Atch 7 - Hazardous Materials Survey Report_MUHJ 24-4024 Repair MWD Kennel Interior Facility 1030.pdf
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This document is a Hazardous Materials Survey Report for the MUHJ 24-4024 JBLE Facility 1030 Military Working Dog Kennels located at 1030 Worley Road in Hampton, Virginia. Prepared by ECS Mid-Atlantic, LLC on November 22, 2024, the survey assessed asbestos-containing materials (ACMs), lead paint, and mold in the facility. Laboratory analysis of 40 bulk samples found no asbestos in the sampled materials. However, XRF lead paint screening detected lead concentrations on metal pipes, an air compressor unit, exterior metal doors, window sills, and gutters. The survey also identified visible mold and moisture damage on the drywall ceilings in the central kennel room.
The report recommends removing and replacing the moisture-impacted drywall ceilings in the central kennel room, including any insulation directly above the affected area. A qualified mold/moisture remediation contractor should perform the work using proper containment and HEPA air scrubbers. The report advises identifying and correcting moisture intrusion sources concurrently with remediation. For lead-containing painted surfaces, the contractor must follow OSHA Lead in Construction standards, including environmental and personnel monitoring to ensure exposure remains below the Permissible Exposure Limit of 50 micrograms per cubic millimeter as an 8-hour Time Weighted Average.
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HAZARDOUS MATERIALS SURVEY REPORT
MUHJ 24-4024 JBLE FACILITY 1030 - REPAIR MILITARY WORKING DOG
KENNELS
1030 WORLEY RD
HAMPTON, VIRGINIA 23665
ECS PROJECT NO. 47:19897
FOR: VANSANT & GUSLER, INC.
NOVEMBER 22, 2024
November 22, 2024
Mr. Tad Sellers, P.E.
President, Electrical Department Manager Vansant & Gusler, Inc.
6330 Newtown Road Suite 400 Norfolk, Virginia 23502
ECS Project No. 47:19897
Reference: Hazardous Materials Survey, MUHJ 24-4024 JBLE Facility 1030 - Repair Military Working Dog Kennels, 1030 Worley Rd, Hampton, Virginia
Dear Mr. Sellers:
ECS Mid-Atlantic, LLC (ECS) is pleased to provide Vansant & Gusler, Inc. with the results of the above referenced Hazardous Materials Survey performed for the MUHJ 24-4024 JBLE Facility 1030 - Repair Military Working Dog Kennels renovation project located at 1030 Worley Rd in Hampton, Virginia. This report summarizes our observations, analytical results, findings, and recommendations related to the work performed. The work described in this report was performed by ECS in general accordance with the Scope of Services described in ECS Proposal Number 47:35638-EP and the terms and conditions of the agreement authorizing those services.
ECS appreciates this opportunity to provide Vansant & Gusler, Inc. with our services. If we can be of further assistance to you, please do not hesitate to contact us.
Sincerely, ECS Mid-Atlantic, LLC
Shawn Cowden Nemanja Zivadinovic, CSP Environmental Project Manager Associate Principal scowden@ecslimited.com nzivadinovic@ecslimited.com 757-229-6677 757-229-6677
1643 Merrimac Trail, Williamsburg, Virginia 23185 • T:757-366-5100 ECS Florida, LLC • ECS Mid-Atlantic LLC • ECS Midwest, LLC • ECS Pacific, Inc. • ECS Southeast, LLC • ECS Southwest, LLP
ECS New York Engineering, PLLC - An Associate of ECS Group of Companies • ecslimited.com
"ONE FIRM. ONE MISSION."
EXECUTIVE SUMMARY
The property is developed with a one-story building located at 1030 Worley Rd at Langley Air Force Base in Hampton, Virginia.
The purpose of this Hazardous Materials Survey was to evaluate if asbestos-containing materials (ACMs), lead paint, and mold may be present within readily accessible areas of the subject building. No other areas of the property were assessed.
Based on the laboratory analysis of the bulk samples collected during the survey, asbestos was not identified in the sampled materials.
Painted and/or glazed surfaces were assessed for lead content using a Direct-Read X-ray fluorescence (XRF) Spectrometer. Detectable concentrations of lead were identified in the paint on the following components:
• Metal pipes
• Metal air compressor unit
• Exterior metal doors
• Exterior metal window sills
• Exterior metal gutters
Visible mold/moisture impact was identified on the drywall ceilings in the central kennel room.
The executive summary is an integral portion of this report; however, ECS recommends reading the report in its entirety. The executive summary is not intended to replace the overall findings/ recommendations discussed in the full report. The findings discussed in this executive summary should only be viewed within the full context of the report.
ii
PAGETABLE OF CONTENTS
1.0 SITE DESCRIPTION
2.0 PURPOSE
3.0 METHODOLOGY
3.1 Asbestos-Containing Materials
3.2 Lead in Paint and Surface Coatings
3.3 Mold and Moisture
4.0 RESULTS
4.1 Asbestos Sampling
4.2 Suspect or Assumed Asbestos-Containing Materials
4.3 Lead in Paint and Surface Coatings
4.4 Mold and Moisture
5.0 RECOMMENDATIONS AND REGULATORY REQUIREMENTS
5.1 Asbestos-Containing Materials
5.2 Lead in Paint and Surface Coatings
5.3 Mold and Moisture
6.0 LIMITATIONS
iii
TABLE OF APPENDICES
Appendix I: Approximate Location of Moisture-Impacted Materials
Appendix II: Representative Photographs of Sampled Materials for Asbestos - Asbestos Not Detected
Appendix III: Representative Photographs of Identified Lead Paint
Appendix IV: Representative Photographs of Identified Moisture-Impacted Materials
Appendix V: Asbestos Bulk Sample Results Summary
Appendix VI: XRF Lead Paint Readings
Appendix VII: Laboratory Report
Appendix VIII: Certifications/Licenses
Appendix IX: Mold Reference and Guidance Documents iv
1.0 SITE DESCRIPTION
The property is developed with a one-story building located at 1030 Worley Rd at Langley Air Force Base in Hampton, Virginia.
