Attachment 3i - B754 Limited Hazardous Materials Survey Report.pdf
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This Request for Proposals (RFP) solicits abatement of hazardous materials and associated demolition and repairs at historic buildings within Fort Vancouver National Historic Site. The National Park Service seeks to abate asbestos, lead, mercury, polychlorinated biphenyls, and wildlife excrement across multiple buildings. Offerors must provide payment and performance bonds as well as liability insurance, and work will be performed under a firm-fixed-price construction contract adhering to Davis-Bacon wage requirements. The small business set-aside project has an estimated value between $250,000 and $1,000,000 depending on optional items. The solicitation package is available through SAM.gov, with technical and price proposals due on specified dates. The award will be made using best value tradeoff.
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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
East Vancouver Barracks Building 754
Vancouver, Washington 98661
December 24th, 2018
Prepared For:
Kristen Jontos 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 754, Vancouver, Washington 98661
EHSI Project No.: # 11176
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
NATIONAL PARK SERVICE
FORT VANCOUVER NATIONAL HISTORIC SITE
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
2.4 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 ... 14
2.4.4 Polychlorinated Biphenyls
2.4.5 Mercury-Containing Fluorescent Light Tubes, CFL Bulbs, and thermostats
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 Laboratory Reports and Field Data Forms C ........................ Certified AHERA Building Inspector Certificates D ........................ Laboratory Certifications for Asbestos and Lead Analysis
E ......................... Sample Location Drawings for Asbestos and Lead F ......................... Hazardous Metals TCLP Laboratory Reports and Field Data Forms iv
ACRONYM LIST
ACM .......................Asbestos-Containing Material
Ag ..........................Silver
AHERA ....................Asbestos Hazard Emergency Response Act
AHU .......................Air Handling unit
AIHA ......................American Industrial Hygiene Association
As ..........................Arsenic
Ba ..........................Barium
Cd ..........................Cadmium
CFL ........................Compact Fluorescent Light
CFR ........................Code of Federal Regulations
Cr ..........................Chromium
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
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
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 – B754
EHSI Project 11176
1.0 EXECUTIVE SUMMARY
1.1 BACKGROUND
The National Park Service (NPS) plans to renovate Building 754 (B754) at the Fort Vancouver
National Historic Site (FV NHS) located in Vancouver, Washington. The NPS has contracted
EHS-International, Inc. (EHSI), a hazardous materials and industrial hygiene consulting firm, to conduct a Hazardous Materials Survey of B754 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.
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. EHSI accomplished a representative destructive inspection; however, in areas inaccessible for inspection (e.g., energized electrical equipment and mirror mastics) suspect materials were assumed to be
ACM.
1.3 ACM MATERIALS FOUND
SUMMARY OF ASBESTOS-CONTAINING MATERIALS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 754
ASBESTOS MATERIAL DESCRIPTION
LOCATION
Non-ACM 12” x 12” tan VCT (w/ beige and brown streaks) on ACM black mastic (on concrete)
[Sample #181 and 182]
Throughout
ACM black compressor motor gaskets (in ACU)
[Sample #229] Exterior, S.W. Side
Fridge/freezer w/ assumed ACM wall insulation and door core
(12’x16’x8’) N.W. Section
Wood IT panel box w/ assumed ACM mastic Manager Office
29” x 23.5” Mail box w/ assumed ACM mastic Manager Office
2’ x 2.5” Mirror w/ assumed ACM mastic Toilet
8” x 14” Mirror w/ assumed ACM mastic Receiving
1’ x 1’ x 10” Heater w/ assumed ACM internal components Storage
SUMMARY OF ASBESTOS-CONTAINING MATERIALS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 754
ASBESTOS MATERIAL DESCRIPTION
LOCATION
Small Electrical panel w/ assumed ACM internal components (1 square feet {SF} – 5 SF in size) Storage
Electrical panel w/ assumed ACM internal components (1 square feet {SF} – 5 SF in size) Storage
4” OD Electrical mast w/ assumed ACM roof penetration sealant Roof, N. Corner
3’ OD Attic vents w/ assumed ACM roof penetration sealant Roof, Throughout
2’ x 2’ Chimney w/ assumed ACM roof penetration sealant Roof, S.E. Section
4” OD drain vent pipe w/ assumed ACM roof penetration sealant Roof, S.W. Side
KEY: ACM = asbestos containing material, ACU = air conditioning unit, EA = each, SF = square feet, 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.
