Asbestos Content %

1 179-1 Concrete Slab – Floor Exterior Northwest ND

1 179-2 Concrete Slab – Floor Exterior Northeast ND

1 179-3 Concrete Slab – Floor Exterior Southeast ND

1 179-4 Concrete Slab – Floor Exterior Southwest ND

1 179-5 Concrete Slab – Floor Exterior Center ND

HA- Homogenous Area ND – None Detected

3 LEAD BASED PAINT SCREENING

An inspection was conducted to screen for the existence of lead containing painted building components. Testing of the painted building components was performed using an XRF Spectrometer. The XRF is a screening instrument currently recommended by the US Department of Housing and Urban Development (HUD) for analysis of lead levels in paint. The screening was used to assist in determining the need and relative concentrations of lead on painted building components for purposes of designing a sampling scheme for a composite waste stream analysis and demolition contractor worker protection information. The screening was not intended to be a lead-based paint survey in accordance with HUD guidelines. A summary of the screening results is included in Table 3.

AirQuest Project #15671 4 Building 179 Pre-Demolition W912DY-19-P-0053 Hazardous Materials & Asbestos Survey

Table 3 - Lead Based Paint Screening Information

Structure Color Substrate Location Results1 Pb (mg/cm2)

Beam Brown Metal Exterior Negative 0.1 Beam Brown Metal Exterior Negative 0.1

Pb - Lead mg/cm2 – milligrams per square centimeter 1Indicates if the material meets the Department of Housing and Urban Development definition of Lead Based Paint

4 TCLP RCRA METALS

A waste stream composite sample was collected from the building for laboratory analysis of TCLP RCRA-8 Metals.

4.1 TCLP SAMPLE COLLECTION

The sample composition was determined by the composition of the materials comprising the building. Each major building component (such as wood, metal, concrete, glass, etc.) was estimated as a percentage of the weight of the building whole. Once the composition of the building was estimated, representative samples were collected of each material, in an approximate weight proportion as shown in Table 4.

Table 4 - Waste Stream Composition

Waste Stream Component Percentage of

Waste Concrete 75

Wood 10 Metal 15

Total Percentage 100

4.2 TCLP SAMPLE RESULTS

The samples were submitted under chain of custody to Spectrum Environmental Laboratories (“Spectrum”), a National Environmental Laboratory Accreditation Conference (NELAC) accredited laboratory, for analysis of TCLP-RCRA-8 Metals by EPA via 1311/6010C/7470A. The results are summarized in Table 5.

Table 5 – Toxicity Characteristic Leachate Procedure Results

Sample TCLP Results (milligrams/liter)

Arsenic Barium Cadmium Chromium Lead Mercury Selenium Silver 179-

ND 0.166 ND 0.0450 ND ND ND ND

Limit1 5.0 100.0 1.0 5.0 5.0 0.2 1.0 5.0 1Regulatory Limit per 40 CFR 261.24 ND – None Detected

AirQuest Project #15671 5 Building 179 Pre-Demolition W912DY-19-P-0053 Hazardous Materials & Asbestos Survey

5 PCBS

Samples for PCBs were collected in general accordance with the EPA Region 1 Standard Operating Procedure for Sampling Porous Surfaces for Polychlorinated Biphenyls (PCBs), May 2011.

The samples were collected from representative painted surfaces to include up to a half-inch of the substrate. The samples were submitted under chain of custody to Spectrum for analysis by EPA Method SW 846 3540C/8020A.

Table 6 – PCB Results

Sample Results (mg/kg)

Aroclor-

Aroclor-

Aroclor-

Aroclor-

Aroclor-

Aroclor-

Aroclor-

179-001 Concrete

ND ND ND ND ND ND ND

179-002 Paint

ND ND ND ND ND ND ND

1Regulatory Limit per 40 CFR 761.50 Subpart D is 50 mg/kg mg/kg – milligrams/kilogram ND – None Detected

6 OTHER REGULATED MATERIALS INVENTORY

AirQuest conducted another regulated/hazardous materials inventory in general accordance with the Recommended Management Practices for the Removal of Hazardous Materials from Buildings Prior to Demolition prepared by the University of Florida and sponsored by the Florida Department of Environmental Protection, 1999. The inventory included lamps, thermostats, and light switches potentially containing mercury; exit signs, emergency lights, and smoke alarms that have batteries; lighting ballasts which contain polychlorinated biphenyls (PCBs); transformers;

freon, hazardous chemicals and petroleum products; and lead pipes and roof vent flashings.

Certain assumptions for the inspection of fluorescent light ballasts for PCBs were utilized for the building inspections to be completed in a timely and cost-effective manner. As required by regulation, lighting ballasts must not contain PCBs and the label on the ballast must state “No PCB”. AirQuest inventoried 100% of the fluorescent lighting fixtures and inspected a representative of each type of fixture (i.e. 2-foot, 4-foot, etc.) for the “No PCB” labeling. Each exit sign and emergency lights were presumed to each contain a single lead-acid rechargeable battery.

There was no ORM present onsite at the time of the inspection.

AirQuest Project #15671 6 Building 179 Pre-Demolition W912DY-19-P-0053 Hazardous Materials & Asbestos Survey

7 SOIL TESTING FOR ORGANOCHLORINE PESTICIDES

AirQuest advanced four (4) soil borings and collected two (2) samples at each boring location at depths of zero to six inches (0 - 6 in.) and eighteen to twenty-four inches (18 – 24 in.) below land surface using a properly decontaminated hand bucket auger. The samples were generally collected near the four corners of the building as shown in Appendix II.