2.0 PURPOSE
The purpose of this Hazardous Materials Survey was to evaluate if asbestos-containing materials (ACMs), lead paint, and mold may be present within readily accessible areas of the subject building. No other areas of the property were assessed.
3.0 METHODOLOGY
ECS performed the authorized Scope of Services in general accordance with our proposal, standard industry practice(s) and methods specified by regulation(s) for the identification of Asbestos-Containing Materials (ACMs), lead paint, and mold and moisture-impacted areas.
3.1 Asbestos-Containing Materials
The non-destructive/non-invasive asbestos survey was performed by an asbestos inspector who has received EPA-accredited training and is appropriately licensed in the Commonwealth of Virginia.
Samples of suspect ACMs were collected utilizing hand tools and placed into individual, labeled plastic bags. Unique bulk suspect ACM samples were submitted to Environmental Hazards Services, LLC in Richmond, Virginia for analysis via Polarized Light Microscopy (PLM) in accordance with current EPA-600 methodology. Materials consisting of additional layers were analyzed separately.
Environmental Hazards Services, LLC is listed as an accredited laboratory by the National Voluntary Laboratory Accreditation Plan (NVLAP) managed by the National Institute of Standards and Technology (NIST) for bulk sample analysis by currently approved EPA methodology by PLM.
During the survey, ECS attempted to identify suspect ACMs in readily accessible areas. However, due to the destructive means required to identify some materials, certain areas were deemed inaccessible (i.e. behind walls or sub grade materials) and were not surveyed for suspect ACMs. Unidentified suspect ACMs may be located in these areas and/or other inaccessible areas.
Samples were collected in general accordance with EPA Standard 40 CFR 763 Subpart E, Asbestos Hazard Emergency Response Act (AHERA) and OSHA Standard 29 CFR 1926.1101 Inspection Protocol.
Multiple samples of each unique material were submitted.
3.2 Lead in Paint and Surface Coatings
The lead paint screening was performed by a Virginia-licensed lead risk assessor using an X-ray fluorescence (XRF) Spectrometer to identify lead concentrations in painted and glazed surfaces. Paints with concentrations of lead detectable by the XRF are considered lead-containing paints. Activities that disturb lead-containing paints are regulated by OSHA (29 CFR 1926.62).
Because the current or proposed use of the property is not residential or child-occupied, the scope of the limited lead paint testing was not conducted in accordance with HUD Chapter 7 requirements.
This limited testing included taking readings from selected representative surfaces. The results of the
November 22, 2024
ECS Project # 47:19897 testing identify the concentration of lead within the painted surfaces tested and provide data to assist in determining appropriate work practices and worker protection during the renovation activities in accordance with the OSHA Lead-in-Construction Standard.
Test locations were listed by letters with side “A” being the east of the building, proceeding clockwise to “B, C, and D”.
3.3 Mold and Moisture
ECS performed a non-invasive visual assessment for mold/moisture in the building's interior. No testing or sampling was performed as part of this process. A reasonable effort was made to identify visible indicators of water damage and/or visible mold growth; however, this does not guarantee that all possible reservoirs (growth or airborne) of mold growth have been ruled out, as mold or water-impacted building materials may be hidden behind solid walls, ceilings, partitions, and other objects.
4.0 RESULTS
The following is a summary of laboratory results, findings and observations.
4.1 Asbestos Sampling
A total of 40 bulk samples were submitted to the laboratory, of which 58 layers were analyzed.
Samples of the following materials were collected for laboratory analysis: 12" vinyl floor tiles and mastic, vinyl cove base and adhesive, concrete masonry unit (CMU) paint/filler, drywall and joint compound, window frame caulk (interior), ceiling texturing and EIFS, pipe flange gaskets, sealants at threaded pipe fittings, soffit/attic wall texturing and EIFS, door frame caulk, brick joint caulk, window frame caulk (exterior), red penetration caulk, mastic on fiberglass pipe insulation, cementitious panel board, roof shingles and felt, and flashing at room seam.
Based on the laboratory analysis of the bulk samples collected during the survey, asbestos was not identified in the sampled materials.
Asbestos-Containing Materials (ACMs) are defined as any material containing more than one percent (>1%) asbestos as determined using the method specified in Appendix A, Subpart F, 40 CFR Part 763, Section 1, PLM. A list of materials sampled and submitted for analysis, the associated chain of custody, and the reported analytical results can be found in the Appendices of this report. Representative photographs of these materials are also provided in the Appendices.
November 22, 2024
4.2 Suspect or Assumed Asbestos-Containing Materials
Due to the inaccessibility or the destructive means that asbestos sampling requires, additional suspect ACMs may remain within areas of the four buildings, hidden behind inaccessible areas that include, but are not limited to, sub-grade walls, structural members, topping slabs, sub-grade sealants, flooring located below underlayments, areas behind solid walls/ceilings, pipe trenches, and subsurface utilities, etc. These areas were deemed inaccessible and were not assessed.
If these or any other materials not previously sampled are discovered during construction activities, they should be presumed to contain asbestos and be treated as ACMs or be sampled immediately upon discovery and prior to disturbance for asbestos content by a licensed asbestos inspector in accordance with 29 CFR 1926.1101.
Based upon our past experience in the identification of ACMs in similarly constructed buildings, the following suspect ACMs may also be located in inaccessible areas of the buildings:
• Vapor barriers/waterproofing/insulation within the exterior walls and below concrete slabs on grade
• Electrical components inside electrical panels/boxes
• Pipe insulation concealed behind solid walls/ceilings
• Fire doors
4.3 Lead in Paint and Surface Coatings
Paint and surface coatings that contain detectable concentrations of lead are considered “lead-containing paints”. Since OSHA has no specific action level for lead in paint, all paint on the site found to have a measurable concentration of lead should be assumed to be lead containing. Work performed that may disturb lead-containing paint is regulated under OSHA as referenced under 29
CFR 1926.62.