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 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).
73% 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.
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 and mirror mastics 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, and to provide analytical reports indicating the presence and quantity of the hazardous materials.
On September 13th, 2018, 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 (SWAA).
2.2 BUILDING DESCRIPTION
Building 754 is located at East Vancouver Barracks, Vancouver, Washington. The building was constructed in 1909 and is a single-story wood-framed concrete structure with an attic. The building sits on a concrete footing foundation. The building’s roof is covered with 3-tab composite shingles. Interior floor finishes include: vinyl composite tile (VCT) and bare concrete floors. Interior wall finishes include: gypsum wallboard (GWB) walls and textured concrete walls. Interior ceiling finishes include: suspended acoustical ceiling tiles (SACT) and wood ceiling decking. Windows throughout the building are operable and wood-framed.
Heating is provided by an air handing unit (AHU) located in the attic and a unit heater in the northwest storage room. Air conditioning and refrigeration is provided by exterior air conditioning units (ACUs). Hot water is provided by an electric domestic hot water tank located in the attic. Interior lighting consists of incandescent and fluorescent ceiling fixtures and natural light from the windows.
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
C. 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). Only materials containing more than 1% total asbestos were classified as “asbestos-containing” based on USEPA, state, and local regulations.
Samples in the report labeled as ##QA are quality assurance (QA) samples. Split samples were taken from the same location and they were sent to separate laboratories. QA samples were submitted to, NVL Laboratories, Inc. (NVL) in Seattle, WA, another NVLAP laboratory.
Copies of both laboratories’ NVLAP certifications are included in Appendix D.
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 and 4, 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.
2.4 SAMPLING RESULTS
2.4.1 Asbestos-Containing Materials
Forty-nine (49) bulk samples of suspect ACM were collected as part of the survey. Three (3) of those samples were split for quality assurance analyses. 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 and lead sample location drawings are provided in Appendix E. 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. Suspect materials not sampled were assumed to be ACM.
TABLE 1
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 754
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11176-181
1st Floor, Retail
Space
Layer 1: 12” x 12” Tan VCT (w/ beige and brown streaks)
Layer 2: Black mastic (on concrete)
L1: ND
L2: 2%
N/A
Chrysotile
11176-182
1st Floor, Retail
Space, N.E.
Corner
Layer 1: 12” x 12” Tan VCT (w/ beige and brown streaks)
Layer 2: Black mastic (on concrete)
L1: ND
L2: 2%
Chrysotile
11176-183
1st Floor, Retail
Space, N.W.
Corner
Layer 1: 2” x 5’ Reddish brown threshold floor tile
Layer 2: Trace clear/yellow mastic (on concrete)
ND
(All Layers)
N/A
(All Layers)
11176-184
1st Floor, Retail
Space, N.E.
Corner
Layer 1: 4” Brown cove base
Layer 2: Orange/tan mastic
ND
(All Layers)
N/A
(All Layers)
11176-185
1st Floor, Retail
Space, N.E.