The soil sampling was conducted in accordance with Florida Department of Environmental Protection (FDEP) Standard Operating Procedures SOP-001-01 FS 3000 (Soil) and SOP-001-01 FQ1000 (Field Quality Control Requirements). One boring log was completed for each building location documenting the observed lithology, visually estimated moisture content, noticeable odors, soil color, sample collection times, sampler’s name, sampling interval and boring completion method. The soil boring log and soil boring location photographs are included in Appendix VIII.

Samples were placed in dedicated sample containers provided by the laboratory and labeled according to the referenced building/structure, collection time, sampler’s name and analysis. A chain of custody form was completed to document the chronology of ownership, control and transfer of the samples. All samples were placed in a cooler filled with ice for transfer to the laboratory.

The soil samples were shipped to Eurofins TestAmerica (“TestAmerica”) in Pensacola, Florida, a NELAC accredited environmental laboratory licensed in the State of Florida, for analysis by EPA Method: 8081B (Organochlorine Pesticides by GC). Analytical results are summarized in Table

7. A copy of the laboratory report and chain of custody record is included in Appendix IX.

The analytical results indicate trace to moderate levels of OCPs 4,4’-DDD, 4,4’-DDE, 4,4’-DDT, Dieldrin, and Total Chlordane above laboratory method detection limits and some above practical quantitation limits, in most of the soil samples. Sample OCP-179.5 analytical results indicate Dieldrin concentrations above Residential Soil Cleanup Target Levels (SCTLs) but below the Commercial/Industrial SCTLs. All the other detected OCP constituents were below the Residential or Commercial/Industrial SCTLs listed in Chapter 62-777 FAC, the criteria used by the FDEP.

8 CONCLUSIONS AND RECOMMENDATIONS

A thorough pre-demolition inspection for asbestos and hazardous materials was conducted at the site and an inventory of the materials was created. The soils surrounding the site were sampled and analyzed for pesticides. Based upon the results of the inspections, recommendations for each contaminant are discussed separately below.

8.1 ASBESTOS CONCLUSIONS AND RECOMMENDED RESPONSE ACTION

The results of our observation and laboratory analysis did not identify ACM within the samples collected from the site.

AirQuest Project #15671 7 Building 179 Pre-Demolition W912DY-19-P-0053 Asbestos, Hazardous Materials & Soil Testing

Table 7 – Soil Sample Analytical Results

Sample Sample Depth (Inches)

Results (mg/kg)

4,4’-DDD 4,4’-DDE 4,4’-DDT Dieldrin Total Chlordane

OCP-179.1 0-6 ND 0.0059I ND ND ND

OCP-179.2 18-24 ND 0.00066I ND ND ND

OCP-179.3 0-6 ND 0.00087I ND 0.00080I ND

OCP-179.4 18-24 ND ND ND ND ND

OCP-179.5 0-6 0.0020I 0.037 0.024 0.091 ND

OCP-179.6 18-24 0.00039I 0.0072 0.0026 0.0083 0.00053I

OCP-179.7 0-6 ND 0.0019 ND 0.0030 ND

OCP-179.8 18-24 ND 0.00043I ND 0.00053I ND

SCTL (Commercial/Industrial) 22 15 15 0.3 14

SCTL (Residential) 4.2 2.9 2.9 0.06 2.8 mg/kg – milligrams/kilogram ND – None Detected Above the Method Detection Limit SCTL – Soil Cleanup Target Level, Chapter 62-777 Florida Administrative Code I – The Reported Value is Between the Laboratory Method Detection Limit and the Laboratory Practical Quantitation Limit

AirQuest Project #15671 8 Building 179 Pre-Demolition W912DY-19-P-0053 Asbestos, Hazardous Materials & Soil Testing

8.2 LEAD SCREENING & OSHA LEAD GUIDANCE

Lead was identified in the paint at the site. Under the present OSHA lead construction standard, all identified lead-containing materials affected by construction activities falls under the requirements of 29 CFR 1926. There are no current government guidelines defining a lead-based paint or lead concentration that creates a hazardous atmosphere when disturbed. Based on current OSHA guidelines, for those employees who will be disturbing lead-containing paint (LCP), their employer must make an initial determination by monitoring employee exposure if any employee is exposed to lead at or above 30 micrograms per cubic meter for an eight-hour time weighted average (30 µg/m3 8-hour time weighted average). The employer must implement OSHA prescribed protective measures until they can demonstrate that the employee exposure is not in excess of the action level.

In general, relatively low levels of lead were detected in the various coated surfaces surveyed.

Depending on the degree and type of disturbance of these surfaces (i.e. sanding, cutting, or demolishing), employers may be required to implement varying degrees of OSHA prescribed protective measures. These protective measures must be maintained until it can be demonstrated that employee exposures do not exceed the action level. The employer should also implement and maintain a written compliance program detailing the protective measures they will utilize to control lead exposure during renovation activities.

8.3 TCLP RCRA METALS / LEAD

The results of the laboratory analysis indicate that the waste stream generated from the site is non-hazardous.

8.4 PCBS

The results of the sampling and analysis did not identify PCBs in composite waste stream paint and concrete samples.

