Attachment 3a - B410 Limited Hazardous Materials Survey Report.pdf
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- 140P8320R0008
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This Request for Proposals solicits abatement services for hazardous materials including asbestos, lead, mercury, polychlorinated biphenyls, and wildlife excrement in several historic buildings at Fort Vancouver National Historic Site. The National Park Service requires a small business contractor to remove hazardous materials from multiple buildings and perform associated selective demolition and minor repairs. The contractor must provide payment and performance bonds for 100% and maintain liability insurance. The estimated contract value is between $250,000 and $1,000,000. Proposals are due by the date specified in the solicitation, which is a best value procurement set aside for small businesses. The work must be completed within 180 days of award.
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1011 SW Klickitat Way, Suite 104, Seattle, Washington 98134 Phone 206-381-1128 Toll Free 800-666-2959 Fax 206-254-4279
Environmental Consulting Hazardous Materials Management Industrial Hygiene Services Construction Management Indoor Air Quality
LIMITED HAZARDOUS MATERIALS SURVEY REPORT
NATIONAL PARK SERVICE
FORT VANCOUVER NATIONAL HISTORIC SITE
BUILDING 410
East Vancouver Barracks Building 410
Vancouver, Washington 98661
October 31st, 2019
Prepared For:
Mary Hazell National Park Service 612 East Reserve Street Vancouver, WA 98661 ii
Limited Hazardous Materials Survey Report
National Park Service Fort Vancouver Historic Site
East Vancouver Barracks Building 410 Vancouver, Washington 98661
EHSI Project No.: # 11295
The material and data in this report were prepared under the supervision and direction of the undersigned.
Rory Peterson Lead AHERA Building Inspector
Derica Escamilla Principal of Hazardous Materials Services iii
TABLE OF CONTENTS
Acronym List ....................................................................................... iv
1.0 EXECUTIVE SUMMARY
1.1 BACKGROUND
1.2 EXTENT OF CURRENT SURVEY
1.3 ACM MATERIALS FOUND
1.4 OPINIONS AND RECOMMENDATIONS
1.5 LIMITATIONS/DISCLAIMER
2.0 LIMITED LEAD AND ASBESTOS SURVEY REPORT
2.1 BACKGROUND
2.2 BUILDING DESCRIPTION
2.3 SAMPLING METHODOLOGY
2.3.1 Asbestos-Containing Materials
2.3.2 Lead-Containing Paint/Lead-Containing Materials
2.3.3 Ionizing Radiation
2.3.4 Petroleum Hydrocarbon Contaminated Sludge
2.4 SAMPLING RESULTS
2.4.1 Asbestos-Containing Materials
2.4.2 Lead-Containing Paint and Building Materials
2.4.3 Toxicity Characteristic Leaching Procedure Sampling
2.4.4 Ionizing Radiation
2.4.5 Polychlorinated Biphenyls
2.4.6 Mercury-Containing Fluorescent Light Tubes, CFL Bulbs, and thermostats
2.4.7 Petroleum Hydrocarbon Contaminated Sludge
3.0 LIMITATIONS
4.0 STANDARD OF CARE
5.0 CERTIFIED AHERA BUILDING INSPECTORS
APPENDICES
A ............................Asbestos Laboratory Reports and Field Data Forms B ............................Lead Analytical Laboratory Results and Field Data Forms C ............................Toxicity Characterization Leaching Procedure Analytical Laboratory
Results and Field Data Forms D ...........................Radon Analytical Laboratory Results and Field Data Forms E ............................Petroleum Hydrocarbon Contaminated Sludge Analytical Laboratory
Results and Field Data Forms F ............................Certified AHERA Building Inspector Certificates G ...........................Laboratory Certifications for Asbestos, Lead, Radon, and Petroleum
Hydrocarbon Contaminated Sludge Analysis H ...........................Sample Location Drawings for Asbestos, Lead, Radon, and Petroleum
Hydrocarbon Contaminated Sludge iv
ACRONYM LIST
ACM .......................Asbestos-Containing Material AHERA ....................Asbestos Hazard Emergency Response Act AHU .......................Air Handling unit AIHA ......................American Industrial Hygiene Association CFL ........................Compact Fluorescent Light CFR ........................Code of Federal Regulations CMU………………………….Concrete Masonry Unit DOSH .....................Washington State Department of Labor and Industries, Division of
Occupational Safety and Health EA ..........................Each Ecology ...................Washington State Department of Ecology EHSI .......................EHS-International, Inc.
ELLAP .....................Environmental Lead Laboratory Accreditation Program GWB .......................Gypsum Wall Board Hg ..........................Mercury JC ..........................Joint Compound LCM ........................Lead-Containing Material LCP ........................Lead-Containing Paint LF ..........................Linear Feet L&I .........................Washington State Department of Labor and Industries mg/L ......................Milligrams Per Liter N/A ........................Not Applicable ND .........................None Detected NVL ........................NVL Laboratories, Inc.
NVLAP ....................National Voluntary Laboratory Accreditation Program OD .........................Outside Diameter OSHA .....................US Occupational Safety and Health Administration Pb ..........................Lead PCBs .......................Polychlorinated Biphenyls PLM ........................Polarized Light Microscopy ppm .......................Parts per Million QA .........................Quality Assurance RCW .......................Revised Code of Washington SAT ........................Seattle Asbestos Test, LLC Se ..........................Selenium SF ..........................Square Feet SVF ........................Sheet Vinyl Flooring SWCAA ...................Southwest Clean Air Agency TCLP .......................Toxicity Characteristic Leaching Procedure VCT ........................Vinyl Composite Tile WAC .......................Washington Administrative Code
wt. .........................Weight w/ ..........................With XRF ........................x-ray fluorescence
Fort Vancouver National Historic Site – B410
EHSI Project 11295
1.0 EXECUTIVE SUMMARY
1.1 BACKGROUND
The National Park Service (NPS) plans to renovate Building 410 (B410) at the Fort Vancouver National Historic Site (FV NHS) located at 612 E. Reserve Street, Vancouver, Washington. The NPS has contracted EHS-International, Inc. (EHSI), a hazardous materials and industrial hygiene consulting firm, to conduct a Limited Lead and Asbestos Survey of B410 in preparation for this project. The intent of the survey is to specifically identify and quantify asbestos-containing building materials (ACM), interior lead-containing paint (LCP), other interior lead-containing building materials (LCM), to collect a lead toxicity characteristic leaching procedure (TCLP) sample representative of all materials that may be in the assumed waste stream, and to inspect and quantify fluorescent light fixtures that may contain polychlorinated biphenyl (PCB)-containing ballasts, and mercury (Hg)-containing fluorescent light tubes, compact fluorescent light (CFL) bulbs, and high intensity discharge (HID) lamps, that may be impacted by renovation activities. In addition, EHSI also collected sludge samples from interior and exterior drains to identify the presence of Benzene, Toluene, Ethylbenzene, and Xylenes (BTEX), total petroleum hydrocarbons (TPH) as diesel and motor oil, and Resource Conservation and Recovery Act (RCRA) metals (arsenic, barium, cadmium, chromium, lead, mercury, selenium, and silver).