Corner
Layer 1: 4” Brown cove base
Layer 2: Orange/tan mastic
ND
(All Layers)
N/A
(All Layers)
11176-186 1st Floor, Receiving
White caulking/putty (along wall at old wall location)
ND N/A
11176-187 1st Floor, Receiving
Gray coating/texturing w/ paint on concrete wall
ND N/A
11176-188 1st Floor, Receiving
Beige coating/texturing w/ paint on concrete wall
ND N/A
11176-189 1st Floor, Storage
Gray coating/texturing w/ paint on concrete wall
ND N/A
11176-190 1st Floor, Storage
Beige coating/texturing w/ paint on concrete wall
ND N/A
11176-191
1st Floor, Secure
Storage
Beige coating/texturing w/ paint on concrete wall
ND N/A
11176-192 1st Floor, Storage
Gray coating/texturing w/ paint on concrete wall
ND N/A
11176-193 1st Floor, Vestibule
Layer 1: Reddish brown threshold tile
Layer 2: Black fibrous concrete seam filler w/ black asphaltic tar
ND
(All Layers)
N/A
(All Layers)
11176-194 1st Floor, Storage
Layer 1: JC w/ paint
Layer 2: GWB wall w/ paper
(corner)
ND
(All Layers)
(All Layers)
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 754
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11176-195
1st Floor, Manger’s
Office
Layer 1: JC w/ paint
Layer 2: GWB wall w/ paper
(corner)
ND
(All Layers)
N/A
(All Layers)
11176-196 1st Floor, Toilet
GWB wall w/ paint and paper
(mid-wall)
ND N/A
11176-197
1st Floor, Manager’s
Office
GWB wall w/ paint and paper
(mid-wall)
ND N/A
11176-198
1st Floor, Retail
Space
GWB wall w/ paint and paper
(mid-wall)
ND N/A
11176-199 Attic
Blown-in fluffy white insulation w/ glass beads (only over storage and fridge/freezer area)
ND N/A
11176-200 Attic
Blown-in fluffy white insulation w/ glass beads (only over storage and fridge/freezer area)
ND N/A
11176-201 Attic
Layer 1: Black asphaltic paper vapor barrier
Layer 2: Yellow fiberglass insulation (on attic hatch)
ND
(All Layers)
N/A
(All Layers)
11176-202 Attic 3’ x 5’ White/black rubber fibrous flex duct
ND N/A
11176-203 Attic Gray duct seam sealant ND N/A
11176-204 Attic Gray duct seam sealant ND N/A
11176-205 Attic
Layer 1: Silver foil
Layer 2: Brown/tan paper vapor barrier w/ mastic
Layer 3: Yellow fiberglass insulation (on supply ducting)
ND
(All Layers)
N/A
(All Layers)
11176-206 Attic
Layer 1: White/beige paint/coating
Layer 2: Black asphaltic coating on black fibrous wire wrap
Layer 3: Black rubber insulation
(on knob and tube)
Layer 4: Metal
ND
(All Layers)
N/A
(All Layers)
11176-207 Attic
Layer 1: Black asphaltic coating on black fibrous wire wrap
Layer 2: Black rubber insulation
(on knob and tube wiring)
Layer 3: Metal
ND
(All Layers)
N/A
(All Layers)
11176-
208QA
Attic
Black asphaltic paper vapor barrier with tan mastic
(between roof deck and roofing)
ND N/A
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 754
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11176-209 Attic
Black asphaltic paper vapor barrier (between roof deck and roofing)
ND N/A
11176-210 Attic
Layer 1: Red brick
Layer 2: Gray mortar (on old chimney above ceiling)
ND
(All Layers)
N/A
(All Layers)
11176-211
1st Floor, Retail
Space, N.E.
Corner
2’ x 4’ Beige/gray SACT w/ white paint (w/ small worm track and pinhole pattern, patch tiles)
ND N/A
11176-212
1st Floor, Manager’s
Office
2’ x 4’ Beige/gray SACT w/ white paint (w/ worm track and pinhole pattern)
ND N/A
11176-213
1st Floor, Retail
Space
2’ x 4’ Beige/gray SACT w/ white paint (w/ worm track and pinhole pattern)
ND N/A
11176-214
1st Floor, Retail
Space
2’ x 4’ Beige/gray SACT w/ white paint (w/ deep worm track pattern, patch tile)
ND N/A
11176-215
1st Floor, Retail
Space
2’ x 4’ Beige/gray SACT w/ white paint (w/ light worm track pattern, patch tile)
ND N/A
11176-216 1st Floor, Hall
Layer 1: White caulking w/ paint
Layer 2: Trace JC w/ paper (on drinking fountain and sink)
ND
(All Layers)
N/A
(All Layers)
11176-217 1st Floor, Toilet
Layer 1: Black sink drain gasket
Layer 2: Brown plumber’s putty
ND
(All Layers)
N/A
(All Layers
11176-2181
1st Floor, Exterior
N.E. Side
Gray window glazing putty patch w/ paint (on 3’ x 4’6” wood-framed windows)
0.75% Chrysotile
11176-219
1st Floor, Exterior
N.E. Side
Tan window glazing putty patch w/ paint (on 3’ x 4’6” wood-framed windows)
ND N/A