A total of 67 readings were collected during the survey, including calibration readings. Paint in which detectable concentrations of lead were identified during the screening survey is summarized in the table below, and representative photographs of these materials can be found in the Appendices.
Summary of Identified Lead Paint
Location Substrate Component Color
Throughout Metal Pipes Red
East Kennel Room Metal Air compressor Blue
Exterior Metal Doors Burgundy
Exterior Metal Window sills Black
Exterior Metal Gutters Burgundy
November 22, 2024
Any similar paint located on the property should be assumed to contain lead, regardless of color, unless determined otherwise by appropriate testing.
4.4 Mold and Moisture
ECS performed a visual survey of the building's interior for suspected mold/moisture-impacted materials on October 18, 2024.
The drywall ceilings in the central kennel room showed visible moisture and suspected mold impact.
Photographs of the observed mold/moisture-impacted drywall are attached in the Appendices. A sketch indicating the approximate area in which moisture-impacted ceilings were observed is also attached in the Appendices.
5.0 RECOMMENDATIONS AND REGULATORY REQUIREMENTS
Based on our understanding of the purpose of the Hazardous Materials Survey, the results of laboratory analysis, and our findings and observations, ECS presents the following recommendations.
Note: Additional requirements regarding the disturbance of paint with lead and mold/ moisture-impacted materials identified within the building will be provided in the project specifications as separate documents.
5.1 Asbestos-Containing Materials
None of the bulk samples submitted to Environmental Hazards Services, LLC were reported to contain detectable concentrations of asbestos. If additional suspect asbestos-containing materials are uncovered that were not accessible or sampled during this sampling event, it is recommended that these materials be sampled or tested immediately upon discovery for asbestos content by an asbestos inspector in accordance with 29 CFR 1926.1101.
5.2 Lead in Paint and Surface Coatings
Based on the findings of the limited lead paint survey, detectable concentrations of lead were identified on some painted surfaces.
The presence of lead is a concern primarily when conditions exist where it may be inhaled or ingested. The OSHA standard gives no guidance on acceptable lead levels in paint at which no exposure to airborne lead (above the action level) would be expected. Rather, OSHA defines airborne concentrations and references specific types of work practices and operations from which a lead hazard may be generated (reference 29 CFR 1926.62, section d). Due to the presence of paint with lead, environmental and personnel monitoring should be conducted during any removal/demolition process (as appropriate) to verify that actual personal exposures are below the Permissible Exposure Limit (PEL) of 50 micrograms per cubic millimeter (μg/m3) as an 8-hour Time Weighted Average (TWA).
Under OSHA Lead in Construction requirements, the contractor performing demolition/renovation work (or any other personnel) will be required to conduct this monitoring and follow applicable requirements under 29 CFR 1926.62 when disturbing painted surfaces.
November 22, 2024
5.3 Mold and Moisture
Based on our understanding of the purpose of the non-invasive visual assessment for mold/moisture and our observations, ECS recommends the following response actions be performed:
• Removal and replacement of the identified mold/moisture-impacted drywall ceilings in the central kennel room. Any materials encountered directly above the mold/moisture-impacted ceiling (if any), such as insulation, should also be removed as part of the remediation process. After the removal of the moisture-impacted drywall, the surrounding ceiling cavity (e.g., wood framing, sheathing, etc.) should be inspected, dried, and cleaned as necessary.
• Throughout the course of remediation activities, it is recommended that a containment be utilized to isolate the work area and that HEPA air scrubbers be utilized to purify the air within the work area and within the building.
General
ECS recommends the remediation activities indicated in this report be performed by a qualified mold/ moisture remediation contractor.
It is recommended that a qualified contractor/engineer/architect identify and correct all sources of moisture intrusion within the building concurrently with mold/moisture remediation activities or sooner. It is ECS' understanding that the moisture intrusion issues will be addressed during the upcoming renovation project.
In general accordance with the EPA and OSHA guidelines, ECS recommends utilizing a containment during the remediation activities. The containment should be constructed using plastic barriers and tape to create negative air pressure inside the containment during the removal of mold/ moisture-impacted materials. The contractor should seal HVAC vents in the work area(s), as well as all penetrations and openings. The pressure differential in the containment should be -0.02 inches of water gauge between the outside and inside of the containment. HEPA-filtered local exhaust ventilation (negative air machine) should be utilized directly adjacent to the area(s) being removed/cleaned and should maintain negative pressure and HEPA filtration continuously inside the containment during remediation activities and prior to post-remediation assessment. The filtered air from containment should be exhausted outside the buildings using flexible tubing. All of the HVAC systems within the containment should be turned off for the duration of the remediation effort.
ECS recommends that post-remediation assessment be performed following the completion of the remediation efforts.
Note: The purpose of this evaluation was to evaluate areas where visible or apparent mold growth and/or moisture intrusion has occurred and provide findings and recommendations for remedial work efforts. Identification and recommendation(s) for correction of moisture intrusion concerns were outside of the scope of services for this work.
November 22, 2024
6.0 LIMITATIONS
The conclusions and recommendations presented within this report are based upon a reasonable level of assessment within normal bounds and standards of professional practice for a site in this particular geographic setting. ECS is not responsible or liable for the discovery and elimination of hazards that may potentially cause damage, accidents, or injuries.
The observations, conclusions, and recommendations pertaining to environmental conditions at the subject site are necessarily limited to conditions observed, and/or materials reviewed at the time this study was undertaken. No warranty, expressed or implied, is made with regard to the conclusions and recommendations presented within this report. This report is provided for the exclusive use of the client. This report is not intended to be used or relied upon in connection with other projects or by other unidentified third parties without the written consent of ECS and the client.
During this study, samples were submitted for analysis at an accredited laboratory via polarized light microscopy. As with any similar survey of this nature, actual conditions exist only at the precise locations from which samples were collected. Certain inferences are based on the results of this sampling and related testing to form a professional opinion of conditions in areas beyond those from which the samples were collected. No warranty, expressed or implied, is made.
This survey is not intended to represent an exhaustive research of every potential hazard or condition that may exist, nor does it claim to represent indoor conditions or events that arise after the survey.