8.5 OTHER REGULATED MATERIALS

There was no ORM present onsite at the time of the inspection.

8.6 SOIL CONCLUSIONS

The soil analytical results identified the compound Dieldrin at a concentration of 0.091 mg/kg in the 0-6-inch interval of borehole number 3 (sample OCP-179.5). The reported concentration for sample OCP-179.5 is above the Residential SCTL of 0.06 mg/kg but below the Commercial/Industrial SCTL of 0.3 mg/kg.

Upon completion of the building demolition and concrete pad removal, AirQuest recommends that the area of impacted soil (southeast corner of the building) be excavated and stockpiled onsite.

The excavation should extend to a depth of two (2) feet below land surface (BLS) and extend out in an approximate three (3) foot radius around borehole number 3. Five (5) confirmation samples should be collected from the excavation area and submitted for laboratory analysis to confirm Dieldrin and other OCPs are below the residential FDEP SCTL.

The stockpiled soil should be protected with proper engineering controls to prevent cross contamination of surrounding soil. At a minimum, the soil should be in a secured bermed area

AirQuest Project #15671 9 Building 179 Pre-Demolition W912DY-19-P-0053 Asbestos, Hazardous Materials & Soil Testing lined and covered with polyethylene sheeting. The demolition personnel should utilize Level C PPE protection to reduce the potential for exposure to any impacted soils. Once it has been confirmed that all contaminated soils have been removed from the excavation and stockpiled, the excavated soil must be sampled and characterized for proper disposal.

9 LIMITATIONS

If any suspect hazardous/asbestos containing building materials are encountered during demolition activities that were not sampled in this report, the materials should not be disturbed until they have been sampled and identified as non-hazardous and non-ACM through appropriate investigation and/or laboratory analysis. Many of the roofs at Tyndall Air Force Base were sealed with an EPDM roofing system covering all the original roofing materials. It is possible, if not likely, that additional suspect asbestos materials are present under the EPDM and were not identified during the asbestos survey.

This report was prepared in a manner consistent with that level of care and skill ordinarily exercised by members of the profession currently practicing under similar conditions. This report was prepared for the exclusive use of the client and assigned agents and is not intended for any other purposes. Our report is based on the information available to us at the time of our investigation and limited in scope to the stated purpose and/or the area(s) inspected. Other conditions elsewhere in the site may differ from those in the inspected/ surveyed locations and such conditions are unknown, may change over time, and/or have not been considered. This report does not claim to identify all potential hazards and/or contaminants that may be present, nor does it imply any medical opinion on the relationship of potential health effects with any reported hazards and/ or contaminants. Our opinions are based on our findings and professional expertise, with no guaranty or warranty implied herein. Should additional information become available, we reserve the right to determine the impact, if any, of the new information on our opinions, conclusions, and recommendations if necessary, as warranted by the discovery of the additional information. AirQuest accepts no responsibility for interpretation of this report by others. Its contents shall not be used or relied upon by other parties without prior written authorization by AirQuest.

Appendix I Certifications

JONATHAN ZACHEM, SECRETARYRICK SCOTT, GOVERNOR

STATE OF FLORIDA

DEPARTMENT OF BUSINESS AND PROFESSIONAL REGULATION

ASBESTOS LICENSING UNIT

THE ASBESTOS CONSULTANT HEREIN IS LICENSED UNDER THE

PROVISIONS OF CHAPTER 469, FLORIDA STATUTES

BOYLE, TRACI-ANNE

Do not alter this document in any form.

AIRQUEST ENVIRONMENTAL INC

LICENSE NUMBER: AX60

EXPIRATION DATE: NOVEMBER 30, 2020

This is your license. It is unlawful for anyone other than the licensee to use this document.

6851 SW 45 ST

DAVIE FL 33314

Always verify licenses online at MyFloridaLicense.com https://www.myfloridalicense.com/LicenseDetail.asp?SID=&id=8c21d1d6249bcaa3338cefa039457259

JONATHAN ZACHEM, SECRETARYRICK SCOTT, GOVERNOR

STATE OF FLORIDA

DEPARTMENT OF BUSINESS AND PROFESSIONAL REGULATION

BOARD OF PROFESSIONAL GEOLOGISTS

THE PROFESSIONAL GEOLOGIST HEREIN IS LICENSED UNDER THE

PROVISIONS OF CHAPTER 492, FLORIDA STATUTES

SMITH, TED J

Do not alter this document in any form.

1735 CLARENDON AVENUE

LICENSE NUMBER: PG1368

EXPIRATION DATE: JULY 31, 2020

This is your license. It is unlawful for anyone other than the licensee to use this document.

