FDOT Building 4907 Auto Shop Attached Storage Shed Roof 5548 Northwest 9 th Avenue Fort Lauderdale, Florida

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DEMOLTION ASBESTOS SURVEY REPORT FDOT Building 4907 Auto Shop Attached Storage Shed Roof 5548 Northwest 9 th Avenue Fort Lauderdale, Florida GLE Project No.: 11000-11607 Prepared for: WRScompass 2400 Centrepark West Drive, Suite 125 West Palm Beach, Florida 33409 October 2011 Prepared by:

October 26, 2011 Mr. John Ciminelli WRScompass 2400 Centrepark West Drive, Suite 125 West Palm Beach, Florida 33409 RE: Demolition Asbestos Survey Report FDOT Building 4907 Auto Shop Attached Shed Roof Fort Lauderdale, Florida GLE Project No.: 11000-11607 Dear Mr. Ciminelli: GLE Associates, Inc. (GLE) performed a demolition survey for asbestos-containing materials (ACM) on October 24, 2011 at the FDOT Building 4907 Auto Shop Attached Shed Roof located in Fort Lauderdale, Florida. The survey was performed by Mr. Jeffrey Knight and Mr. Michael Love with GLE. This report outlines the sampling and testing procedures, and presents the results along with our conclusions and recommendations. GLE appreciates the opportunity to serve as your consultant on this project. If you should have any questions, or if we can be of further service, please do not hesitate to call. Sincerely, GLE Associates, Inc. Jeffrey C. Knight Robert B. Greene, PE, PG, CIH Environmental Scientist Asbestos Consultant, EA 0000009 JCK/MBC/RBG/ard D:\Work\ASB\11000\11607 WRS FDOT Bldg. 4907 ACM Roof Survey\Report\ACM Survey Report 11607.doc GLE Associates, Inc. 1000 NW 65 th Street Suite 100 Ft. Lauderdale, Florida 33309 954-968-6414 Fax 954-968-6090 www.gleassociates.com Tampa Ft. Lauderdale Orlando Gainesville Jacksonville Atlanta Nashville Architecture AA 0002369 Engineer EB 0005483 Asbestos ZA 0000034 Geology 0000297

TABLE OF CONTENTS 1.0 EXECUTIVE SUMMARY 1 1.1 Introduction 1 1.2 Facility Description 1 2.0 RESULTS 2 2.1 Asbestos Survey Procedures 2 2.2 Identified Suspect Asbestos-Containing Materials 3 Table 2.2-1 Summary of Homogeneous Sampling Areas 3.0 CONCLUSIONS AND RECOMMENDATIONS 5 3.1 General 5 3.2 Specific 5 4.0 LIMITATIONS AND CONDITIONS 6 APPENDICES Appendix A Analytical Results and Chain of Custody Appendix B Personnel and Laboratory Certifications Appendix C Photographs

1.1 INTRODUCTION 1.0 EXECUTIVE SUMMARY The purpose of this demolition survey was to identify accessible asbestos-containing materials (ACMs) and their general locations within the FDOT Building 4907 Auto Shop Attached Shed Roof, located at 5548 Northwest 9 th Avenue in Fort Lauderdale, Florida. The survey was conducted pursuant to National Emission Standards for Hazardous Air Pollutants (NESHAP, 40 CFR 61) requirements associated with the scheduled demolition plans. The survey was performed on October 24, 2011, by Jeffrey Knight and Mr. Michael Love, Environmental Protection Agency/Asbestos Hazard Emergency Response Act (EPA/AHERA) accredited inspectors. The scope of this survey did not include demolition of any building components, evaluation of architectural plans, or the quantification of materials for abatement purposes, or removal cost estimating. 1.2 FACILITY DESCRIPTION A summary of the facility investigated is outlined in the table below. A representative view of the FDOT Building 4907 Auto Shop Attached Shed Roof is shown in Appendix C. Facility Type: Storage Construction Date: Unknown Number of Floors: 1 Structural Foundation: Asphalt Wall Support: Wood Frame Exterior Finish: Paint Roof Support: Wood Frame Roof System Type: Rolled Roofing Mechanical/Plumbing HVAC Type: N/A Duct Type: N/A Pipe Insulation: N/A Interior Wall Substrate: Wood Wall Finishes: Paint Floor Substrate: Asphalt Floor Finishes: N/A Ceiling System: Wood Ceiling Finishes: N/A 1