1.2 EXTENT OF CURRENT SURVEY
EHSI inspected accessible interior and exterior suspect ACM that may be potentially impacted by future projects. Accessible suspect materials were sampled including, but not limited to:
interior and exterior wall systems, window systems, and mechanical systems. The LCP and LCM survey was limited to the interior of the building only. The sludge sampling was limited to drains that were accessible and representative of the interior and exterior drainage system in and around B748. EHSI accomplished a representative destructive inspection; however, in areas inaccessible for inspection (e.g., energized electrical equipment, energized air handling unit and fire door cores) suspect materials were assumed to be ACM.
1.3 ACM MATERIALS FOUND
SUMMARY OF ASBESTOS-CONTAINING MATERIALS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 410
ASBESTOS MATERIAL DESCRIPTION LOCATION
Non-ACM 12”x12” beige/tan VCT (w/ brown and off-white streaks) on ACM black mastic on gray paint (on concrete) [Sample #s 11295-B410-44, 45 and 46]
Rooms 2, 3, 4, 6, 11, 12, and Corridor 8
Non-ACM 12”x12” brown/tan VCT (w/ brown and beige streaks) on ACM black mastic on painted (on concrete) [Sample #s 11295-B410-44, 45 and 46]
Room 7 and Corridor
Non-ACM 12”x12” beige/tan VCT (w/ brown and off-white streaks) on ACM black mastic on OSB [Sample #s 11295-B410-46]
2nd Floor Room 2-1, 2-2, 2-3 and 2-4
SUMMARY OF ASBESTOS-CONTAINING MATERIALS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 410
ASBESTOS MATERIAL DESCRIPTION LOCATION
Non-ACM beige SVF (w/ broken rock pattern) on ACM off-white/gray paper backing w/ACM beige mastic and black mastic on concrete [Sample # 11295-B410-53]
Toilet Room 10
Non-ACM red/brown rubber stair tread on ACM brown mastic w/ paint on wood stair tread [Sample # 11295-B410-55]
Stairs
Metal fire door w/ 1’x1’ window w/ assumed ACM core Auto Bay Area 1
Metal fire door w/ assumed ACM core
Auto Bay Area 1, Room 9, Corridor 8 and 2nd Floor Room 2-1
Small electrical panels w/ assumed ACM internal components (<1 SF in size) Corridor 8
Electrical panels w/ assumed ACM internal components (1-6 SF in size)
Corridor 8 2nd Floor Room 2-1
Small electrical disconnect w/ assumed ACM internal components (<1 SF in size) (associated w/ rollup doors and heating system)
Auto Bay Area 1
Small electrical disconnect w/ assumed ACM internal components (<1 SF in size) Room 9
Electrical disconnect/control panel w/ assumed ACM internal components (1-6 SF in size)
Auto Bay Area 1
5’x4 ½’x3 ¾’ AHU w/ assumed ACM internal components Exterior, south side of building
Assumed ACM tar/sealant around 1’x1 vent hood Roof Assumed ACM tar/sealant around 1’ OD vent Roof Assumed ACM tar/sealant around 2’x2’ mushroom-shaped vent Roof Assumed ACM tar/sealant around lead vent pipe Roof
KEY: ACM = asbestos containing material, OD = outer diameter, VCT = vinyl composite tile, w/ = with
1.4 OPINIONS AND RECOMMENDATIONS
EHSI recommends that all impacted ACM identified in paragraph 1.3 be removed and disposed of prior to any renovation and demolition activities.
Any suspect materials not identified as having been surveyed in this report must be treated as an ACM until determined otherwise by a Certified Asbestos Building Inspector and NVLAP certified laboratory.
The United States Environmental Protection Agency (EPA) recommends mitigation of radon gas if the average of two short-term tests taken in the lowest level of the building suitable for occupancy show radon levels that are equal to or greater than 4.0 picoCuries per liter (pCi/L).
Only one of the two radon canisters submitted for analysis registered at or above the action level and therefore no remedial actions for mitigation of radon gas are recommended at this time.
Washington State Department of Labor and Industries (L&I) Division of Occupational Safety and Health (DOSH) and the US Occupational Safety and Health Administration (OSHA) require employers to conduct a hazard assessment and take appropriate worker protection precautions whenever building materials are disturbed that have detectable quantities of lead. Since the type of work planned (e.g., demolition or renovation) will disturb the LCP, the contractor will need to perform an initial exposure assessment and lead awareness training in accordance with the regulations. Special care should be taken to reduce potential employee exposure to lead when demolishing porcelain bathroom fixtures and painted metal, including reducing airborne dust (eq., water misting and use of hand tools, and/or local exhaust ventilation).
A select number of fluorescent light fixtures inspected have magnetic ballasts which are assumed to contain greater than two parts per million (> 2 ppm) PCB-dielectric fluid. Magnetic ballasts must be removed from fixtures and disposed of as Washington Department of Ecology (Ecology) Dangerous Waste. All fluorescent tubes and lamps contain mercury; any fluorescent lamps/tubes to be disturbed during the project must be recycled as (Ecology) Universal Waste.
Ecology’s Model Toxics Control Act (MTCA) (Chapter 70.105D RCW) cleanup standards and law administer cleanup and prevention of contaminated sites. A representative number of interior and exterior drain sludge was sampled and compared to MTCA Method A and Method B cleanup levels. Based on the results, the sludge and surrounding soil should be cleaned up in accordance with MTCA standards. The following samples exceeded MTCA Method A or Method B cleanup levels:
11295-B410-S1 for motor oil range, cadmium and lead 11295-B410-S2 for lead 11176-B410-S3 for cadmium 11176-B410-S4 for motor oil range and lead
1.5 LIMITATIONS/DISCLAIMER
This report does not represent a comprehensive hazardous materials investigation for the subject property. This investigation has been conducted by EHSI under a specific scope of work authorized by the NPS for a specific purpose. Energized electrical equipment, energized air handling units, fire door cores and some roofing materials were not sampled but were assumed to be present based on the inspector’s experience with similar systems on other projects and are assumed to be ACMs. Exterior lead sampling was excluded from the scope of work. All exterior painted surfaces are assumed to have lead-containing paint. This report and accompanying appendices include the supporting information for this executive summary.
2.0 LIMITED LEAD AND ASBESTOS SURVEY REPORT
2.1 BACKGROUND
The NPS has contracted EHSI to accomplish a pre-renovation limited hazardous materials survey of the existing structure and to collect a lead-TCLP sample representative of the anticipated demolition debris. For the limited hazardous materials survey, EHSI was tasked to use applicable federal, state, and local guidelines in the accomplishment of its survey. EHSI was further tasked to provide a written survey report including: identification of all suspect materials; a determination of whether suspect materials were: ACM, LCP, and LCM, whether drain sludge contained BTEX, TPH as diesel and motor oil, RCRA metals, and characterization of ionizing radiation concentrations and to provide analytical reports indicating the presence and quantity of the hazardous materials.