11176-220
1st Floor, Exterior
S.W. Side
Tan window glazing putty patch w/ paint (on 3’ x 4’6” wood-framed windows)
ND N/A
SUMMARY OF ASBESTOS BULK SAMPLING AND ANALYTICAL RESULTS
FORT VANCOUVER BARRACKS – BUILDING 754
SAMPLE
NUMBER
SAMPLE
LOCATION
MATERIAL DESCRIPTION
ASBESTOS
TYPE OF
ASBESTOS
11176-
221QA Roof
Layer 1: Black asphaltic 3-tab roofing w/ granules
Layer 2: Black asphaltic tar
Layer 3: Black asphaltic 3-tab roofing w/ granules
Layer 4: Black asphaltic tar
Layer 5: Clear plastic and dark gray material
Layer 6: Black asphaltic vapor barrier
Layer 7: Black asphaltic tar
ND
(All Layers)
N/A
(All Layers)
11176-222 Roof
Layer 1: Black asphaltic 3-tab roofing w/ granules
Layer 2: Black asphaltic tar
Layer 3: Black asphaltic 3-tab roofing w/ granules
Layer 4: Black asphaltic tar
Layer 5: Clear plastic
Layer 6: Black asphaltic vapor barrier
Layer 7: Black asphaltic tar
ND
(All Layers)
N/A
(All Layers)
11176-223 Exterior, N.E. Side
Black foam pipe wrap/ insulation (on water pipe to
ACU)
ND N/A
11176-224 Exterior, S.W. Side
Trace white coating w/ paint
(on fence around 2 units)
ND N/A
11176-225 Exterior, S.W. Side
White door frame caulking w/ paint
ND N/A
11176-226 Exterior, N.E. Side
Hard white caulking (on 8” wood cove base)
ND N/A
11176-
227QA
Exterior, S.W. Side
(in AC unit)
Black asphaltic pipe wrap on black foam insulation (in ACU)
ND N/A
11176-228
Exterior, S.W. Side
(in ACU)
Black rubber pipe wrap/insulation
ND N/A
11176-229
Exterior, S.W. Side
(in ACU)
Black compressor motor gaskets 3% Chrysotile
KEY: ACU = air conditioning unit, GWB = gypsum wall board, JC = joint compound, ND = non-detect, N/A = not applicable, OD = outer diameter, SACT = suspended acoustical ceiling tile, VCT = vinyl composite tile, w/ = with
1 Point Counted Results. Preliminary analytical reports indicated that one sample contained approximately 2% chrysotile asbestos (Sample # 11176-218). EHSI re-submitted this sample reported to have greater than 1% asbestos concentration for re-analysis using the more precise
EPA “Point Count” method. The “Point Count” analytical method is recommended by the EPA for samples with less than 10% asbestos. Based on the results of that re-analysis, the material found to contain less than 1% (<1%) asbestos was determined to be a non-ACM (e.g., containing < 1% asbestos fibers) and is therefore not ACM. Materials found to contain greater than 1% asbestos are identified and quantified in Table 2 of this report. Only the “Point Count” re-analysis concentrations are listed in Table 1. Analytical results for all analyses are provided in Appendix A.
Washington State Department of Labor and Industries Division of Occupational Safety and
Health (L&I DOSH) requires special worker exposure precautions and qualifications when dealing with ACM used on seams and nail holes (refer to L&I DOSH regulations and WISHA
Regional Directives {WRD}). Any “dust creating activity”, such as: sanding, sawing, grinding, or drilling of GWB walls or ceilings shall be accomplished by certified asbestos workers using glove-bag, mini-enclosure and/or negative pressure enclosure engineering controls and work practices. As directed by WRD 23.30, for all other demolition or disturbance of GWB walls/ceilings with ACM JC, employees shall have received at least two hours of asbestos awareness training as specified L&I DOSH Instruction WAC 296-62-07722(5).
Samples containing <1% asbestos fibers are considered to be a non-ACM. Materials that contain
<1% asbestos are not regulated for disposal purpose. However, removal of <1% asbestos materials are considered an unclassified asbestos operation by DOSH. As directed by WRD
23.30, for all other demolition of materials with <1% asbestos, employees shall have received at least two hours of asbestos awareness training as specified L&I DOSH Instruction WAC
296-62-07722(5).
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 754
ASBESTOS MATERIAL DESCRIPTION LOCATION QUANTITY
Non-ACM 12” x 12” tan VCT (w/ beige and brown streaks) on ACM black mastic (on concrete)
[Sample #181 and 182]
Throughout 3,000 SF
ACM black compressor motor gaskets (in ACU)
[Sample #229]
Exterior, S.W.