2.0 RESULTS 2.1 ASBESTOS SURVEY PROCEDURES The demolition survey was performed by visually observing accessible areas of the building. EPA/AHERA accredited inspectors performed the visual observations (refer to Appendix B for personnel qualifications). After the overall visual survey was completed, representative sampling areas were determined. The surveyors delineated homogeneous areas of suspect materials and samples of each material were obtained in general compliance with regulations as established by the Occupational Safety and Health Administration (OSHA) and NESHAP. The field surveyors determined sample locations based on previous experience. Both friable and non-friable materials were sampled. A friable material is one that can be crushed when dry by normal hand pressure. This survey did not include the demolition of building components to access suspect material. After completion of the fieldwork, the samples were delivered to EMSL s National Voluntary Laboratory Accreditation Program (NVLAP) accredited laboratory for analysis. The samples were analyzed by Polarized Light Microscopy (PLM) coupled with dispersion staining, in general accordance with EPA-600/R-93/116. Utilizing this procedure, the various asbestos minerals (chrysotile, amosite, crocidolite, actinolite, tremolite, and anthophyllite) can be determined. The percentages of asbestos minerals in the samples were visually determined by the microscopist. Please note that the EPA designates all materials containing greater than 1% asbestos as an asbestos-containing material. Regulated Asbestos-Containing Material (RACM) is defined as (a) Friable asbestos materials, (b) Category I non-friable ACM that has become friable, (c) Category I non-friable ACM that will be or has been subjected to sanding, grinding, cutting, or abrading, or (d) Category II nonfriable ACM that has a high probability of becoming or has become crumbled, pulverized, or reduced to powder by the forces expected to act on the material in the course of demolition or renovation operations regulated by this subpart. Category I and Category II non-friable ACM, as defined by the EPA: Category I non-friable ACM means asbestos containing packings, gaskets, resilient floor covering, and asphalt roofing products containing more than 1 percent asbestos and determined using the method specified in Appendix E, Subpart E, 40 CFR Part 763, Section 1, PLM. Category II non-friable ACM means any material, excluding Category I non-friable ACM, containing more than 1 percent asbestos as determined using the methods specified in Appendix E, Subpart E, 40 CFR Part 763 Section 1, PLM that, when dry, cannot be crumbled, pulverized, or reduced to powder by hand pressure. 2

2.2 IDENTIFIED SUSPECT ASBESTOS-CONTAINING MATERIALS A total of 12 samples of suspect building materials were collected from the facility during the survey, representing 4 different homogeneous areas. The results of the laboratory analyses are included in Appendix A and photographs of the various materials sampled are included in Appendix C. A summary of the homogenous sampling areas of suspect ACM determined to be present is outlined in the following table: 3

HA # HOMOGENEOUS MATERIAL DESCRIPTION TABLE 2.2-1: SUMMARY OF HOMOGENEOUS SAMPLING AREAS FDOT BUILDING 4907 AUTO SHOP ATTACHED SHED ROOF HOMOGENEOUS MATERIAL LOCATION FRIABILITY (F /NF) % ASBESTOS* # OF SAMPLES COLLECTED APPROXIMATE QUANTITY ACM CATEGORY RBU-01 Built-Up Rolled Roof Roof NF ND 3 N/A N/A RF-01 Edge Flashing Roof NF ND 3 N/A N/A RF-02 Roof Pitch On Wall Roof NF 10-15% Chrysotile 3 66 LF CAT I M-01 White Caulk Bay Doors NF ND 3 N/A N/A * = The facility owner has the option of point-counting by polarized light microscopy (PLM) those RACM whose asbestos content is less than 10% ASBESTOS CONTENT in order to more accurately determine the asbestos content therein. Expressed as percent PC = Results based on Point-Count analysis FRIABILITY F = Friable Material NF = Non-Friable Material CATEGORY OF MATERIAL RACM = Regulated ACM CAT I = Category I non-friable ACM CAT II = Category II non-friable ACM ABBREVIATIONS: NA = Not Applicable ND = None Detected NIS = Not in Scope HA = Homogeneous Area SF = Square Feet LF = Linear Feet CF = Cubic Feet 4