On September 3rd & 4th, 2019, EHSI conducted a Limited Hazardous Materials Survey that meets the Washington State “Good Faith Survey” requirements as cited in Revised Code of Washington (RCW) 49.26.016 and implemented by L&I DOSH regulation, Washington Administrative Code (WAC) 296-62-07721, and Regulation Section 476-040 of the Southwest Clean Air Agency (SWCAA).
2.2 BUILDING DESCRIPTION
B410 is located in Vancouver, Washington at the Fort Vancouver National Historic site and part of the East Barracks portion of the site. B410 was originally constructed in 1935 with alterations and repairs made in 1987, 1990, and 2005. The building is a single-story structure on a slab-on grade foundation with a mezzanine and attic space. The building has been used as a former auto maintenance facility. Currently, it is largely unoccupied with a small area of the maintenance bay is used by a local bicycle group. The exterior of B410 is made up of wood siding, wood windows, metal doors and a composite shingle roof. Interior finishes include; bare concrete floors, vinyl composite tile (VCT), wood base, gypsum wallboard (GWB), and wood wall panels. The building is currently heated by a forced air system in the office area of the building while the auto maintenance bays are heated with natural gas ceiling mounted unit heaters. Fluorescent light fixtures provide light throughout the building.
2.3 SAMPLING METHODOLOGY
2.3.1 Asbestos-Containing Materials
The EHSI field inspectors are asbestos Building Inspectors, certified under the requirements of the United States Environmental Protection Agency (USEPA) AHERA regulation 40 Code of Federal Regulations (CFR) 763, Subpart E. Copies of their certificates are provided in Appendix F. The number of bulk samples collected and their locations are based on the AHERA regulation and the guidelines provided by the USEPA Document 560/5-85-030a, October 1985, Asbestos in Buildings: Simplified Sampling Scheme for Friable Surfacing Materials.
EHSI collected samples and obtained analytical data for suspect ACM identified on the property. Once collected, each bulk sample was sealed in an unadulterated plastic bag to eliminate the possibility of cross-contamination. “Chain-of-Custody” tracking was followed to maintain sample integrity during handling and data reporting at EHSI and the analytical laboratory. As specified in 40 CFR Chapter 1 (1-1-87 edition) Part 763, Subpart F, and Appendix A, each sample was analyzed using polarized light microscopy (PLM) / dispersion staining techniques, in accordance with USEPA Method 600/R-93/116. Samples were analyzed for asbestos content by Seattle Asbestos Test, LLC (SAT) located in Seattle, Washington. SAT participates in the National Institute for Standards and Technology (NIST) National Voluntary Laboratory Accreditation Plan (NVLAP). Laboratory NVLAP certifications are included in Appendix G. Only materials containing more than 1% total asbestos were classified as “asbestos-containing” based on USEPA, state, and local regulations.
2.3.2 Lead-Containing Paint/Lead-Containing Materials
EHSI used a Niton Model XLp x-ray fluorescence (XRF) Spectrum Analyzer to measure lead content on interior paint coatings and other suspect LCM. Measurements were representative of all layers of paint and/or LCM. A summary of Lead Paint XRF results is provided in Table 3.
Bulk quality assurance samples were taken for a representative number of LBP and LCM and were sent to NVL located in Seattle, Washington, an accredited laboratory for Atomic Absorption Spectroscopy (USEPA Method-7000B) by the American Industrial Hygiene Association (AIHA) under the Environmental Lead Laboratory Accreditation Program (ELLAP).
Copies of laboratory reports and field data forms for lead are in Appendix B.
All XRF sample shots are representative of that color on that specific substrate and component. The report user shall deduce from the data in Table 3, if certain building materials throughout the entire building contain lead and should not assume that what is detected is only in the specific location identified in the Table.
2.3.3 Ionizing Radiation
EHSI used a Ludlum 2241 Geiger Counter to measure for the presence of ionizing radiation levels above background on the interior and exterior of the building. Interior measurements were recorded in uniformly sized partitions of the building footprint (roughly 12’x12’ in dimensions) as well the expansion joint in the middle of the building floor foundation running east and west. Exterior measurements were generalized over roughly 10’ intervals and were taken along the ground adjacent to the building foundation. A summary of Geiger Counter readings is provided in Table 6. EHSI used Radon Testing Corporation of America (RTCA) Professional Radon Test kits, each containing one 4-inch charcoal canister in accordance with the manufacturer’s recommendations to collect a representative measure of the radon level present inside Building 410. After collection, the test kits were submitted to RTCA, a certified member of the National Radon Safety Board (NRSB) for laboratory analysis. Copies of the laboratory report and field data forms for radon are in Appendix D.
2.3.4 Petroleum Hydrocarbon Contaminated Sludge
EHSI collected four (4) sludge samples using three (3) volatile organic analysis (VOA) vials and one-two (1-2), four (4) ounce containers. The VOA vials were filled using EPA 5035 – purge and trap techniques. The four-ounce jars were filled using the same method. Following collection, the filled sample containers were placed in a cooler with ice until delivery to the analytical laboratory. EHSI field personnel checked all sample containers for completeness and cap tightness. The sample cooler was then placed in a field vehicle to await transportation to Freidman and Bruya, Inc. located in Seattle, Washington, a National Environmental Laboratory Program (NELAP) accredited laboratory for Ecology Method NWTPH-Dx, USEPA
Method 8021B, and USEPA Method 6020B. Not all samples were submitted for each analysis.
Selected samples were submitted based upon the primary contaminants of concern. A summary of the analytical results is provided in Table 7,8, and 9 and associated laboratory report is provided in Appendix E.
2.4 SAMPLING RESULTS
2.4.1 Asbestos-Containing Materials
One hundred and three (103) bulk samples of suspect ACM were collected as part of the survey. Limited destructive inspection was conducted to identify hidden and/or concealed materials. Copies of the asbestos analytical laboratory results are included in Appendix A.
Asbestos sample location drawings are provided in Appendix H. Asbestos sampling information including sample number, material description, sample location, and analytical results are summarized in Table 1. The ACM and assumed ACM identified during this survey, including the quantity and location, is summarized in Table 2. All suspect materials were accessible for sampling.