Side
3 EA
Fridge/freezer w/ assumed ACM wall insulation and door core (12’x16’x8’) N.W. Section 1 EA
Wood IT panel box w/ assumed ACM mastic Manager Office 1 EA
29” x 23.5” Mail box w/ assumed ACM mastic Manager Office 1 EA
2’ x 2.5” Mirror w/ assumed ACM mastic Toilet 1 EA
8” x 14” Mirror w/ assumed ACM mastic Receiving 1 EA
1’ x 1’ x 10” Heater w/ assumed ACM internal components Storage 1 EA
TABLE 2
SUMMARY OF ASBESTOS-CONTAINING MATERIALS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 754
ASBESTOS MATERIAL DESCRIPTION LOCATION QUANTITY
Small Electrical panel w/ assumed ACM internal components (1 square feet {SF} – 5 SF in size) Storage 1 EA
Electrical panel w/ assumed ACM internal components (1 square feet {SF} – 5 SF in size) Storage 1 EA
4” OD Electrical mast w/ assumed ACM roof penetration sealant Roof, N. Corner 1 EA
3’ OD Attic vents w/ assumed ACM roof penetration sealant
Roof, Throughout
3 EA
2’ x 2’ Chimney w/ assumed ACM roof penetration sealant Roof, S.E.
Section
1 EA
4” OD drain vent pipe w/ assumed ACM roof penetration sealant Roof, S.W. Side 1 EA
KEY: ACM = asbestos containing material, ACU = air conditioning unit, EA = each, SF = square feet, OD = outer diameter, 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
Forty-one (41) samples were analyzed for lead using the X-Ray fluorescence (XRF) analyzer.
Red bolded results indicate materials containing detectable levels of lead and “lead-based paint” (e.g., >1.0 mg/cm2) as defined by USEPA regulation 40CFR745 and
Washington State Commerce regulation WAC 365-230.
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
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 754
Read
Component Substrate Color Building Room
Lead
Conc.
(mg/cm2)
1 SHUTTER CALL N/A N/A BUILDING 754 N/A 3.9
2 N/A N/A RED BUILDING 754 N/A 1
3 N/A N/A RED BUILDING 754 N/A 0.9
4 N/A N/A RED BUILDING 754 N/A 1
5 WALL CONCRETE BEIGE BUILDING 754 STORAGE ROOM < LOD
6 WALL DRYWALL BEIGE BUILDING 754 STORAGE ROOM < LOD
7 ELECTRICAL PANEL METAL GRAY BUILDING 754 STORAGE ROOM < LOD
SECURE STORAGE
STUDS
WOOD BEIGE BUILDING 754 STORAGE ROOM < LOD
9 WALL CONCRETE BEIGE BUILDING 754 STORAGE ROOM 1.2
10 CEILING WOOD BEIGE BUILDING 754 STORAGE ROOM 4.6
11 WALL DRYWALL BEIGE BUILDING 754 STORAGE ROOM < LOD
12 FA PANEL METAL RED BUILDING 754 STORAGE ROOM < LOD
13 FA PANEL DRYWALL BEIGE BUILDING 754 RETAIL SPACE < LOD
14 WALL DRYWALL BEIGE BUILDING 754 RETAIL SPACE < LOD
15 MERCH DISPLAY
WOOD FIBER
BOARD
BEIGE BUILDING 754 RETAIL SPACE < LOD
16 MERCH DISPLAY METAL BEIGE BUILDING 754 RETAIL SPACE < LOD
MERCH DISPLAY
AWNING
WOOD RED BUILDING 754 RETAIL SPACE 1
MERCH DISPLAY
AWNING
WOOD BLUE BUILDING 754 RETAIL SPACE 1
19 WALL DRYWALL BEIGE BUILDING 754 RETAIL SPACE 1
20 WALL WOOD BEIGE BUILDING 754 RETAIL SPACE < LOD
21 MERCH DISPLAY WOOD GRAY BUILDING 754 RETAIL SPACE < LOD
22 WALL DRYWALL BEIGE BUILDING 754
RETAIL SPACE
HALL
< LOD
23 WALL DRYWALL PINK BUILDING 754 MANAGER OFFICE < LOD
24 WALL DRYWALL PINK BUILDING 754 MANAGER OFFICE < LOD
25 WALL DRYWALL PINK BUILDING 754
ACCOUNTING
OFFICE
< LOD
26 WINDOW WOOD WHITE BUILDING 754
ACCOUNTING
OFFICE
9.8
WINDOW
TRIM_SILL
WOOD CLEAR BUILDING 754
ACCOUNTING
OFFICE
< LOD
28 WALL DRYWALL WHITE BUILDING 754
ACCOUNTING
OFFICE
< LOD
BASEBOARD
HEATER
METAL TAN BUILDING 754
ACCOUNTING
OFFICE
< LOD
TABLE 3
XRF SAMPLING
SUMMARY OF PAINTED COMPONENTS AND MATERIALS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 754
Read
Component Substrate Color Building Room
Lead
Conc.