This report has been prepared in accordance with generally accepted environmental practices. Our conclusions and findings are based, in part, upon information provided to us by others and our site observations. We have not verified the completeness or accuracy of the information provided by others. The scope of services performed was limited to those requested by the Client and does not constitute a full microbial assessment of the site or a comprehensive moisture survey of the site. The data provided in this study is only indicative of conditions sampled at the immediate time of the study. The work performed in conjunction with this assessment and the data developed is intended as a description of available information at the dates and locations given. This report does not warrant against future operations or conditions, nor does it warrant against extant, or future, conditions of a type or at a location not investigated. The reported microbial levels (if any) are only reflective of conditions at the time of the site visit. Microbial populations can vary over time, depending upon a number of conditions, including environmental factors (i.e., temperature and relative humidity). The work performed in conjunction with this assessment and the data developed is intended as a description of available information at the dates and locations given.
Our recommendations are in part based on federal, state, and local regulations and guidelines. ECS does not assume the responsibility of the person(s) in charge of the site, or otherwise undertake responsibility for reporting to any local, state, or federal public agencies, any conditions at the site that may present a potential danger to public health, safety, or the environment. Under this scope of services, ECS assumes no responsibility regarding any response actions initiated as a result of these findings. General compliance with regulations and response actions are the sole responsibility of the Client and should be conducted in accordance with local, state, and/or federal requirements.
November 22, 2024
Appendix I: Approximate Location of Moisture-Impacted
Materials
MUHJ 24-4024; Repair Military Working Dog Kennels, 633/SFS, Facility 1030
Central Kennel Room
East Kennel Room
Observed moisture damage on drywall ceilings
SCowden Rectangle
SCowden Line
Appendix II: Representative Photographs of Sampled Materials for Asbestos - Asbestos Not Detected
1 - 12 inch vinyl floor tiles and mastic
2 - Vinyl base cove and adhesive
ECS Project No. 47:19897
3 - CMU paint
4 - Drywall and associated joint compound
5 - Window frame caulk - interior
6 - Ceiling texturing and EIFS
7 - Pipe flange gaskets
8 - Sealants at threaded pipe fittings
9 - Soffit wall texturing and EIFS
10 - Door frame caulk
11 - Brick joint caulk
12 - Window frame caulk - exterior
13 - Cementitious exterior panel board
14 - Red penetration caulk
15 - Mastic on fiberglass pipe insulation
16 - Roof shingles and felt
17 - Flashing sealants
Appendix III: Representative Photographs of Identified Lead
Paint
1 - Lead paint - metal pipes
2 - Lead paint - air compressor unit
3 - Lead paint - exterior metal doors
4 - Lead paint - exterior metal window sills
5 - Lead paint - metal gutters
Appendix IV: Representative Photographs of Identified
Moisture-Impacted Materials
1 - Moisture-impacted drywall ceiling - central kennel room
2 - Moisture-impacted drywall ceiling - central kennel room
Appendix V: Asbestos Bulk Sample Results Summary
Asbestos Bulk Sample Analysis Results Summary
JBLE Facility 1030 Hampton, Virginia
Sample ID Collection Location Layer Type Sample Description Asbestos 1-1 HALL CLOSET Tile 12" vinyl floor tiles and mastic NAD
1-1 HALL CLOSET Mastic 12" vinyl floor tiles and mastic NAD
1-2 HALLWAY, WEST Mastic 12" vinyl floor tiles and mastic NAD
1-2 HALLWAY, WEST Tile 12" vinyl floor tiles and mastic NAD
2-1 HALL CLOSET Cove Base Vinyl cove base and adhesive NAD
2-1 HALL CLOSET Mastic Vinyl cove base and adhesive NAD
2-2 TAC ROOM Cove Base Vinyl cove base and adhesive NAD
2-2 TAC ROOM Mastic Vinyl cove base and adhesive NAD
3-1 HALL CLOSET CMU paint/filler NAD
3-2 BREAK ROOM CMU paint/filler NAD
3-3 EAST KENNELS CMU paint/filler NAD
4-1 RESTROOM Texture Drywall and joint compound NAD
4-1 RESTROOM Joint Comp. Drywall and joint compound NAD
4-1 RESTROOM Drywall Drywall and joint compound NAD
4-2 BREAK ROOM Joint Comp. Drywall and joint compound NAD
4-2 BREAK ROOM Drywall Drywall and joint compound NAD
4-3 HALLWAY, NORTH Joint Comp. Drywall and joint compound NAD
4-3 HALLWAY, NORTH Drywall Drywall and joint compound NAD
4-4 TAC ROOM Joint Comp. Drywall and joint compound NAD
NAD - No Asbestos Detected
JBLE Facility 1030 Hampton, Virginia