TABLE 1
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-01
Custodial Closet Room 5
Gray CMU w/ gray grout w/ paint ND N/A
11295- B410-02
Exterior North Side
Hard beige/gray window glazing putty w/ paint (on 4’x6’ wood-framed windows)
ND N/A
11295- B410-03
Exterior North Side
Hard beige/gray window glazing putty w/ paint (on 4’x6’ wood-framed windows)
ND N/A
11295- B410-
04QA
Exterior North Side
Hard beige/gray/off-white window glazing putty w/ paint and debris (on 4’x6’ wood-framed windows)
ND N/A
11295- B410-05
Exterior North Side
Beige/off-white window glazing putty patch w/ paint (on 4’x6’ wood-framed windows)
ND N/A
11295- B410-06
Exterior North Side
Beige/off-white window glazing putty patch w/ paint (on 4’x6’ wood-framed windows)
ND N/A
11295- B410-07
Exterior North Side
Beige/off-white window glazing putty patch w/ paint (on 4’x6’ wood-framed windows)
ND N/A
11295- B410-08
Auto Bay Area
Layer 1: Black foam window glazing gasket w/ trace paint Layer 2: Trace black/clear putty/mastic
ND
(All Layers)
N/A (All Layers)
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-09
Auto Bay Area
Layer 1: Black foam window glazing gasket w/ paint Layer 2: Black/clear putty/mastic
ND
(All Layers)
N/A (All Layers)
11295- B410-10
Auto Bay Area
Layer 1: Black foam window glazing gasket w/ paint Layer 2: Black/clear putty/mastic
ND
(All Layers)
N/A (All Layers)
11295- B410-11
Room 11 Beige/off-white fibrous rope w/ paint (counter-weight rope on each side of old windows)
ND N/A
11295- B410-12
Room 11 Beige/off-white fibrous rope w/ paint (counter-weight rope on each side of old windows)
ND N/A
11295- B410-13
Room 12 Beige/off-white fibrous rope w/ paint (counter-weight rope on each side of old windows)
ND N/A
11295- B410-14
Exterior West Side
Layer 1: White window glazing putty patch w/ paint Layer 2: Beige window glazing putty w/ paint (on old 3’x4’8” wood-framed window)
ND
(All Layers)
N/A (All Layers)
11295- B410-15
Exterior West Side
Layer 1: White window glazing putty patch w/ paint Layer 2: Beige window glazing putty w/ paint (on old 3’x4’8” wood-framed window)
ND
(All Layers)
N/A (All Layers)
11295- B410-16
Exterior West Side
Layer 1: White window glazing putty patch w/ paint Layer 2: Beige window glazing putty w/ paint (on old 3’x4’8” wood-framed window)
ND
(All Layers)
N/A (All Layers)
11295- B410-
17QA
Exterior West Side
Layer 1: White window glazing putty patch w/ paint Layer 2: Gray window glazing putty patch (on old 3’x4’8” wood-framed window)
ND
(All Layers)
N/A (All Layers)
11295- B410-18
Exterior West Side
Layer 1: White window glazing putty patch w/ paint Layer 2: Gray window glazing putty patch (on old 3’x4’8” wood-framed window)
ND
(All Layers)
N/A (All Layers)
11295- B410-19
Exterior South Side
Beige/off-white window glazing putty w/ paint (on new 3’x4’8” wood-framed window)
ND N/A
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-20
Exterior South Side
Beige/off-white window glazing putty w/ paint (on new 3’x4’8” wood-framed window)
ND N/A
11295- B410-21
Exterior East Side
Beige/off-white window glazing putty w/ paint (on new 3’x4’8” wood-framed window)
ND N/A
11295- B410-22
Exterior South Side
Hard beige/off-white window glazing putty w/ paint (on new 3’x4’8” wood-framed window)
ND N/A
11295- B410-23
Exterior South Side
Hard beige/off-white window glazing putty w/ paint (on new 3’x4’8” wood-framed window)
ND N/A
11295- B410-
24QA
Exterior South Side
Hard beige/off-white window glazing putty w/ paint (on new 3’x4’8” wood-framed window)
ND N/A
11295- B410-25
Room 11 Layer 1: 4” Black cove base w/ paint Layer 2: Brown mastic
ND
(All Layers)
N/A (All Layers)
11295- B410-26
Room 10 Layer 1: 4” Black cove base w/ paint Layer 2: Brown mastic
ND
(All Layers)
N/A (All Layers)
11295- B410-27
2nd Floor, Room 2-1
Layer 1: 4” Black cove base w/ paint Layer 2: Brown mastic Layer 3: Off-white/green paint
ND
(All Layers)
N/A (All Layers)
11295- B410-28
Toilet Room
Layer 1: 4” Newer black/dark gray cove base Layer 2: White/off-white mastic
ND
(All Layers)
N/A (All Layers)
11295- B410-29
Office Room 3
Layer 1: 4” Newer black/dark gray/brown cove base Layer 2: White/off-white mastic Layer 3: Trace JC w/ paint
ND
(All Layers)
N/A (All Layers)
11295- B410-30 Room 7
Layer 1: 4” Newer black/dark gray/brown cove base Layer 2: White/off-white mastic Layer 3: Trace JC w/ paint
ND
(All Layers)
N/A (All Layers)
11295- B410-
31QA
Room 9 Layer 1: 4” Black cove base Layer 2: Light brown/tan mastic
ND
(All Layers)
N/A (All Layers)
11295- B410-32 Stairwell
Layer 1: 4” Black cove base Layer 2: Light brown mastic
ND
(All Layers)
N/A (All Layers)
11295- B410-33
Toilet Room
Layer 1: Rough texturing/skim coat w/ JC w/ paint and paper Layer 2: GWB w/ paint and paper (corner)
ND
(All Layers)
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-34
Toilet Room
Layer 1: Trace rough texturing/ skim coat w/ paint and paper Layer 2: GWB wall w/ paint and paper (mid-wall)
ND
(All Layers)
N/A (All Layers)
11295- B410-35
Toilet Room
Layer 1: Trace rough texturing/ skim coat and paper Layer 2: GWB wall w/ paint and paper (mid-wall)
ND
(All Layers)
N/A (All Layers)
11295- B410-36 Room 2
Layer 1: Orange peel texturing w/ JC w/ paint and paper Layer 2: GWB wall w/ paper (corner)
ND
(All Layers)
N/A (All Layers)
11295- B410-37
Room 7
Layer 1: Orange peel texturing w/ JC w/ paint and paper Layer 2: GWB wall w/ paper (corner)
ND
(All Layers)
N/A (All Layers)
11295- B410-38
Room 7
Layer 1: Orange peel texturing w/ paint and paper Layer 2: GWB wall w/ paper (mid-wall)
ND
(All Layers)
N/A (All Layers)
11295- B410-39
Room 4
Layer 1: Orange peel texturing w/ paint and paper Layer 2: GWB wall w/ paper (mid-wall)
ND
(All Layers)
N/A (All Layers)
11295- B410-40 Room 8
Layer 1: Orange peel texturing on JC w/ paint and paper Layer 2: GWB wall w/ paper (mid-wall)
ND
(All Layers)
N/A (All Layers)
11295- B410-41
2nd Floor, Room 2-3
Layer 1: JC w/ paint and paper Layer 2: GWB wall w/ paper (corner)
ND
(All Layers)
N/A (All Layers)
11295- B410-42
2nd Floor, Room 2-4
GWB wall w/ paint and paper (mid-wall) ND N/A
11295- B410-43
2nd Floor, Room 2-1
GWB wall w/ paint and paper (mid-wall)
ND N/A
11295- B410-44 Room 12
Layer 1: 12”x12” Beige/tan VCT (w/ brown and off-white streaks) Layer 2: Black mastic Layer 3: Gray paint (on concrete)
L1: ND
L2: 2%
L3: ND
Chrysotile
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-45
Office Room
Layer 1: 12”x12” Beige/tan VCT (w/ brown and off-white streaks) Layer 2: Black mastic Layer 3: Gray paint (on concrete)