(mg/cm2)
30 DOORFRAME WOOD CLEAR BUILDING 754 MANAGER OFFICE < LOD
31 DOOR WOOD CLEAR BUILDING 754 MANAGER OFFICE < LOD
32 WALL DRYWALL BEIGE BUILDING 754 VESTIBULE < LOD
33 WALL DRYWALL BEIGE BUILDING 754 VESTIBULE < LOD
34 TRIM WOOD CLEAR BUILDING 754 RETAIL < LOD
35 WALL CONCRETE BEIGE BUILDING 754 STORAGE 5
36 WINDOW INFILL WOOD BEIGE BUILDING 754 STORAGE < LOD
37 WALL PANEL WOOD BEIGE BUILDING 754 STORAGE 0.4
38 CONDUIT METAL BEIGE BUILDING 754 STORAGE < LOD
39 N/A N/A RED BUILDING 754 N/A 1
40 N/A N/A RED BUILDING 754 N/A 0.9
41 N/A N/A RED BUILDING 754 N/A 1
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 and 4, 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. Building materials and paint containing detectable levels of lead are considered regulated by DOSH.
Table 4 summarizes bulk QA lead samples, 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
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 754
SAMPLE
NUMBER
LOCATION
COMPONENT/
SUBSTRATE
COLOR
RESULTS
% Pb by WT
11176-Pb05 1st Floor, Storage Chimney Remnant Mortar Gray .0036
11176-Pb06 1st Floor, Attic Chimney / Brick & mortar Red & gray <.0030 Key: Pb = lead
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, demolition) may 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.
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 (mg/L), per liter 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 assumed waste stream was analyzed for the USEPA RCRA 8 metals: Lead (Pb), Cadmium (Cd), Chromium (Cr), Silver (Ag), Arsenic (AS), Barium (Ba), Mercury (hg), and Selenium (Se).
TABLE 5
SUMMARY OF TCLP SAMPLING AND ANALYTICAL RESULTS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 754
Sample # Elements RL in mg/L Results in mg/L Results in ppm
11176-
TCLP-
B754-01
Sample Description:
• 41% Painted GWB walls;
• 28% 12”x12” VCT;
• 28% painted 2’x4’ SACT; and
• 3% painted 4” cove base
Silver (Ag) 0.20 <0.20 <0.20
Arsenic (As) 0.20 <0.20 <0.20
Barium (Ba) 0.20 0.33 0.33
Cadmium (Cd) 0.20 <0.20 <0.20
Chromium (Cr) 0.20 <0.20 <0.20
Mercury (Hg) 0.01 <0.011 <0.011
Lead (Pb) 0.20 <0.20 <0.20
Selenium (Se) 0.20 <0.20 <0.20
KEY: Ag = silver, As = Arsenic, Ba = Barium, Cd = Cadmium, Cr = Chromium, GWB = gypsum wall board, Hg = Mercury, mg/L = milligram per liter, Pb = Lead, ppm = part per million, RL = Reporting Limit, SACT = suspended acoustical ceiling tile, Se = Selenium, VCT
= vinyl composite tile, w/ = with
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 Polychlorinated Biphenyls
Ballasts
EHSI inspected every type of fluorescent fixture for PCB-containing ballasts. 73% of fixtures inspected were found to contain magnetic ballasts and must be assumed to contain PCB containing dielectric fluid and may be disposed/recycled as Ecology Dangerous Waste.
Electronic ballasts, which contain no dielectric fluid, may be disposed as construction debris.
A Summary of PCB-containing ballasts and Hg-containing light tubes, CFL bulbs, and HID lamps is provided in Table 6.