Sample ID Collection Location Layer Type Sample Description Asbestos 4-4 TAC ROOM Drywall Drywall and joint compound NAD
4-5 HALLWAY, WEST Joint Comp. Drywall and joint compound NAD
4-5 HALLWAY, WEST Drywall Drywall and joint compound NAD
5-1 KITCHEN Window frame caulk (interior) NAD
5-2 EAST KENNELS Window frame caulk (interior) NAD
6-1 HALL, NORTH Other * Ceiling texturing and EIFS NAD
6-1 HALL, NORTH Other * Ceiling texturing and EIFS NAD
6-2 HALL, NORTH Other * Ceiling texturing and EIFS NAD
6-2 HALL, NORTH Other * Ceiling texturing and EIFS NAD
6-3 HALL, NORTH Other * Ceiling texturing and EIFS NAD
6-3 HALL, NORTH Other * Ceiling texturing and EIFS NAD
7-1 EAST KENNELS Pipe flange gasket NAD
7-2 EAST KENNELS Pipe flange gasket NAD
8-1 TAC ROOM Sealants at threaded pipe fittings NAD
8-2 TAC ROOM Sealants at threaded pipe fittings NAD
9-1 EXTERIOR Other * Soffit/attic wall texturing and EIFS NAD
9-1 EXTERIOR Other * Soffit/attic wall texturing and EIFS NAD
9-2 EXTERIOR Other * Soffit/attic wall texturing and EIFS NAD
9-2 EXTERIOR Other * Soffit/attic wall texturing and EIFS NAD
JBLE Facility 1030 Hampton, Virginia
Sample ID Collection Location Layer Type Sample Description Asbestos 9-3 EXTERIOR Other * Soffit/attic wall texturing and EIFS NAD
9-3 EXTERIOR Other * Soffit/attic wall texturing and EIFS NAD
10-1 EXTERIOR Door frame caulk NAD
10-2 EXTERIOR Door frame caulk NAD
11-1 EXTERIOR Brick joint caulk NAD
11-2 EXTERIOR Brick joint caulk NAD
12-1 EXTERIOR Window frame caulk NAD
12-2 EXTERIOR Window frame caulk NAD
13-1 EXTERIOR UTILITY CLOSET Red penetration caulk NAD
13-2 EXTERIOR UTILITY CLOSET Red penetration caulk NAD
14-1 EXTERIOR UTILITY CLOSET Mastic on fiberglass pipe insulation NAD
14-1 EXTERIOR UTILITY CLOSET Mastic on fiberglass pipe insulation NAD
14-2 EXTERIOR UTILITY CLOSET Mastic on fiberglass pipe insulation NAD
15-1 EXTERIOR Cementitious panel board NAD
15-2 EXTERIOR Cementitious panel board NAD
16-1 EAST ROOF Shingle Shingles and felt NAD
16-1 EAST ROOF Felt Shingles and felt NAD
16-2 WEST ROOF Shingle Shingles and felt NAD
16-2 WEST ROOF Felt Shingles and felt NAD
JBLE Facility 1030 Hampton, Virginia
Sample ID Collection Location Layer Type Sample Description Asbestos 17-1 EAST ROOF Flashing at seam NAD
17-2 EAST ROOF Flashing at seam NAD
Appendix VI: XRF Lead Paint Readings
JBLE Facility 1030 Hampton, Virginia
XRF Lead Paint Results October 18, 2024
Reading Pb (mg/cm2) Pb +/- Side Component Substrate Color Room Cal-1 1.09 0.04 Calibration Cal-2 0.99 0.04 Calibration Cal-3 1.03 0.04 Calibration 1 0 0.01 Floor Concrete Gray East Kennel 2 0 0.01 D Wall CMU Gray East Kennel 3 0 0.01 D Door Metal Gray East Kennel 4 0 0.01 D Door Casing Metal Gray East Kennel 5 0 0.01 D Conduit Line Metal Gray East Kennel 6 0.05 0.02 A Pipe Metal Red East Kennel 7 0 0.01 A Electrical Switch Box Metal Red East Kennel 8 0 0.01 A Electrical Box Metal Gray East Kennel 9 0.13 0.1 A Air Compressor Metal Blue East Kennel 10 0 0.01 Ceiling Drywall White East Kennel 11 0 0.01 C Upper Trim Wood Gray East Kennel 12 0 0.01 Attic Access Casing Wood White East Kennel 13 0 0.01 B Kennel Wall Concrete Gray East Kennel 14 0 0.01 A Window Casing Metal Dark Gray East Kennel 15 0 0.01 C Column Metal Gray East Kennel 16 0 0.01 B Wall CMU Gray Central Kennel 17 0 0.01 Ceiling Drywall White Central Kennel 18 0 0.01 D Upper Trim Wood White Central Kennel 19 0 0.01 A Kennel Wall Concrete Gray Central Kennel 20 0 0.01 Trench Floor Concrete Gray Central Kennel 21 0 0.01 C Door Casing Metal Gray Central Kennel 22 0 0.01 D Window Header Metal Gray Central Kennel 23 0 0.01 C Wall CMU White Restroom Near Kitchen 24 0 0.01 Ceiling Drywall White Restroom Near Kitchen 25 0 0.01 D Door Casing Metal Brown Restroom Near Kitchen 26 0 0.01 Floor Tile Ceramic White Kitchen 27 0 0.01 B Wall Tile Ceramic White Kitchen 28 0 0.01 B Conduit Line Metal White Kitchen 29 0 0.01 B Trim Under Window Wood White Kitchen 30 0 0.01 Ceiling Drywall White Hall Closet At Kennel 31 0 0.01 D Water Heater Plastic Gray Hall Closet At Kennel
JBLE Facility 1030 Hampton, Virginia
XRF Lead Paint Results October 18, 2024