3.1 GENERAL 3.0 CONCLUSIONS AND RECOMMENDATIONS The EPA, OSHA and the State of Florida have promulgated regulations dealing with asbestos. For commercial building owners, the EPA NESHAP (40 CFR 61) regulations require removal of RACM prior to conducting activities which might disturb the material. They also deal with notification, handling and disposal of asbestos. For facilities not scheduled for demolition or complete removal of all ACM, the EPA recommends that an Operations and Maintenance (O&M) Program be developed for any facilities with ACM, and this Program should address all ACM (known and/or assumed) present. The O&M Program establishes notification and training requirements along with special procedures for working around the asbestos. The O&M Program would remain in effect until all asbestos is removed. Category I and Category II non-friable materials, as defined by the EPA, may remain within a facility during demolition with no potential cessation of work provided they remain non-friable and the appropriate engineering controls (i.e., wet methods) are utilized, with the resulting waste disposed of as asbestos-containing waste. However, there is no guarantee that these materials will remain non-friable. If the materials become friable, then they are classified as RACM. RACM, as defined by the EPA, must be removed prior to renovation or demolition activities that may disturb the materials. The OSHA regulations deal with employee exposure to airborne asbestos fibers. The regulations restrict employee exposure, and require special monitoring, training and handling procedures when dealing with asbestos. Additionally, OSHA has regulations that may supersede the EPA regulations. In order to protect the worker, OSHA has established a permissible exposure limit (PEL), which limits employee exposure to airborne fiber concentrations. OSHA requires objective evidence that the PEL will not be exceeded, as justification that personal air monitoring and engineering controls will not be required. OSHA has also established rules requiring the containerization and labeling of asbestos waste. The State regulations require that anyone involved in asbestos consulting activities be a licensed asbestos consultant and that anyone involved in asbestos abatement, with the exception of roofing materials, be a licensed asbestos abatement contractor. 3.2 SPECIFIC Roof Pitch on Wall This material may remain within a facility during demolition with no potential stoppage of work provided it remains non-friable. However, there is no guarantee that it will remain non-friable. If a material becomes friable, then it is classified as RACM. RACM, as defined by the EPA, must be removed prior to renovation or demolition activities that may disturb the materials. Also, OSHA has additional requirements that may supersede the EPA rules. 5

As discussed above, in order to protect the worker, OSHA has established a PEL which limits airborne fiber concentrations. Objective evidence that the PEL will not be exceeded is required by OSHA as justification that personal air monitoring and engineering controls will not be required. OSHA has also established rules requiring the containerization and labeling of asbestos waste. Should prior abatement be desired, the work must be performed in accordance with Federal, State, and local regulations. In lieu of abatement, demolition utilizing the wet method is acceptable. 4.0 LIMITATIONS AND CONDITIONS As a result of previous renovations, there may be hidden materials, such as floor tile, sheet vinyl flooring, etc. These materials may be found in various areas hidden under existing flooring materials. Any materials found during construction activities, either not addressed in this survey report, or similar to the ACM identified in this survey report should be assumed to be ACM until sampling and analysis documents otherwise. The Florida Department of Environmental Protection (FDEP) has recently issued an interpretation regarding the testing of concrete flooring, walls and roofing materials, which states that if concrete will be recycled or reused, the concrete must be sampled and analyzed for the presence of asbestos prior to the commencement of activities that may release asbestos fibers into the environment, and that all of the different layers or types of concrete in a sample must be analyzed, individually, using the method specified in Appendix E, subpart E, 40 CFR Part 763, Section 1, Polarized Light Microscopy, with point-counting, as applicable. Under the presumption that the Client will not be reusing/recycling the concrete, this additional sampling and analysis of concrete is not included with our scope of work. However, if requested by the Client, GLE will perform this work as an additional service. Because of the hidden nature of many building components (i.e. within mechanical chases), it may be impossible to determine if all of the suspect building materials have been located and subsequently tested. Destructive testing in some instances is not a viable option. We cannot, therefore, guarantee that all potential ACM has been located. For the same reasons, estimates of quantities and/or conditions are subject to readily apparent situations, and our findings reflect this condition. We do warrant, however, that the investigations and methodology reflect our best efforts based upon the prevailing standard of care in the environmental industry. The information contained in this report was prepared based upon specific parameters and regulations in force at the time of this report. The information herein is only for the specific use of the client and GLE. GLE accepts no responsibility for the use, interpretation, or reliance by other parties on the information contained herein, unless prior written authorization has been obtained from GLE. 6