2.4.5 Mercury-Containing Fluorescent Light Tubes, CFL Bulbs, and thermostats
All fluorescent light tubes and CFL bulbs quantified in Table 6 contain Hg. Hg wastes are regulated as “universal wastes” under Ecology’s regulation WAC 173-303. Hg-containing building materials must be recycled or disposed of as hazardous waste. One (1) Hg-containing switches or thermostats were identified in the structures.
TABLE 6
SUMMARY OF LIGHT FIXTURE INSPECTION RESULTS
NATIONAL PARK SERVICE
FORT VANCOUVER BARRACKS – BUILDING 754
LIGHT TYPE FIXTURES
TUBES/
BULBS
MAGNETIC
BALLASTS
2’x4’ Recessed light fixture w/ 2 bulbs and 1 magnetic ballast 41 82 41
1’x4’ Mounted light fixture w/ 2 bulbs and 1 electronic ballast 7 14 0
4”x4’ Mounted light fixture w/ 1 bulb and 1 magnetic ballast 27 27 27
4”x4’ Mounted light fixture w/ 1 bulb and 1 electronic ballast 8 8 0
2’x2’ Recessed light fixture w/ 2 bulbs and 1 magnetic ballast 1 2 1
CFL bulbs 4 4 0
Sign light w/ assumed 4 bulbs and 2 magnetic ballasts 2 8 4
Loose 4’ bulbs in box 8 8 0
HID lamps 1 1 1
BUILDING 754 TOTAL 99 154 74
Key: CFL = compact fluorescent light, HID = high intensity discharge, w/ = with
3.0 LIMITATIONS
This survey was limited to those materials accessible using standard survey methods. Limited representative destructive inspection was accomplished. All suspect materials present were accessible for sampling.
This survey was limited to the chemicals and materials identified herein. No effort was made to identify hazardous materials in soil, water, or air, other than those listed herein. Any survey regardless of how extensive can miss concealed materials. Contractors should be aware of the potential that demolition activities may expose concealed suspect ACM and should have preplanned contingencies for handling these materials when discovered during demolition work. Any concealed, suspect ACM material that was not sampled or that was assumed to be
ACM by this survey report when encountered must be treated as ACM until sampled by a
Certified AHERA Building Inspector and analyzed by a certified laboratory. Energized electrical equipment and mirror mastics 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.
4.0 STANDARD OF CARE
The recommendations and conclusions contained in this report represent the professional opinions of EHSI. These opinions are derived in accordance with federal, state, and local environmental and health and safety laws and regulations. This survey was accomplished in accordance with applicable federal, state, and local regulations and industry standards in effect at the time. Other than this, no other warranty is implied or intended.
5.0 CERTIFIED AHERA BUILDING INSPECTORS
The Certified AHERA Building Inspectors listed below surveyed Building 754 on September
13th, 2018, in accordance with federal, state, and local requirements.
Rory Peterson Brett Racine
Certified AHERA Building Inspector Certified AHERA Building Inspector
Certificate Number: 169055 Certificate Number: 168604
Expiration Date: August 15, 2019 Expiration Date: July 18, 2019
Appendix A
APPENDIX A
Asbestos Analytical Laboratory Report and Field Data Forms
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Matt Macfarlane, Asbestos Lab Supervisor
Client Project: 11176-001 Location: NPS Fort Vancouver Barracks
Dear Mr. Peterson, Enclosed please find test results for the 13 sample(s) submitted to our laboratory for analysis on 9/21/2018.
Examination of these samples was conducted for the presence of identifiable asbestos fibers using polarized light microscopy (PLM) with dispersion staining in accordance with both EPA 600/M4-82-020, Interim Method for the Determination of Asbestos in Bulk Insulation Samples and EPA 600/R-93/116 Method for the Determination of Asbestos in Bulk Building Materials.
For samples containing more than one separable layer of materials, the report will include findings for each layer (labeled Layer 1 and Layer 2, etc. for each individual layer). The asbestos concentration in the sample is determined by calibrated visual estimation.
For those samples with asbestos concentrations between 1 and 10 percent based on visual estimation, the EPA recommends a procedure known as point counting (NESHAPS, 40 CFR Part 61). Point counting is a statistically more accurate means of quantification for samples with low concentrations of asbestos.
The detection limit for the calibrated visual estimation is <1%, 400 point counts is 0.25% and 1000 point counts is 0.1%
Samples are archived for two weeks following analysis. Samples that are not retrieved by the client are discarded after two weeks.