Reading Pb (mg/cm2) Pb +/- Side Component Substrate Color Room 32 0 0.01 Ceiling Panel Metal White Break Room 33 0 0.01 C Wall CMU Beige Break Room 34 0 0.01 A Wall Drywall Beige Handler Office 35 0 0.01 B Window Sill Drywall Beige Handler Office 36 0 0.01 C Wall Drywall Beige Tac Room 37 0 0.01 D Door Casing Metal Beige Tac Room 38 0 0.01 D Window Casing Metal Black KM Office 39 0 0.01 Attic Access Casing Wood White KM Office 40 0 0.01 D Wall Drywall White Trainer Office 41 0 0.01 C Door Metal Beige Hall 42 0 0.01 C Door Casing Metal Beige Hall 43 0 0.01 D Door Casing Metal Burgundy Exterior 44 0.01 0.01 D Door Metal Burgundy Exterior 45 0.01 0.01 D Door Metal Burgundy Exterior 46 0 0.01 D Upper Trim Wood Burgundy Exterior 47 0 0.01 D Light Fixture Backboard Wood White Exterior 48 0 0.01 D Light Fixture Metal Black Exterior 49 0 0.01 D Ceiling Plaster White Exterior 50 0 0.01 D Gutter Spout Metal Burgundy Exterior 51 0 0.01 B HVAC Unit Metal Gray Exterior 52 0.02 0.01 B Window Sill Metal Black Exterior 53 0 0.01 B Window Casing Metal Black Exterior 54 0 0.01 B Door Casing Metal Burgundy Exterior 55 0.02 0.01 A Gutter Metal Burgundy Exterior 56 0.02 0.01 A Pipe Metal Red Exterior 57 0 0.01 A Wall Stucco White Exterior 58 0 0.01 A Flashing Panel Metal Black Roof 59 0 0.01 A Upper Brick Cover Metal Black Exterior 60 0 0.01 A Toilet Porcelain White Restroom 61 0 0.01 A Sink Porcelain White Restroom Cal-4 1.16 0.05 Calibration Cal-5 1.04 0.04 Calibration Cal-6 1.09 0.04 Calibration
Appendix VII: Laboratory Report
Asbestos Bulk Analysis Report
Client:
Report Number:
Project/Test Address:
Client Number:
Reported Date:
Received Date:
Analyzed Date:
ECS Mid-Atlantic - Williamsburg 10/21/2024
48-5723
10/28/2024
24-10-04088
JBLE Facility 1030; Hampton, Virginia
Laboratory Results Fax Number:
757-229-9978
1643 Merrimac Trail Suite A Williamsburg, VA 23185
10/25/2024
Layer Type Asbestos Client Sample Number
Other Materials
Lab Gross DescriptionLab Sample Number
Client Sample Description
7469 Whitepine Rd
Telephone: 800.347.4010
North Chesterfield, VA 23237
Beige Vinyl; Homogeneous24-10-04088-001A
1-1
100% Non-FibrousTile NAD
12" vinyl floor tiles and mastic
Tan Adhesive; Homogeneous24-10-04088-001B
1-1
3% Cellulose 97% Non-Fibrous
Mastic NAD
12" vinyl floor tiles and mastic
Translucent Green Adhesive; Homogeneous24-10-04088-002A
1-2
4% Cellulose 1% Synthetic 95% Non-Fibrous
Mastic NAD
12" vinyl floor tiles and mastic
Black Vinyl; Homogeneous24-10-04088-002B
1-2
100% Non-FibrousTile NAD
12" vinyl floor tiles and mastic
No bottom mastic present
Black Vinyl-Like; Homogeneous24-10-04088-003A
2-1
100% Non-FibrousCove Base NAD
Vinyl cove base and adhesive
1 of 9Page
Tan Adhesive; Homogeneous24-10-04088-003B
2-1
100% Non-FibrousMastic NAD
Vinyl cove base and adhesive
Black Vinyl-Like; Homogeneous24-10-04088-004A
2-2
100% Non-FibrousCove Base NAD
Vinyl cove base and adhesive
Cream Adhesive; Homogeneous24-10-04088-004B
2-2
100% Non-FibrousMastic NAD
Vinyl cove base and adhesive
Beige Paint-Like; White Brittle-Like;
Inhomogeneous
24-10-04088-005
3-1
100% Non-FibrousNAD
CMU paint/filler
Beige Paint-Like; White Soft Brittle-Like;
Inhomogeneous
24-10-04088-006
3-2
100% Non-FibrousNAD
CMU paint/filler
Gray Paint-Like; White Brittle-Like; Inhomogeneous24-10-04088-007
3-3
100% Non-FibrousNAD
CMU paint/filler
White Texured Paint-Like; White Powdery;
Inhomogeneous
24-10-04088-008A
4-1
100% Non-FibrousTexture NAD
Drywall and joint compound
White Paint-Like; Off-White Powdery;
Inhomogeneous
24-10-04088-008B
4-1
100% Non-FibrousJoint Comp.
NAD
Drywall and joint compound
Environmental Hazards Services, L.L.C
Project/Test Address:
Client Number: Report Number:48-5723 24-10-04088
JBLE Facility 1030; Hampton, Virginia
Other Materials
AsbestosLab Gross Description
Client Sample Number Client Sample Description
Lab Sample Number Layer Type
2 of 9Page
Brown Fibrous; Brown Chalky; Inhomogeneous24-10-04088-008C
4-1
25% Cellulose 75% Non-Fibrous
Drywall NAD
Drywall and joint compound
Beige Paint-Like; White Powdery; Off-White Fibrous; Inhomogeneous
24-10-04088-009A
4-2
15% Cellulose 85% Non-Fibrous
Joint Comp.
NAD
Drywall and joint compound
Brown Fibrous; Gray Chalky; Inhomogeneous24-10-04088-009B
4-2
25% Cellulose 75% Non-Fibrous
Drywall NAD
Drywall and joint compound
White Paint-Like; White Powdery; Off-White Fibrous; Inhomogeneous
24-10-04088-010A
4-3
10% Cellulose 90% Non-Fibrous
Joint Comp.
NAD
Drywall and joint compound
Brown Fibrous; Gray Chalky; Inhomogeneous24-10-04088-010B
4-3
20% Cellulose 80% Non-Fibrous
Drywall NAD
Drywall and joint compound
White Paint-Like; White Powdery; Off-White Fibrous; Inhomogeneous
24-10-04088-011A
4-4
15% Cellulose 85% Non-Fibrous
Joint Comp.
NAD
Drywall and joint compound
Brown Fibrous; Gray Chalky; Inhomogeneous24-10-04088-011B
4-4
25% Cellulose 75% Non-Fibrous
Drywall NAD
Drywall and joint compound
Environmental Hazards Services, L.L.C
Project/Test Address:
Client Number: Report Number:48-5723 24-10-04088
JBLE Facility 1030; Hampton, Virginia
Other Materials
AsbestosLab Gross Description
Client Sample Number Client Sample Description
3 of 9Page
White Paint-Like; White Powdery; Off-White Fibrous; Inhomogeneous
24-10-04088-012A
4-5
15% Cellulose 85% Non-Fibrous
Joint Comp.