11295- B410-46
2nd Floor, Room 2-1
Layer 1: 12”x12” Beige/tan VCT (w/ brown and off-white streaks) Layer 2: Black mastic Layer 3: OSB
11295- B410-47
Corridor 8
Layer 1: 12”x12” Brown VCT (w/ brown and beige streak) Layer 2: Black mastic (on painted concrete)
ND
(All Layers)
N/A (All Layers)
11295- B410-48 Room 7
Layer 1: 12”x12” Brown VCT (w/ brown and beige streak) Layer 2: Black mastic (on painted concrete)
ND
(All Layers)
N/A (All Layers)
11295- B410-49
Corridor 8
Layer 1: 12”x12” Brown VCT (w/ brown and beige streak) Layer 2: Black mastic (on painted concrete)
ND
(All Layers)
N/A (All Layers)
11295- B410-50
2nd Floor, Room 2-1
Layer 1: 12”x12” Newer beige/off-white VCT Layer 2: Trace yellow mastic (on OSB)
ND
(All Layers)
N/A (All Layers)
11295- B410-
51QA
2nd Floor, Room 2-1
Layer 1: 12”x12” Newer beige/off-white VCT Layer 2: Yellow/tan mastic w/ derbis Layer 3: OSB (on hard wood floor)
ND
(All Layers)
N/A (All Layers)
11295- B410-52
Toilet Room
Layer 1: Beige/gray SVF (w/broken rock pattern) Layer 2: Off-white/gray paper backing w/ beige mastic and black mastic (on concrete)
ND
(All Layers)
N/A (All Layers)
11295- B410-
53QAX
Toilet Room
Layer 1: Beige/gray SVF (w/broken rock pattern) Layer 2: Off-white/gray paper backing w/ beige/yellow mastic and black mastic (on concrete)
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-54
Stairs
Layer 1: Red/brown rubber stair tread Layer 2: Brown mastic w/ paint (on wood stairs)
ND
(All Layers)
N/A (All Layers)
11295- B410-
55QAX
Stairs
Layer 1: Red/brown rubber stair tread Layer 2: Brown mastic w/ paint Layer 3: Wood stair tread w/ paint
11295- B410-56 Corridor
2’x4’ Beige SACT w/ white paint (w/ small worm track and pin hole pattern)
ND N/A
11295- B410-57 Room 7
2’x4’ Beige SACT w/ white paint (w/ small worm track and pin hole pattern)
ND N/A
11295- B410-58
Toilet Room
2’x4’ Beige SACT w/ white paint (w/ small worm track and pin hole pattern)
ND N/A
11295- B410-59
Auto Bay Area
Layer 1: Beige/off-white paper wrap w/mastic Layer 2: Silver foil Layer 3: SB yellow fiberglass
TSI
ND
(All Layers)
N/A (All Layers)
11295- B410-60
Auto Bay Area
Layer 1: Beige/off-white paper wrap w/mastic Layer 2: Silver foil Layer 3: Yellow fiberglass TSI (on small bore pipes)
ND
(All Layers)
N/A (All Layers)
11295- B410-61
Toilet Room
Layer 1: Beige/off-white paper wrap w/mastic Layer 2: Silver foil Layer 3: Yellow fiberglass TSI (on small bore pipes)
ND
(All Layers)
N/A (All Layers)
11295- B410-62
Auto Bay Area
Beige/gray pipe dope (on galvanized water line fittings) ND N/A
11295- B410-63
Auto Bay Area
Black pipe dope (on galvanized water line fittings)
ND N/A
11295- B410-64
Auto Bay Area
Black pipe dope (on galvanized water line fittings)
ND N/A
11295- B410-65
Auto Bay Area
Beige/white pipe dope (on galvanized water line fittings) ND N/A
11295- B410-66
Auto Bay Area
Black pipe dope (on galvanized water line fittings)
ND N/A
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-67 Room 9
Layer 1: Silver foil Layer 2: Black duct seam tape
ND
(All Layers)
N/A (All Layers)
11295- B410-68 Room 9
Layer 1: Silver foil Layer 2: Black duct seam tape
ND
(All Layers)
N/A (All Layers)
11295- B410-69
Auto Bay Area
Layer 1: Black asphaltic fibrous expansion joint Layer 2: Thick black asphaltic tar (between concrete slabs)
ND
(All Layers)
N/A (All Layers)
11295- B410-70
Auto Bay Area
Layer 1: Black asphaltic fibrous expansion joint Layer 2: Thick black asphaltic tar (between concrete slabs)
ND
(All Layers)
N/A (All Layers)
11295- B410-71
Auto Bay Area
Layer 1: Black asphaltic fibrous expansion joint Layer 2: Thick black asphaltic tar (between concrete slabs)
ND
(All Layers)
N/A (All Layers)
11295- B410-72
Exterior East Side
White window trim caulking w/ paint (on windows and building trim throughout east, north and west sides)
ND N/A
11295- B410-73
Exterior South Side
Beige window trim caulking w/ paint (on windows and doors throughout south side)
ND N/A
11295- B410-74
Exterior South Side
Beige door frame caulking w/ paint (on windows and doors throughout south side) w/ paint
ND N/A
11295- B410-75
Exterior West Side
Layer 1: Beige/white building trim caulking w/ paint (on windows and building trim throughout north, east and west sides) Layer 2: Wood trim debris
ND
(All Layers)
N/A (All Layers)
11295- B410-
76QA
Exterior South Side
Layer 1: White/gray duct seam sealant w/ debris Layer 2: Silver material
ND
(All Layers)
N/A (All Layers)
11295- B410-77
Exterior South Side
Clear/tan AHU seam sealant w/ paint
ND N/A
11295- B410-
78QA
Exterior South Side
Silver/gray AHU seam sealant w/ paint ND N/A
11295- B410-79
Exterior South Side
Black rubber flex duct (to AHU) 39”x1’6”
ND N/A
11295- B410-80
Exterior South Side
Black pipe dope w/ paint (on natural gas line fitting) ND N/A
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-81
Exterior South Side
Black pipe dope w/ paint (on natural gas line fitting) ND N/A
11295- B410-82
Exterior South Side
Tan natural gas meter gasket w/ paint (12”x12” on meter) ND N/A
11295- B410-83
Exterior South Side
6” OD Black regulator gasket w/ paint (on natural gas line)
ND N/A
11295- B410-84
Exterior South Side
Layer 1: White/off-white duct seam sealant Layer 2: Wood debris (on ducting to AHU)
ND
(All Layers)
N/A (All Layers)
11295- B410-85
Exterior South Side
Silver/gray AHU seam sealant (on AHU)
ND N/A
11295- B410-
86QA
Attic Above Auto Bays
Layer 1: White/off-white fibrous duct seam tape w/ paint Layer 2: Dried white mastic Layer 3: Clear yellow/white sealant (on all duct seams in attic)
ND
(All Layers)
N/A (All Layers)
11295- B410-87
Attic Above Auto Bays
Layer 1: White/off-white fibrous duct seam tape w/ paint Layer 2: Dried white mastic Layer 3: Clear yellow sealant (on all duct seams in attic)
ND
(All Layers)
N/A (All Layers)
11295- B410-88
Attic Above Auto Bays
Layer 1: White/off-white fibrous duct seam tape w/ paint Layer 2: Dried white mastic Layer 3: Clear yellow sealant (on all duct seams in attic)
ND
(All Layers)
N/A (All Layers)
11295- B410-89
Attic Above Auto Bays
Layer 1: Red duct hatch sealant (1’x1’) Layer 2: White/off-white fibrous duct seam tape Layer 3: Dried white mastic Layer 4: Clear/yellow mastic
ND
(All Layers)
N/A (All Layers)
11295- B410-90
Attic Above Auto Bays
Red duct hatch sealant (on 1’x1’ hatch) ND N/A
11295- B410-91
Attic Above Auto Bays
Red duct hatch sealant (on 1’x1’ hatch)
ND N/A
11295- B410-92
Attic Above Auto Bays