LAKELAND FL 33803

Always verify licenses online at MyFloridaLicense.com https://www.myfloridalicense.com/LicenseDetail.asp?SID=&id=6b0348687cc372fc3b319e7b329b1312

Appendix II Sample Location Diagrams

Sampling Locations

LEGEND

ASBESTOS SAMPLE # 1

PCB PAINT COMPOSITE P

PCB CONCRETE COMPOSITE C

SOIL BORING LOCATION 1

Contract

FACILITIES REDUCTION PROGRAM

FY19 TYNDALL II

W912DY-19-P-0053

DATE: MARCH 2020

Site

TYNDALL AIR FORCE BASE

FLORIDA

BUILDING: PAVILION HANGAR 2

(B180)

BUILDING #: 179

6851 SW 45TH STREET

FT. LAUDERDALE, FLORIDA 33314

AIRQUEST PROJECT 15671

Appendix III Structure Demolition Overview Diagram, Aerial

Photographs and Demolition Overview Photographs

Demolition Overview

BUILDING INFORMATION

NAME PAVILION HANGAR 2

(B180)

NUMBER 179

YEAR

BUILT 1981

SQUARE

FEET 500

STORIES 1

Contract

FACILITIES REDUCTION PROGRAM

FY19 TYNDALL II

W912DY-19-P-0053

DATE: MARCH 2020

Site

TYNDALL AIR FORCE BASE

FLORIDA

BUILDING: PAVILION HANGAR 2

(B180)

BUILDING #: 179

6851 SW 45TH STREET

FT. LAUDERDALE, FLORIDA 33314

AIRQUEST PROJECT 15671

Building 179 – Pre-Hurricane Aerial Photographs

Overview

Side Angle Side Angle

Side Angle Side Angle

Images Obtained Using Google Earth

Overview

Bld 179 - PAVILION HANGAR 2 (B180) Tyndall Air Force Base

AirQuest Environmental, Inc.

Project #15671

Exterior

Appendix IV Asbestos Laboratory Report and Chain of Custody Record

EMSL Analytical, Inc.

3303 PARKWAY CENTER COURT Orlando, FL 32808

Tel/Fax: (407) 599-5887 / (407) 599-9063 http://www.EMSL.com / orlandolab@emsl.com

341918741EMSL Order:

Customer ID: AQE63

Customer PO:

Project ID:

Attention: Phone:Lab Results (954) 792-4549

Fax:AirQuest Environmental, Inc. (954) 792-2221

Received Date:6851 Southwest 45th Street 11/26/2019 9:20 AM

Analysis Date:Fort Lauderdale, FL 33314 11/26/2019

Collected Date: 11/22/2019

Project: Tyndall AFB 15671-179

Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized

Light Microscopy

Sample Description Appearance % Fibrous % Non-Fibrous

Non-Asbestos Asbestos

% Type

179-1

341918741-0001

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

30%

15%

55%

Gray

Non-Fibrous

Homogeneous

Exterior Northwest -

Floor-Concrete Slab

179-2

341918741-0002

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

30%

15%

55%

Tan

Non-Fibrous

Homogeneous

Exterior Northeast -

Floor-Concrete Slab

179-3

341918741-0003

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

30%

15%

55%

Gray/Tan

Non-Fibrous

Homogeneous

Exterior Southeast -

Floor-Concrete Slab

179-4

341918741-0004

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

30%

15%

55%

Gray/Tan

Non-Fibrous

Homogeneous

Exterior Southwest -

Floor-Concrete Slab

179-5

341918741-0005

None DetectedQuartz

Ca Carbonate

Non-fibrous (Other)

30%

15%

55%

Gray

Non-Fibrous

Homogeneous

Exterior Center -

Floor-Concrete Slab

Analyst(s)

Jessicka Lopez (1)

Laura Vera (4)

Carlos Rivadeneyra, Laboratory Director or Other Approved Signatory

EMSL maintains liability limited to cost of analysis . The above analyses were performed in general compliance with Appendix E to Subpart E of 40 CFR (previously EPA 600/M4-82-020 "Interim

Method"), but augmented with procedures outlined in the 1993 ("final") version of the method. This report relates only to the samples reported above, and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations . Interpretation and use of test results are the responsibility of the client. All samples received in acceptable condition unless otherwise noted. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. EMSL recommends gravimetric reduction for all non -friable organically bound materials prior to analysis. Estimation of uncertainty is available on request.

Samples analyzed by EMSL Analytical, Inc. Orlando, FL NVLAP Lab Code 101151-0

Initial report from: 11/26/2019 17:00:26

Page 1 of 1ASB_PLM_0008_0001 - 1.78 Printed: 11/26/2019 5:00 PM

O r d e r I D

P a g e

O f

Appendix V Suspect Asbestos Containing Material Photographs

HA Photolog

Tyndall Air Force Base

AirQuest Environmental, Inc.

HA 1- Concrete Slab

Appendix VI TCLP Laboratory Report and

Chain of Custody Record

1460 West McNab Road

Fort Lauderdale, FL 33309

1-800-ANALYTE Phone

(954) 978-6400 Phone

(954) 978-2233 Fax

13 December 2019

Dear Paul LeBlanc:

This report details the analytical results of samples collected at the above -referenced project location as well as the results of any associated quality control samples. These samples were received by Florida Spectrum Environmental

Services at 12/04/2019 09:15.

All Analyses were performed according to the TNI/NELAP standard unless indicated by a "~" on the report.

Your samples will be retained by Florida Spectrum Environmental for a period of at least 30 days following sample receipt or until the longest of the preparation and/or analytical hold times expires, whichever is shorter. After that time , they will be properly disposed without further notice, unless there exists an explicit contractual agreement to the contrary. We reserve the right to return any unused samples, extracts, or related materials or solutions to you if we consider it necessary. Examples might include those samples identified as hazardous wastes, submissions where the sample sizes significantly exceed those required for analysis, samples containing controlled substances, etc.

We thank you for selecting Florida Spectrum Environmental to serve your analytical needs. Should you have any questions or require additional information regarding any of the information in this report, please feel free to contact us at any time. We appreciate the opportunity to be of service.

Florida Spectrum Environmental Inc.