NAD
Drywall and joint compound
Brown Fibrous; Gray Chalky; Inhomogeneous24-10-04088-012B
4-5
25% Cellulose 75% Non-Fibrous
Drywall NAD
Drywall and joint compound
Off-White Paint-Like; Brown Pliable;
Inhomogeneous
24-10-04088-013
5-1
100% Non-FibrousNAD
Window frame caulk (interior)
Brown Pliable; Homogeneous24-10-04088-014
5-2
100% Non-FibrousNAD
Window frame caulk (interior)
White Paint-Like; Yellow Granular; Inhomogeneous24-10-04088-015A
6-1
100% Non-FibrousOther * NAD
Ceiling texturing and EIFS
*Granular Material I
Gray Granular; Homogeneous24-10-04088-015B
6-1
100% Non-FibrousOther * NAD
Ceiling texturing and EIFS
*Granular Material II
White Paint-Like; Yellow Granular; Inhomogeneous24-10-04088-016A
6-2
100% Non-FibrousOther * NAD
Ceiling texturing and EIFS
*Granular Material I
Gray Grnaular; Homogeneous24-10-04088-016B
6-2
100% Non-FibrousOther * NAD
Ceiling texturing and EIFS
*Granular Material II
Environmental Hazards Services, L.L.C
Project/Test Address:
Client Number: Report Number:48-5723 24-10-04088
JBLE Facility 1030; Hampton, Virginia
Other Materials
AsbestosLab Gross Description
Client Sample Number Client Sample Description
4 of 9Page
White Paint-Like; Yellow Granular; Inhomogeneous24-10-04088-017A
6-3
100% Non-FibrousOther * NAD
Ceiling texturing and EIFS
*Granular Material I
Gray Granular; Homogeneous24-10-04088-017B
6-3
100% Non-FibrousOther * NAD
Ceiling texturing and EIFS
*Granular Material II
Black Pliable; Homogeneous24-10-04088-018
7-1
100% Non-FibrousNAD
Pipe flange gasket
Black Pliable; Homogeneous24-10-04088-019
7-2
100% Non-FibrousNAD
Pipe flange gasket
Beige Paint-Like; Beige/Gray Pliable-Like; Fibrous;
Inhomogeneous
24-10-04088-020
8-1
10% Talc 90% Non-Fibrous
NAD
Sealants at threaded pipe fittings
Beige Paint-Like; Beige/Gray Pliable-Like; Fibrous;
Inhomogeneous
24-10-04088-021
8-2
10% Talc 90% Non-Fibrous
NAD
Sealants at threaded pipe fittings
Beige Paint-Like; White Pliable Granular-Like;
Inhomogeneous
24-10-04088-022A
9-1
100% Non-FibrousOther * NAD
Soffit/attic wall texturing and EIFS
*Pliable Granular-Like Material
Gray Granular; Homogeneous24-10-04088-022B
9-1
10% Fibrous Glass 90% Non-Fibrous
Other * NAD
Soffit/attic wall texturing and EIFS
*Granular Material
Environmental Hazards Services, L.L.C
Project/Test Address:
Client Number: Report Number:48-5723 24-10-04088
JBLE Facility 1030; Hampton, Virginia
Other Materials
AsbestosLab Gross Description
Client Sample Number Client Sample Description
5 of 9Page
Beige Paint-Like; White Pliable Granular-Like;
Inhomogeneous
24-10-04088-023A
9-2
100% Non-FibrousOther * NAD
Soffit/attic wall texturing and EIFS
*Pliable Granular-Like Material
Gray Granular; Homogeneous24-10-04088-023B
9-2
10% Fibrous Glass 90% Non-Fibrous
Other * NAD
Soffit/attic wall texturing and EIFS
*Granular Material
Beige Paint-Like; White Pliable Granular-Like;
Inhomogeneous
24-10-04088-024A
9-3
100% Non-FibrousOther * NAD
Soffit/attic wall texturing and EIFS
*Pliable Granular-Like Material
Gray Granular; Homogeneous24-10-04088-024B
9-3
10% Fibrous Glass 90% Non-Fibrous
Other * NAD
Soffit/attic wall texturing and EIFS
*Granular Material
Brown Pliable; Homogeneous24-10-04088-025
10-1
100% Non-FibrousNAD
Door frame caulk
Red Pliable; Homogeneous24-10-04088-026
10-2
100% Non-FibrousNAD
Door frame caulk
Red Pliable; Homogeneous24-10-04088-027
11-1
100% Non-FibrousNAD
Brick joint caulk
Red Pliable; Homogeneous24-10-04088-028
11-2
100% Non-FibrousNAD
Brick joint caulk
Environmental Hazards Services, L.L.C
Project/Test Address:
Client Number: Report Number:48-5723 24-10-04088
JBLE Facility 1030; Hampton, Virginia
Other Materials
AsbestosLab Gross Description
Client Sample Number Client Sample Description
6 of 9Page
Brown Pliable; Homogeneous24-10-04088-029
12-1
100% Non-FibrousNAD
Window frame caulk
Brown Pliable; Homogeneous24-10-04088-030
12-2
100% Non-FibrousNAD
Window frame caulk
White Paint-Like; Red Pliable; Inhomogeneous24-10-04088-031
13-1
100% Non-FibrousNAD
Red penetration caulk
White Paint-Like; Red Pliable; Inhomogeneous24-10-04088-032
13-2
100% Non-FibrousNAD
Red penetration caulk
Off-White Pliable; Homogeneous24-10-04088-033
14-1
5% Wollastonite 95% Non-Fibrous
NAD
Mastic on fiberglass pipe insulation
Off-White Pliable; Homogeneous24-10-04088-034
14-2
5% Wollastonite 95% Non-Fibrous
NAD
Mastic on fiberglass pipe insulation
Red Paint-Like; Gray Grnaular; Inhomogeneous24-10-04088-035
15-1
15% Cellulose 85% Non-Fibrous
NAD
Cementitious panel board
Red Paint-Like; Gray Granular; Inhomogeneous24-10-04088-036
15-2
15% Cellulose 85% Non-Fibrous
NAD
Cementitious panel board
Environmental Hazards Services, L.L.C
Project/Test Address:
Client Number: Report Number:48-5723 24-10-04088
JBLE Facility 1030; Hampton, Virginia
Other Materials
AsbestosLab Gross Description
Client Sample Number Client Sample Description
7 of 9Page
Black Aggregate; Black Tar-Like; Fibrous;
Inhomogeneous
24-10-04088-037A
16-1
25% Fibrous Glass 75% Non-Fibrous
Shingle NAD
Shingles and felt
Black Tar-Like; Fibrous; Homogeneous24-10-04088-037B
16-1
55% Cellulose 45% Non-Fibrous
Felt NAD
Shingles and felt