Layer 1: Black asphaltic composite roofing w/ red granules and mica Layer 2: Black asphaltic vapor barrier Layer 3: Black asphaltic vapor barrier (debris throughout)
ND
(All Layers)
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-93
Attic Above Auto Bays
Layer 1: Black asphaltic composite roofing w/ red granules and mica Layer 2: Thick black asphaltic felt vapor barrier
ND
(All Layers)
N/A (All Layers)
11295- B410-94
Attic Above Auto Bays
Layer 1: Black asphaltic paper vapor barrier Layer 2: Black asphaltic paper vapor barrier
ND
(All Layers)
N/A (All Layers)
11295- B410-95
West Attic Space
New white fibrous fabric vapor barrier (on wood siding on south wall only)
ND N/A
11295- B410-96
East Attic Space
New white fibrous fabric vapor barrier (on wood siding on south wall only)
ND N/A
11295- B410-97
Auto Bay Area
Layer 1: Silver foil w/ mastic Layer 2: Brown/tan paper vapor barrier w/ black mastic Layer 3: Off-white fiberglass batt insulation (between wood framing and wood siding) Layer 4: Trace wood debris
ND
(All Layers)
N/A (All Layers)
11295- B410-
98QA
Auto Bay Area
Layer 1: Black plastic vapor barrier Layer 2: Brown/tan paper vapor barrier Layer 3: Black plastic vapor barrier (behind wood siding)
ND
(All Layers)
N/A (All Layers)
11295- B410-99
Roof East Side
Layer 1: Black asphaltic composite roofing w/ granules Layer 2: Black asphaltic tar Layer 3: Black asphaltic composite roofing w/ granules Layer 4: Black asphaltic tar Layer 5: Black asphaltic vapor barrier (on wood)
ND
(All Layers)
N/A (All Layers)
11295- B410-100
Roof Southwest corner Thick black asphaltic tar/sealant ND N/A
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11295- B410-101
Roof Southwest corner
Layer 1: Black asphaltic composite roofing w/ granules Layer 2: Trace black asphaltic tar Layer 3: Black asphaltic composite roofing w/ granules Layer 4: Black asphaltic tar Layer 5: Black asphaltic composite roofing w/ granules Layer 6: Black asphaltic tar Layer 7: Trace wood debris
ND
(All Layers)
N/A (All Layers)
11295- B410-102
Roof West Side
Layer 1: Black asphaltic composite roofing w/ granules Layer 2: Trace black asphaltic tar Layer 3: Black asphaltic composite roofing w/ granules Layer 4: Black asphaltic tar Layer 5: Black asphaltic composite roofing w/ granules Layer 6: Black asphaltic tar (on wood)
ND
(All Layers)
N/A (All Layers)
11295- B410-103
Toilet Room
Black rubber sink drain gasket ND N/A
KEY: AHU = air handling unit, CMU = concrete masonry unit, GWB = gypsum wall board, JC = joint compound, ND = non-detect, N/A = not applicable, OD = outside diameter, OSB = oriented strand board SACT = suspended acoustic ceiling tile, SB = small-bore, SVF = sheet vinyl flooring, TSI = Thermal system insulation, VCT = vinyl composite tile, w/ = with x When the reported concentrations differ between primary and QA laboratory results, EHSI reports the most conservative (e.g., highest asbestos concentration) result.
Table 2 summarizes materials identified by EHSI as containing greater than 1% asbestos fibers during its survey, and un-sampled materials assumed to be ACM. The Table 2 Summary of Asbestos Containing Materials is for engineering cost estimating purposes and is not intended for bid quantifications.
TABLE 2
SUMMARY OF ASBESTOS-CONTAINING MATERIALS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 410
ASBESTOS MATERIAL DESCRIPTION LOCATION QUANTITY
Non-ACM 12”x12” beige/tan VCT (w/ brown and off-white streaks) on ACM black mastic on gray paint (on concrete) [Sample #s 11295-B410-44, 45 and 46]
Rooms 2, 3, 4, 6, 11, 12, and Corridor 8
1,200 SF
TABLE 2
SUMMARY OF ASBESTOS-CONTAINING MATERIALS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 410
ASBESTOS MATERIAL DESCRIPTION LOCATION QUANTITY
Non-ACM 12”x12” brown/tan VCT (w/ brown and beige streaks) on ACM black mastic on painted (on concrete) [Sample #s 11295-B410-44, 45 and 46]
Room 7 and Corridor 8
600 SF
Non-ACM 12”x12” beige/tan VCT (w/ brown and off-white streaks) on ACM black mastic on OSB [Sample #s 11295-B410-46]
2nd Floor Room 2-1, 2-2, 2-3 and 2-4
225 SF
Non-ACM beige SVF (w/ broken rock pattern) on ACM off-white/gray paper backing w/ACM beige mastic and black mastic on concrete [Sample # 11295-B410-53]
Toilet Room 10 160 SF
Non-ACM red/brown rubber stair tread on ACM brown mastic on wood stair tread [Sample # 11295-B410-55]
Stairs 80 SF
Metal fire door w/ 1’x1’ window w/ assumed ACM core Auto Bay Area 1 4 EA
Metal fire door w/ assumed ACM core
Auto Bay Area 1, Room 9, Corridor 8 and 2nd Floor Room 2-1
6 EA
Small electrical panels w/ assumed ACM internal components (<1 SF in size)
Corridor 8 2 EA
Electrical panels w/ assumed ACM internal components (1-6 SF in size)
Corridor 8 2nd Floor Room 2-1
2 EA
Small electrical disconnect w/ assumed ACM internal components (<1 SF in size) (associated w/ rollup doors and heating system)
Auto Bay Area 1 8 EA
Small electrical disconnect w/ assumed ACM internal components (<1 SF in size) Room 9 1 EA
Electrical disconnect/control panel w/ assumed ACM internal components (1-6 SF in size)
Auto Bay Area 1 1 EA
5’x4 ½’x3 ¾’ AHU w/ assumed ACM internal components
Exterior, south side of building
1 EA
Assumed ACM tar/sealant around 1’x1 vent hood Roof 2 EA Assumed ACM tar/sealant around 1’ OD vent Roof 3 EA Assumed ACM tar/sealant around 2’x2’ Mushroom shaped vent Roof 2 EA
Assumed ACM tar/sealant around lead vent pipe Roof 3 EA KEY: ACM = asbestos containing material, OD = outer diameter, OSB = oriented strand board, SF = square feet, SVF = sheet vinyl flooring, VCT = vinyl composite tile, w/ = with
ACM identified in this survey should not be disturbed unless handled by personnel who are properly trained and certified in asbestos work. Demolition and/or renovation activities by contractors may expose concealed suspect ACM. Contractors should be aware of the potential for concealed suspect ACM and have pre-planned contingencies for the handling of suspect ACM discovered during renovation and/or demolition work. Any concealed suspect ACM material that was not sampled or was assumed to be ACM and included in this report, must be treated as ACM until proven otherwise by a Certified AHERA Building Inspector and a certified laboratory. Contingency plans should include stopping work on identification of concealed suspect ACM, evacuation of the area, and sampling by a Certified AHERA Building Inspector. Concealed suspect material may include, but is not limited to: spray-applied coatings, asphalt or paper vapor barriers and mastics.