Paul LeBlanc

6851 SW 45th Street

Ft. Lauderdale, FL 33314

RE: 15671 Tyndall AFB

AirQuest Environmental, Inc.

Project Location: Tyndall AFB

Lab Work Order (COC): 19L0107

NELAP Certificate No. E86006

Report Printed:

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/13/2019

Report To:

19L0107Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

Client Sample ID Laboratory ID Matrix Collection Date

DETECTED ANALYTE SUMMARY

Collection TimeAnalyte Result Units

179-001 19L0107-01 Solid 12/2/2019 0:00Chromium mg/L0.0450

179-001 19L0107-01 Solid 12/2/2019 0:00Barium mg/L0.166

179-001 19L0107-01 Solid 12/2/2019 0:00Fluid Type (1,2,or 3) .1.00

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

111 Easton Dr.

Lakeland, FL 33803

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/13/2019

Report To:

19L0107Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

ResultParameter MDL Date Analy.QC Units

Lab ID:

Client Sample ID: 179-001 19L0107-01 Collection Date:

Matrix: Solid

12/02/19 00:00

Laboratory Analysis Report

Received Date: 12/04/19 09:15

PQL Method Date Ext. Analyst

Travis HollandCollected By:

Dil

TCLP Extraction by EPA 1311

. EPA 1311 12/05 10:0012/04 16:00 MAZFluid Type (1,2,or 3) 1.00 1

TCLP Metals by 6000/7000 Series Methods mg/L 0.029 0.100 EPA 6010/3010 12/05 14:3212/05 10:30 MAZArsenic UND 1 mg/L 0.0008 0.0100 EPA 6010/3010 12/05 14:3212/05 10:30 MAZBarium 0.166 1 mg/L 0.0032 0.0100 EPA 6010/3010 12/05 14:3212/05 10:30 MAZCadmium UND 1 mg/L 0.0074 0.0500 EPA 6010/3010 12/05 14:3212/05 10:30 MAZChromium I0.0450 1 mg/L 0.014 0.100 EPA 6010/3010 12/05 14:3212/05 10:30 MAZLead UND 1 mg/L 0.0015 0.0045 EPA 7470 12/11 11:5412/10 09:00 MAZMercury UND 1 mg/L 0.031 0.150 EPA 6010/3010 12/05 14:3212/05 10:30 MAZSelenium UND 1 mg/L 0.0012 0.0080 EPA 6010/3010 12/05 14:3212/05 10:30 MAZSilver UND 1

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/13/2019

Report To:

19L0107Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

Result Limit

Reporting

Units Level

Spike

Result

Source

%REC

%REC

Limits RPD

RPD

Limit Notes Analyte

TCLP Metals by 6000/7000 Series Methods - Quality Control

Batch 19L0011 - EPA 3010A

Blank (19L0011-BLK1) Prepared & Analyzed: 12/05/2019

Arsenic mg/LND 0.100 U

Chromium "ND 0.0500 U

Cadmium "ND 0.0100 U

Lead "ND 0.100 U

Barium "ND 0.0100 U

Silver "ND 0.0080 U

Selenium "ND 0.150 U

LCS (19L0011-BS1) Prepared & Analyzed: 12/05/2019

Chromium mg/L0.4820 0.0050 0.5000 80-12096.4

Barium "0.4676 0.0010 0.5000 80-12093.5

Arsenic "0.4914 0.010 0.5000 80-12098.3

Cadmium "0.4865 0.0010 0.5000 80-12097.3

Selenium "0.4962 0.015 0.5000 80-12099.2

Lead "0.4743 0.010 0.5000 80-12094.9

Silver "0.4734 0.0008 0.5000 80-12094.7

Matrix Spike (19L0011-MS1) Prepared & Analyzed: 12/05/2019Source: 19L0112-01

Cadmium mg/L4.984 0.0100 5.000 0.0120 75-12599.4

Barium "4.967 0.0100 5.000 0.1510 75-12596.3

Arsenic "5.166 0.100 5.000 ND 75-125103

Silver "4.902 0.0080 5.000 ND 75-12598.0

Chromium "4.981 0.0500 5.000 0.0180 75-12599.3

Selenium "5.108 0.150 5.000 ND 75-125102

Lead "4.853 0.100 5.000 ND 75-12597.1

Matrix Spike Dup (19L0011-MSD1) Prepared & Analyzed: 12/05/2019Source: 19L0112-01

Barium mg/L5.001 0.0100 5.000 0.1510 2075-125 0.68297.0

Cadmium "5.016 0.0100 5.000 0.0120 2075-125 0.640100

Chromium "5.037 0.0500 5.000 0.0180 2075-125 1.12100

Arsenic "5.216 0.100 5.000 ND 2075-125 0.963104

Selenium "5.140 0.150 5.000 ND 2075-125 0.625103

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/13/2019

Report To:

19L0107Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

Result Limit

Reporting

Units Level

Spike

Result

Source

%REC

%REC

Limits RPD

RPD

Limit Notes Analyte

TCLP Metals by 6000/7000 Series Methods - Quality Control

Batch 19L0011 - EPA 3010A

Matrix Spike Dup (19L0011-MSD1) Prepared & Analyzed: 12/05/2019Source: 19L0112-01