Black Aggregate; Black Tar-Like; Fibrous;
Inhomogeneous
24-10-04088-038A
16-2
25% Fibrous Glass 75% Non-Fibrous
Shingle NAD
Shingles and felt
Black Tar-Like; Fibrous; Homogeneous24-10-04088-038B
16-2
55% Cellulose 45% Non-Fibrous
Felt NAD
Shingles and felt
Gray Pliable; Homogeneous24-10-04088-039
17-1
100% Non-FibrousNAD
Flashing at seam
Gray Pliable; Homogeneous24-10-04088-040
17-2
100% Non-FibrousNAD
Flashing at seam
Environmental Hazards Services, L.L.C
Project/Test Address:
Client Number: Report Number:48-5723 24-10-04088
JBLE Facility 1030; Hampton, Virginia
Other Materials
AsbestosLab Gross Description
Client Sample Number Client Sample Description
8 of 9Page
Environmental Hazards Services, L.L.C
Project/Test Address:
Client Number: Report Number:48-5723 24-10-04088
JBLE Facility 1030; Hampton, Virginia
Other Materials
AsbestosLab Gross Description
Client Sample Number Client Sample Description
Lab Sample Number Layer Type
Melissa Kanode
1% Asbestos
Analyst:
Reporting Limit:
Method:
QC Blank:
QC Sample:
Keleigh King
EPA Method 600/R-93/116, EPA Method 600/M4-82-020
QA/QC Clerk
Reviewed By Authorized Signatory:
97-M22013-2
SRM 1866 Fiberglass
NAD = no asbestos detectedLEGEND:
These results are based on a comparative visual estimate. The condition of the samples analyzed was acceptable upon receipt per laboratory protocol unless otherwise noted on this report. Each distinct component in an inhomogeneous sample was analyzed separately and reported as a composite.
Results represent the analysis of samples submitted by the client. Sample location, description, area, volume, etc., was provided by the client. This report cannot be used by the client to claim product endorsement by NVLAP or any agency of the U.S. Government. This report shall not be reproduced except in full, without the written consent of the Environmental Hazards Service, L.L.C. All information concerning sampling location, date, and time can be found on Chain-of-Custody. Environmental Hazards Services, L.L.C. does not perform any sample collection. . NVLAP #101882-0 VELAP 460172
Environmental Hazards Services, L.L.C. recommends reanalysis by point count (for more accurate quantification) or Transmission Electron Microscopy
(TEM), (for enhanced detection capabilities) for materials regulated by EPA NESHAP (National Emission Standards for Hazardous Air Pollutants) and found to contain less than ten percent (<10%) asbestos by polarized light microscopy (PLM). Both services are available for an additional fee.
400 Point Count Analysis, where noted, performed per EPA Method 600/R-93/116 with a Reporting Limit of 0.25%.
9 of 9Page
Appendix VIII: Certifications/ Licenses
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Appendix IX: Mold Reference and Guidance Documents
REFERENCE AND GUIDANCE DOCUMENTS
A Brief Guide to Mold in the Workplace, Occupational Safety Health Administration
(OSHA), SHIB 03-10-10, updated 11-08-13
ANSI/IICRC S520 Standard and Reference Guide for Professional Mold Remediation, Institute of Inspection, Cleaning, and Restoration Certification, 2015.
ANSI/IICRC S500 Standard and Reference Guide for Professional Water Damage
Restoration, Institute of Inspection, Cleaning, and Restoration Certification, 2015.
Bioaerosols: Assessment and Controls, American Conference of Governmental
Industrial Hygienists, 1999.
Building Air Quality: A Guide for Building Owners and Facility Managers, EPA, EPA 402-
F-91-102, December 1991
Centers for Disease Control and Prevention (CDC), https://www.cdc.gov/mold/faqs.htm
Department of Energy and the Environment (DOEE), Mold Assessment and
Remediation Licensure Regulations.
EPA – Mold Resources, https://www.epa.gov/mold
Guidelines on Assessment and Remediation of Fungi in Indoor Environments, New York
City Department of Health and Mental Hygiene, November 2008.
Mold Moisture and Your Home, EPA, EPA-402-K-02-003, September 2012
Mold Remediation in Schools and Commercial Buildings, EPA, EPA 402-K-01-001, September 2008 https://www.cdc.gov/mold/faqs.htm https://www.epa.gov/mold
| Title Page |
| Cover Letter |
| Executive Summary |
| 1.0 Site Description |
| 2.0 Purpose |
| 3.0 Methodology |
| 3.1 Asbestos-Containing Materials |
| 3.2 Lead in Paint and Surface Coatings |
| 3.3 Mold and Moisture |
| 4.0 Results |
| 4.1 Asbestos Sampling |
| 4.2 Suspect or Assumed Asbestos-Containing Materials |
| 4.3 Lead in Paint and Surface Coatings |
| 4.4 Mold and Moisture |
| 5.0 Recommendations and Regulatory Requirements |
| 5.1 Asbestos-Containing Materials |
| 5.2 Lead in Paint and Surface Coatings |
| 5.3 Mold and Moisture |
| 6.0 Limitations |
| Approximate Location of Moisture-Impacted Materials |
| Representative Photographs of Sampled Materials for Asbestos - Asbestos Not Detected |
| Representative Photographs of Identified Lead Paint |
| Representative Photographs of Identified Moisture-Impacted Materials |
| Asbestos Bulk Sample Results Summary |
| XRF Lead Paint Readings |
| Laboratory Report |
| Certifications/Licenses |
| Mold Reference and Guidance Documents |
File details come from the government source that posted it. Updated .