2.4.2 Lead-Containing Paint and Building Materials
Eighty (80) samples were analyzed for lead using the X-Ray fluorescence (XRF) analyzer.
Results marked with “<LOD” are less than the limit of detection. XRF sample results ranged from 31.4 milligrams of lead per square centimeter (mg Pb/cm2) to < LOD. Items in Tables 3 and 4 that are bolded in red font will trigger a negative exposure assessment and lead awareness training per WAC 296-155-17609.
Table 3 summarizes XRF lead samples, including sample number, material description, substrate, color, location and analytical results.
TABLE 3
XRF SAMPLING
SUMMARY OF PAINTED COMPONENTS AND MATERIALS
VANCOUVER BARRACKS – BUILDING 410
Read # Component Substrate Color Floor Room
Lead Conc.
(mg/cm2)
1 SELF-
CALIBRATION
N/A N/A N/A N/A 2.26
2 CALIBRATION N/A RED N/A N/A 1.0
3 CALIBRATION N/A RED N/A N/A 0.9
4 CALIBRATION N/A RED N/A N/A 1.0
5 WALL WOOD WHITE FIRST 1 < LOD
6 WALL TRIM WOOD WHITE FIRST 1 < LOD
7 DOOR TRIM WOOD WHITE FIRST 1 < LOD
8 DOOR FRAME METAL LIGHT BLUE FIRST 1 < LOD
9 DOOR METAL LIGHT BLUE FIRST 1 < LOD
10 BEAM WOOD WHITE FIRST 1 < LOD
11 COLUMN WOOD WHITE FIRST 1 3.8
12 WINDOW WOOD LIGHT BLUE FIRST 1 5.5
13 WINDOW TRIM WOOD LIGHT BLUE FIRST 1 < LOD
14 DOOR METAL LIGHT BLUE FIRST 1 < LOD
15 DOOR FRAME METAL LIGHT BLUE FIRST 1 < LOD
16 WALL WOOD WHITE FIRST 1 < LOD
17 WALL WOOD WHITE FIRST 1 < LOD
18 DOOR METAL LIGHT BLUE FIRST 1 < LOD
19 DOOR FRAME METAL LIGHT BLUE FIRST 1 < LOD
20 CEILING WOOD WHITE FIRST 1 < LOD
21 FLOOR
STRIPPING
CONCRETE YELLOW FIRST 1 4.3
SERVICE
WINDOW METAL LIGHT BLUE FIRST 1 < LOD
23 DOOR METAL BLUE FIRST 1 < LOD
XRF SAMPLING
SUMMARY OF PAINTED COMPONENTS AND MATERIALS
VANCOUVER BARRACKS – BUILDING 410
Read
Component Substrate Color Floor Room Lead Conc.
(mg/cm2)
ELECTRICAL
PANEL
METAL GRAY FIRST 1 < LOD
25 LIGHT FIXTURE METAL WHITE FIRST 1 < LOD
FIRST AID
CABINET
WOOD GREEN FIRST 1 2.7
27 WALL WOOD OFF-WHITE FIRST 11 3.9
28 WALL WOOD BLUE FIRST 11 0.23
29 DOOR WOOD BLUE FIRST 11 7.2
30 DOOR TRIM WOOD BLUE FIRST 11 6.5
31 WINDOW WOOD BLUE FIRST 11 4.4
32 WINDOW SILL WOOD BLUE FIRST 11 4.2
33 WINDOW TRIM WOOD BLUE FIRST 11 6
34 WINDOW WOOD BLUE FIRST 12 < LOD
35 WINDOW WOOD WHITE FIRST 12 < LOD
36 DOOR TRIM WOOD BLUE FIRST 12 0.8
37 CEILING WOOD WHITE FIRST 12 5.0
38 WALL DRYWALL OFF-WHITE FIRST 10 < LOD
39 SINK CERAMIC WHITE FIRST 10 31.4
40 TOILET CERAMIC WHITE FIRST 10 0.7
41 DOOR TRIM WOOD OFF-WHITE FIRST 10 < LOD
42 DOOR METAL OFF-WHITE FIRST 10 < LOD
43 DOOR METAL OFF-WHITE FIRST 10 < LOD
44 STALL METAL BEIGE FIRST 10 < LOD
HOT WATER
TANK
METAL WHITE FIRST 10 < LOD
HOT WATER
TANK
METAL BLUE FIRST 10 < LOD
HOT WATER
TANK METAL BLUE FIRST 10 < LOD
48 WALL CONCRETE WHITE FIRST 10 < LOD
49 WALL DRYWALL WHITE FIRST 10 < LOD
50 WALL DRYWALL WHITE FIRST 7 < LOD
51 WINDOW WOOD WHITE FIRST 7 < LOD
52 DOOR TRIM WOOD WHITE FIRST 7 < LOD
53 DOOR WOOD WHITE FIRST 7 < LOD
54 COLUMN WOOD WHITE FIRST 7 9.0
55 WALL DRYWALL OFF-WHITE FIRST 8 < LOD
56 DOOR METAL BEIGE FIRST 8 0.04
57 WINDOW GUARD METAL OFF-WHITE FIRST 4 < LOD
ELECTRICAL
PANEL
METAL OFF-WHITE FIRST 8 < LOD
59 FA PANEL METAL RED FIRST 8 < LOD
60 WALL DRYWALL OFF-WHITE FIRST 3 < LOD
61 DOORFRAME WOOD OFF-WHITE FIRST 2 < LOD
62 WALL CONCRETE OFF-WHITE FIRST 5 < LOD
63 SLOP SINK METAL WHITE FIRST 5 21.1
64 DOOR METAL OFF-WHITE FIRST STAIRS < LOD
XRF SAMPLING
SUMMARY OF PAINTED COMPONENTS AND MATERIALS
VANCOUVER BARRACKS – BUILDING 410
Read
Component Substrate Color Floor Room Lead Conc.