Silver mg/L4.939 0.0080 5.000 ND 2075-125 0.75298.8

Lead "4.886 0.100 5.000 ND 2075-125 0.67897.7

Batch 19L0030 - EPA 7470A Prep

Blank (19L0030-BLK1) Prepared: 12/10/2019 Analyzed: 12/11/2019

Mercury mg/LND 0.0045 U

LCS (19L0030-BS1) Prepared: 12/10/2019 Analyzed: 12/11/2019

Mercury mg/L0.0113 0.0004 0.01000 80-120113

Matrix Spike (19L0030-MS1) Prepared: 12/10/2019 Analyzed: 12/11/2019Source: 19L0112-01

Mercury mg/L0.0882 0.0045 0.1000 ND 80-12088.2

Matrix Spike Dup (19L0030-MSD1) Prepared: 12/10/2019 Analyzed: 12/11/2019Source: 19L0112-01

Mercury mg/L0.0864 0.0045 0.1000 ND 2080-120 2.0186.4

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/13/2019

Report To:

19L0107Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

Notes and Definitions

Sample results reported on a dry weight basis

Relative Percent DifferenceRPD dry

Not ReportedNR

Analyte NOT DETECTED at or above the detection limitND

Analyte DETECTEDDET

V Indicated that the analyte was detected in both the sample and the associated method blank.

The reported value is between the laboratory method detection limit and the laboratory practical quantitation limit.I

Z Too many colonies were present for accurate counting.

QC=Qualifier Codes as defined by DEP 62-160

Unless indicated, soil results are reported on actual (wet) weight basis.

Work performed by outside (subcontracted) labs denoted by SUB in Analyst Field.

Results relate only to this sample.

Authorized CSM Signature (954) 978-6400

Florida-Spectrum Environmental Services,Inc.

Certification# E86006

All NELAP certified analysis are performed in accordance with Chapter 64E-1 Florida Administrative code, which has been determined to be equivalent to NELAC standards. Analysis certified by programs other than NELAP are designated with a "~".

Maria Castellanos - Lab Manager

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

Appendix VII PCB Laboratory Report and

1460 West McNab Road

Fort Lauderdale, FL 33309

1-800-ANALYTE Phone

(954) 978-6400 Phone

(954) 978-2233 Fax

10 December 2019

Dear Paul LeBlanc:

This report details the analytical results of samples collected at the above -referenced project location as well as the results of any associated quality control samples. These samples were received by Florida Spectrum Environmental

Services at 12/04/2019 09:15.

All Analyses were performed according to the TNI/NELAP standard unless indicated by a "~" on the report.

Your samples will be retained by Florida Spectrum Environmental for a period of at least 30 days following sample receipt or until the longest of the preparation and/or analytical hold times expires, whichever is shorter. After that time , they will be properly disposed without further notice, unless there exists an explicit contractual agreement to the contrary. We reserve the right to return any unused samples, extracts, or related materials or solutions to you if we consider it necessary. Examples might include those samples identified as hazardous wastes, submissions where the sample sizes significantly exceed those required for analysis, samples containing controlled substances, etc.

We thank you for selecting Florida Spectrum Environmental to serve your analytical needs. Should you have any questions or require additional information regarding any of the information in this report, please feel free to contact us at any time. We appreciate the opportunity to be of service.

Florida Spectrum Environmental Inc.

Paul LeBlanc

6851 SW 45th Street

Ft. Lauderdale, FL 33314

RE: 15671 Tyndall AFB

AirQuest Environmental, Inc.

Project Location: Tyndall AFB

Lab Work Order (COC): 19L0121

NELAP Certificate No. E86006

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/10/2019

Report To:

19L0121Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

Client Sample ID Laboratory ID Matrix Collection Date

DETECTED ANALYTE SUMMARY

Collection TimeAnalyte Result Units

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/10/2019

Report To:

19L0121Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

ResultParameter MDL Date Analy.QC Units

Lab ID:

Client Sample ID: 179-001 19L0121-01 Collection Date:

Matrix: Solid

12/02/19 00:00

Laboratory Analysis Report

Received Date: 12/04/19 09:15

PQL Method Date Ext. Analyst

Travis HollandCollected By:

Dil

Polychlorinated Biphenyls (as Congeners) by EPA Method 8082 mg/kg wet 0.00386 0.0116 EPA 8082/3550 12/07 17:4312/05 10:50 ACPCB-1016 UND 3 mg/kg wet 0.00222 0.00665 EPA 8082/3550 12/07 17:4312/05 10:50 ACPCB-1221 UND 3 mg/kg wet 0.00584 0.0175 EPA 8082/3550 12/07 17:4312/05 10:50 ACPCB-1232 UND 3 mg/kg wet 0.00232 0.00697 EPA 8082/3550 12/07 17:4312/05 10:50 ACPCB-1242 UND 3 mg/kg wet 0.00144 0.00432 EPA 8082/3550 12/07 17:4312/05 10:50 ACPCB-1248 UND 3 mg/kg wet 0.00236 0.00707 EPA 8082/3550 12/07 17:4312/05 10:50 ACPCB-1254 UND 3 mg/kg wet 0.00430 0.0129 EPA 8082/3550 12/07 17:4312/05 10:50 ACPCB-1260 UND 3

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/10/2019

Report To:

19L0121Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

ResultParameter MDL Date Analy.QC Units

Lab ID:

Client Sample ID: 179-002 19L0121-02 Collection Date:

Matrix: Solid

12/02/19 00:00

Laboratory Analysis Report

Received Date: 12/04/19 09:15

PQL Method Date Ext. Analyst

Travis HollandCollected By:

Dil

Polychlorinated Biphenyls (as Congeners) by EPA Method 8082 mg/kg wet 0.00773 0.0232 EPA 8082/3550 12/07 18:1712/05 10:50 ACPCB-1016 UND 6 mg/kg wet 0.00443 0.0133 EPA 8082/3550 12/07 18:1712/05 10:50 ACPCB-1221 UND 6 mg/kg wet 0.0117 0.0351 EPA 8082/3550 12/07 18:1712/05 10:50 ACPCB-1232 UND 6 mg/kg wet 0.00465 0.0139 EPA 8082/3550 12/07 18:1712/05 10:50 ACPCB-1242 UND 6 mg/kg wet 0.00288 0.00863 EPA 8082/3550 12/07 18:1712/05 10:50 ACPCB-1248 UND 6 mg/kg wet 0.00472 0.0141 EPA 8082/3550 12/07 18:1712/05 10:50 ACPCB-1254 UND 6 mg/kg wet 0.00861 0.0258 EPA 8082/3550 12/07 18:1712/05 10:50 ACPCB-1260 UND 6

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/10/2019

Report To:

19L0121Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

Result Limit

Reporting

Units Level

Spike

Result

Source

%REC

%REC

Limits RPD

RPD

Limit Notes Analyte

Polychlorinated Biphenyls (as Congeners) by EPA Method 8082 - Quality Control

Batch 19L0215 - EPA 3550C

Blank (19L0215-BLK1) Prepared: 12/05/2019 Analyzed: 12/07/2019

PCB-1016 mg/kg wetND 0.00386 U

PCB-1221 "ND 0.00222 U

PCB-1232 "ND 0.00584 U

PCB-1242 "ND 0.00232 U

PCB-1248 "ND 0.00144 U

PCB-1254 "ND 0.00236 U

PCB-1260 "ND 0.00430 U

LCS (19L0215-BS1) Prepared: 12/05/2019 Analyzed: 12/07/2019

PCB-1016 mg/kg wet0.265 0.00386 0.3366 13-13978.7

PCB-1260 "0.281 0.00430 0.3336 20-11984.2

Matrix Spike (19L0215-MS1) Prepared: 12/05/2019 Analyzed: 12/07/2019Source: 19L0121-01

PCB-1016 mg/kg wet0.816 0.0116 1.004 ND 10-14981.3

PCB-1260 "0.852 0.0129 0.9950 ND 10-13785.6

Matrix Spike Dup (19L0215-MSD1) Prepared: 12/05/2019 Analyzed: 12/07/2019Source: 19L0121-01

PCB-1016 mg/kg wet0.717 0.0116 1.004 ND 3010-149 12.971.4

PCB-1260 "0.720 0.0129 0.9950 ND 3010-137 16.872.4

Blank (19L0215-BLK1) Prepared: 12/05/2019 Analyzed: 12/07/2019 mg/kg wet 0.03326 10-110Surrogate: Decachlorobiphenyl 67.00.0223

" 0.03326 22-159Surrogate: 2,4,5,6 Tetrachloro-m-xylene 59.30.0197

LCS (19L0215-BS1) Prepared: 12/05/2019 Analyzed: 12/07/2019 mg/kg wet 0.03329 10-110Surrogate: Decachlorobiphenyl 78.00.0260

" 0.03329 22-159Surrogate: 2,4,5,6 Tetrachloro-m-xylene 66.30.0221

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/10/2019

Report To:

19L0121Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

Result Limit

Reporting

Units Level

Spike

Result

Source

%REC

%REC

Limits RPD

RPD

Limit Notes Analyte

Polychlorinated Biphenyls (as Congeners) by EPA Method 8082 - Quality Control

Batch 19L0215 - EPA 3550C

Matrix Spike (19L0215-MS1) Prepared: 12/05/2019 Analyzed: 12/07/2019Source: 19L0121-01 mg/kg wet 0.09930 10-110Surrogate: Decachlorobiphenyl 94.50.0938

" 0.09930 22-159Surrogate: 2,4,5,6 Tetrachloro-m-xylene 87.80.0871

Matrix Spike Dup (19L0215-MSD1) Prepared: 12/05/2019 Analyzed: 12/07/2019Source: 19L0121-01 mg/kg wet 0.09930 10-110Surrogate: Decachlorobiphenyl 94.40.0938

" 0.09930 22-159Surrogate: 2,4,5,6 Tetrachloro-m-xylene 90.80.0902

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

6851 SW 45th Street

Paul LeBlanc

Ft. Lauderdale FL, 33314

12/10/2019

Report To:

19L0121Work Order #

Project: 15671 Tyndall AFB

Tyndall AFB

Notes and Definitions

U Indicated that the compound was analyzed for but not detected. This shall be used to indicate that the specific component was not detected. The value associated with the qualifier shall be the laboratory method detection limit.

Sample results reported on a dry weight basis

Relative Percent DifferenceRPD dry

Not ReportedNR

Analyte NOT DETECTED at or above the detection limitND

Analyte DETECTEDDET

V Indicated that the analyte was detected in both the sample and the associated method blank.

The reported value is between the laboratory method detection limit and the laboratory practical quantitation limit.I

Z Too many colonies were present for accurate counting.

QC=Qualifier Codes as defined by DEP 62-160

Unless indicated, soil results are reported on actual (wet) weight basis.