APPENDIX A Analytical Results and Chain of Custody

EMSL Analytical, Inc. 19501 NE 10th Ave. Bay A, N. Miami Beach, FL 33179 Phone: (305) 650-0577 Fax: (305) 650-0578 Email: miamilab@emsl.com Attn: Rafe Padgett GLE Associates, Inc. 1000 NW 65th Street Suite 100 Fort Lauderdale, FL 33309 Customer ID: Customer PO: Received: EMSL Order: GLEA51G 10/24/11 1:00 PM 171105758 Fax: (954) 968-6090 Phone: (954) 968-6414 Project: DOT Building 4607 11000-11607 EMSL Proj: Analysis Date: 10/25/2011 Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % Non-Fibrous % Type RBV-01A 171105758-0001 Rolled Built-Up Roof White/Black Non-Fibrous Heterogeneous 2% Cellulose 98% Non-fibrous (other) None Detected RBV-01B 171105758-0002 Rolled Built-Up Roof White/Black Non-Fibrous Heterogeneous 2% Cellulose 98% Non-fibrous (other) None Detected RBV-01C 171105758-0003 Rolled Built-Up Roof Black Fibrous Heterogeneous 15% Cellulose 85% Non-fibrous (other) None Detected RF-01A 171105758-0004 RF-01B 171105758-0005 RF-01C 171105758-0006 Edge Flashing Gray/Black 3% Cellulose 92% Non-fibrous (other) None Detected Fibrous Heterogeneous 5% Synthetic Edge Flashing Gray/Black 3% Cellulose 94% Non-fibrous (other) None Detected Fibrous Heterogeneous 3% Synthetic Edge Flashing Black 30% Cellulose 70% Non-fibrous (other) None Detected Fibrous Heterogeneous <1% Synthetic Initial report from 10/25/2011 08:59:12 Analyst(s) Edgar Rodriguez (4) Natasha Montoya (8) Kimberly Wallace, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported 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. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Samples analyzed by EMSL Analytical, Inc. N. Miami Beach, FL NVLAP Lab Code 200204-0 Test Report PLM-7.23.0 Printed: 10/25/2011 8:59:12 AM 1

EMSL Analytical, Inc. 19501 NE 10th Ave. Bay A, N. Miami Beach, FL 33179 Phone: (305) 650-0577 Fax: (305) 650-0578 Email: miamilab@emsl.com Attn: Rafe Padgett GLE Associates, Inc. 1000 NW 65th Street Suite 100 Fort Lauderdale, FL 33309 Customer ID: Customer PO: Received: EMSL Order: GLEA51G 10/24/11 1:00 PM 171105758 Fax: (954) 968-6090 Phone: (954) 968-6414 Project: DOT Building 4607 11000-11607 EMSL Proj: Analysis Date: 10/25/2011 Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % Non-Fibrous % Type RF-02A Roof Pitch on Wall Black 85% Non-fibrous (other) 15% Chrysotile 171105758-0007 Non-Fibrous Homogeneous RF-02B Roof Pitch on Wall Black 85% Non-fibrous (other) 15% Chrysotile 171105758-0008 Non-Fibrous Homogeneous RF-02C Roof Pitch on Wall Black <1% Cellulose 90% Non-fibrous (other) 10% Chrysotile 171105758-0009 Non-Fibrous Heterogeneous M-01A 171105758-0010 M-01B 171105758-0011 M-01C 171105758-0012 Caulk White 10% Wollastonite 90% Non-fibrous (other) None Detected Non-Fibrous Homogeneous Caulk White 10% Wollastonite 90% Non-fibrous (other) None Detected Non-Fibrous Homogeneous Caulk White 100% Non-fibrous (other) None Detected Non-Fibrous Homogeneous Initial report from 10/25/2011 08:59:12 Analyst(s) Edgar Rodriguez (4) Natasha Montoya (8) Kimberly Wallace, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported 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. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Samples analyzed by EMSL Analytical, Inc. N. Miami Beach, FL NVLAP Lab Code 200204-0 Test Report PLM-7.23.0 Printed: 10/25/2011 8:59:12 AM THIS IS THE LAST PAGE OF THE REPORT. 2

APPENDIX B Personnel and Laboratory Certifications

APPENDIX C Photographs

Upper Photo: Front View Sheds Lower Photo: View of Roof Photograph Date: October 24, 2011 Prepared By: GLE Associates, Inc. 1000 NW 65 th Street Suite #100 Fort Lauderdale, FL 33309 Drawn JCK Checked MBC Date 10/24/2011 Building 4907 Job # 11000-11607 Figure C-1

Upper Photo: RBU-01: Built Up Rolled Roof Lower Photo: RF-01: Edge Flashing on Roof Photograph Date: October 24, 2011 Prepared By: GLE Associates, Inc. 1000 NW 65 th Street Suite #100 Fort Lauderdale, FL 33309 Drawn JCK Checked MBC Date 10/24/2011 Building 4907 Job # 11000-11607 Figure C-2

Upper Photo: RF-02: Roof Pitch on Wall Lower Photo: M-01: White Caulk on Bay Door Photograph Date: October 24, 2011 Prepared By: GLE Associates, Inc. 1000 NW 65 th Street Suite #100 Fort Lauderdale, FL 33309 Drawn JCK Checked MBC Date 10/24/2011 Building 4907 Job # 11000-11607 Figure C-3