(mg/cm2)
65 DOORFRAME METAL LIGHT BLUE FIRST STAIRS < LOD
66 DOORFRAME METAL LIGHT BLUE FIRST 9 < LOD
67 WALL DRYWALL OFF-WHITE FIRST 9 < LOD
ELECTRICAL
PANEL
METAL GRAY FIRST 9 < LOD
69 STAIR STRINGER WOOD WHITE FIRST STAIRS 6.0
70 NEWEL POST WOOD WHITE FIRST STAIRS 0.13
71 NEWEL POST WOOD WHITE FIRST STAIRS 0.24
72 RAILING WOOD WHITE FIRST STAIRS 0.18
73 WALL WOOD WHITE FIRST STAIRS < LOD
74 RAILING WOOD WHITE SECOND 2-1 0.08
75 POST_COLUMN WOOD WHITE SECOND 2-1 0.08
76 DRAIN PIPE METAL WHITE SECOND 2-1 0.04
77 WALL WOOD WHITE SECOND 2-1 4.6
78 CEILING WOOD WHITE SECOND 2-1 5.1
79 WINDOW TRIM WOOD LIGHT GREEN SECOND 2-1 0.6
80 WINDOW WOOD LIGHT GREEN SECOND 2-1 < LOD
81 DOOR METAL GREEN SECOND 2-1 < LOD
82 WALL DRYWALL WHITE SECOND 2-3 < LOD
83 TRIM WOOD WHITE SECOND 2-3 < LOD
ACCESS HATCH
AND FRAME
METAL RED SECOND ATTIC WEST < LOD
85 CALIBRATION N/A RED N/A N/A 1.0
86 CALIBRATION N/A RED N/A N/A 1.0
87 CALIBRATION N/A RED N/A N/A 0.9
Key: N/A = not applicable, <LOD = less than limit of detection
All XRF sample shots are representative of that color on that specific substrate and component.
The report user shall deduce from the data in Table 3, if certain building materials throughout the entire building contain lead and should not assume that what is detected is only in the specific location identified in the Table.
In addition to the XRF samples, EHSI collected two (2) bulk QA samples for laboratory analysis. The bulk sample results ranged from less than the reporting limit (<RL) to 0.046 percent lead by weight (%Pb/wt.). Building materials and paint containing detectable levels of lead are considered regulated by DOSH.
Table 4 summarizes bulk QA lead sample, including sample number, material description, substrate, color, location, and analytical results. Copies of the analytical laboratory report and field data forms for lead paint are included in Appendix B of this report.
TABLE 4
SUMMARY OF LEAD BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 410
SAMPLE
NUMBER
LOCATION COMPONENT/
SUBSTRATE
COLOR
RESULTS
% Pb by
WT
11295-B410-
Pb01 1st Floor, Auto Bay Area
Support Beam / Wood Off-white 0.046
11295-B410- Pb02
1st Floor, Custodial Closet Room 5
Wall / CMU & Mortar Beige on Gray on
Gray <0.0035
Key: CMU = concrete masonry unit, Pb = lead, WT = weight
L&I DOSH requires employers to conduct a hazard assessment and take appropriate worker protection precautions whenever disturbing materials that have detectable quantities of lead.
Since the type of work planned (e.g., sawing, grinding, select demolition) may likely disturb the lead-containing materials, the contractor will need to conduct lead awareness training and perform an initial exposure assessment in accordance with the regulations.
In addition to XRF and bulk samples, EHSI observed two (2) lead-acid batteries inside the fire alarm control panel in Corridor 8 and three (3) lead vent pipes on the roof during the inspection.
These batteries must be disposed of in accordance with the Washington State Department of Ecology (Ecology) dangerous waste regulations or recycled at an approved facility.
2.4.3 Toxicity Characteristic Leaching Procedure Sampling
At the request of NPS, EHSI accomplished TCLP sampling and analysis of the assumed waste stream for the project and Table 5 summarizes the analytical results. EHSI collected and composited a representative sample of the assumed waste stream for renovation activities that may impact interior building finishes, that included proportionate quantities of all materials expected to be included in the waste stream. Note: Painted metals were not included in the assumed waste stream sampling, because they are expected to be recycled and because there is no limit on metals containing paint on metals being recycled.
Ecology requires testing using the “toxicity characteristic leaching procedure” (TCLP) and segregation of construction debris if it is potentially contaminated with dangerous waste (e.g., hazardous metals-containing paint/hazardous metals-containing materials). Ecology has set a dangerous waste threshold at 5.0 milligrams per liter (mg/L), for arsenic, chromium, lead, and silver, 1.0 Mg/L for cadmium, 100 mg/L for barium and .2 mg/L for mercury.
The TCLP sample for the Project was analyzed for Lead (Pb) only. Copies of the analytical laboratory report and field data forms for the TCLP sample are included in Appendix C of this report.
TABLE 5
SUMMARY OF TCLP SAMPLING AND ANALYTICAL RESULTS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 410
Sample # Elements RL in mg/L Results in mg/L
Results in ppm
11295- B410-
TCLP-01
Sample Description:
40% Composite roofing;
28% Painted “Orange Peel” texturing on GWB walls w/ wood framing;
10% 12”x12” Beige VCT;
5% Painted wood siding;
5% Painted 2’x4’ SACT;
4% 12”x12” Brown VCT;
2% Painted wood wall panels;
2% Newer 12”x12” Beige VCT;
1% 4” Black cove base;
1% Beige SVF;
1% Red/brown stair tread; and 1% Old 4” Dark brown/black cove base
Lead (Pb) 0.5 1.1 1.1 KEY: GWB = gypsum wall board, mg/L = milligram per liter, Pb = Lead, ppm = part per million, RL = Reporting Limit, SACT = suspended acoustic ceiling tile, SVF = sheet vinyl flooring, VCT = vinyl composite tile, w/ = with
Based on the representative waste stream that was submitted for TCLP by EHSI, this waste stream passed TCLP testing for lead (did not exceed the threshold of 5.0 ppm). If the client were to have a waste stream with similar percentages as indicated above, the waste stream would likely pass.
It should be noted that this TCLP was done on behalf of NPS for disposal cost estimating purposes. It is recommended that the contractor take their own TCLP test of their demolition waste stream including the option to not TCLP specific materials based on the ability to recycle metal and concrete painted building materials.
2.4.4 Ionizing Radiation
Ionizing Radiation Above Background (As…
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