Work performed by outside (subcontracted) labs denoted by SUB in Analyst Field.

Results relate only to this sample.

Authorized CSM Signature (954) 978-6400

Florida-Spectrum Environmental Services,Inc.

Certification# E86006

All NELAP certified analysis are performed in accordance with Chapter 64E-1 Florida Administrative code, which has been determined to be equivalent to NELAC standards. Analysis certified by programs other than NELAP are designated with a "~".

Maria Castellanos - Lab Manager

Florida-Spectrum Environmental Services, Inc.

1460 W. McNab Road, Fort Lauderdale, FL 33309

Pembroke Laboratory

528 Gooch Rd.

Fort Mead, FL 33841

Big Lake Laboratory

610 Parrot Ave. N.

Okeechobee, FL 34972

Savannah Laboratory

108 Airport Park Dr.

Garden City, GA 31408 www.flenviro.com

Lakeland Laboratory

Appendix VIII Soil Boring Logs and

Soil Boring Location Photographs

BORING LOG

USCS

Symbol

SP

6"

12"

18"

24"

Depth (feet)

Hand AugerDrilling Method(s):

Dirt

Borehole Completion: Backfill and compacted with Concrete Asphalt Drill Cuttings

Disposition of Drill Cuttings: Backfill

Sample Type

Sample Depth

Interval (feet)

Sample Recovery (inches)

6"

24"

Ted Smith Pavement Thickness (inches):

Site Name:

Borehole Depth (feet):

Environmental Contractor: Environmental Technician’s

Borehole Start Date:

End Date:

Borehole Diameter (inches):

Tyndall AFB, Florida Geologist’s Name:

Drilling Company:

2" 2'AirQuest Environmental Inc. N/A

AirQuest Environmental Inc.

Direct Push

Moisture Content Codes: D = Dry; M = Moist; W = Wet; S = Saturated

Sample Description (include grain size based on USCS, odors, staining, and other remarks)

Sample Type Codes: PH = Post Hole; HA = Hand Auger; SS = Split Spoon; ST = Shelby Tube; DP = Direct Push; SC = Sonic Core; DC = Drill Cuttings

Sand, SP, dark gray, 10YR 4/1, fine-grained quartz, organic-stained, minor limerock gravel.

Moisture Content

Pavement Grass

Page 1 of

11/23/19 Borehole Start Time:

End Time:

Boring Number: Building # 179

Dark grey, N = 4, no gravel.

Slab

Soil Locations

Tyndall Air Force Base

AirQuest Environmental, Inc.

Soil Boring Location #1

Soil Boring Location #2

Soil Boring Location #3

Soil Boring Location #4

Appendix IX Soil Laboratory Report and

ANALYTICAL REPORT

Eurofins TestAmerica, Pensacola 3355 McLemore Drive Pensacola, FL 32514 Tel: (850)474-1001

Laboratory Job ID: 400-180394-1 Laboratory Sample Delivery Group: Building 179 Client Project/Site: Tyndall AFB Project No.15671

For:

Air Quest Environmental Inc 6851 SW 45th Street Fort Lauderdale, Florida 33314

Attn: Teresa A Thomas

Authorized for release by:

12/19/2019 2:29:57 PM

Mark Swafford, Project Manager I (850)471-6207 mark.swafford@testamericainc.com

The test results in this report meet all 2003 NELAC and 2009 TNI requirements for accredited parameters, exceptions are noted in this report. This report may not be reproduced except in full, and with written approval from the laboratory. For questions please contact the Project Manager at the e-mail address or telephone number listed on this page.

This report has been electronically signed and authorized by the signatory. Electronic signature is intended to be the legally binding equivalent of a traditionally handwritten signature.

Results relate only to the items tested and the sample(s) as received by the laboratory.

https://secure.testamericainc.com/TotalAccess/login.aspx http://www.testamericainc.com/services-we-offer/ask-the-expert http://www.testamericainc.com mailto:mark.swafford@testamericainc.com

Table of Contents

Client: Air Quest Environmental Inc Project/Site: Tyndall AFB Project No.15671

Laboratory Job ID: 400-180394-1 SDG: Building 179

Cover Page

Table of Contents

Case Narrative

Sample Summary

Client Sample Results

Lab Chronicle

Certification Summary

Method Summary

Definitions/Glossary

Chain of Custody

Receipt Checklists

Case Narrative Client: Air Quest Environmental Inc Job ID: 400-180394-1 Project/Site: Tyndall AFB Project No.15671 SDG: Building 179

Job ID: 400-180394-1

Laboratory: Eurofins TestAmerica, Pensacola

Narrative

Job Narrative 400-180394-1

Comments

No additional comments.

Receipt

The samples were received on 11/27/2019 9:20 AM; the samples arrived in good condition, properly preserved and, where required, on ice. The temperature of the cooler at receipt was 4.4º C.

GC Semi VOA Method 8081B: The continuing calibration verification (CCV) associated with batch 400-470201 recovered outside acceptance criteria, low biased, for Endrin ketone. A reporting limit (RL) standard was analyzed, and the target analyte was detected. Since the associated samples were non-detect for this analyte, the data have been reported.

Method 8081B: The following samples were diluted due to sample matrix, such as color, odor, appearance, viscosity: OCP.179.1 (400-180394-1) and OCP.179.5 (400-180394-5).