Thank you for using our laboratory services. Please do not hesitate to call if there is anything further we can assist you with.
Sincerely, Enc.: Sample Results
September 30, 2018
Rory Peterson EHS International 1011 SW Klickitat Way. Suite 104 Seattle, WA 98134
RE: Bulk Asbestos Fiber Analysis; NVL Batch # 1818557.00
< Client:
Address:
Attention: Mr. Rory Peterson NPS Fort Vancouver Barracks
Client Project #: 11176-001
Samples Received: 13
By Polarized Light Microscopy Bulk Asbestos Fibers Analysis
EHS International 1011 SW Klickitat Way. Suite 104 Seattle, WA 98134
Method: EPA/600/R-93/116
& EPA/600/M4-82-020
Samples Analyzed: 13 Project Location:
Batch #: 1818557.00
Date Received: 9/21/2018
18094453Lab ID: Client Sample #:
Location: NPS Fort Vancouver Barracks
11176-165QA
Layer 1 of 1 Description: Brown compressed fibrous material with trace black asphaltic mastic Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Asphalt/Binder, Binder/Filler 72%Cellulose None Detected ND
18094454Lab ID: Client Sample #:
Location: NPS Fort Vancouver Barracks
11176-208QA
Layer 1 of 1 Description: Black asphaltic fibrous material tan soft mastic Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Asphalt/Binder, Mastic/Binder 62%Cellulose None Detected ND
18094455Lab ID: Client Sample #:
Location: NPS Fort Vancouver Barracks
11176-221QA
Layer 1 of 5 Description: Layered black asphaltic fibrous material with green/gray granules Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Asphalt/Binder, Granules, Mineral grains 20%Glass fibers None Detected ND Layer 2 of 5 Description: Black asphaltic mastic
Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: % Asphalt/Binder NDNone Detected None Detected ND
Layer 3 of 5 Description: Black asphaltic fibrous material with mineral grains Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Asphalt/Binder, Mineral grains 12%Glass fibers None Detected ND Layer 4 of 5 Description: Dark gray soft material
Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: % Synthetic/Binder NDNone Detected None Detected ND
Note: If samples are not homogeneous, then subsamples of the components were analyzed separately. All bulk samples are analyzed using both EPA 600/R-93/116 and 600/M4-82-020 Methods with the following measurement uncertainties for the reported % Asbestos (1%=0-3%, 5%=1-9%, 10%=5-15%, 20%=10-30%, 50%=40-60%). This report relates only to the items tested. If sample was not collected by NVL personnel, then the accuracy of the results is limited by the methodology and acuity of the sample collector. This report shall not be reproduced except in full, without written approval of NVL Laboratories, Inc. It shall not be used to claim product endorsement by NVLAP or any other agency of the US Government
Client Alla PrysyazhnyukAnalyzed by:
Matt MacfarlaneReviewed by:
09/27/2018 Date:
09/30/2018Date:
Sampled by:
Matt Macfarlane, Asbestos Lab Supervisor
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Attention: Mr. Rory Peterson NPS Fort Vancouver Barracks
Client Project #: 11176-001
Samples Received: 13
By Polarized Light Microscopy Bulk Asbestos Fibers Analysis
EHS International 1011 SW Klickitat Way. Suite 104 Seattle, WA 98134
Method: EPA/600/R-93/116
& EPA/600/M4-82-020
Samples Analyzed: 13 Project Location:
Batch #: 1818557.00
Date Received: 9/21/2018
Layer 5 of 5 Description: Black soft asphaltic material on wood flakes Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Asphalt/Binder, Wood flakes 5%Glass fibers None Detected ND
18094456Lab ID: Client Sample #:
Location: NPS Fort Vancouver Barracks
11176-227QA
Layer 1 of 1 Description: Brown/black soft asphaltic mastic with thin green coating Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Asphalt/Binder, Binder/Filler, Calcareous particles 2%Cellulose None Detected ND
Mastic/Binder 2%Synthetic fibers
18094457Lab ID: Client Sample #:
Location: NPS Fort Vancouver Barracks
11176-231QA
Layer 1 of 1 Description: Cream soft mastic on wood flakes Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Fine particles, Mastic/Binder, Wood flakes NDNone Detected None Detected ND
18094458Lab ID: Client Sample #:
Location: NPS Fort Vancouver Barracks
11176-244QA
Layer 1 of 1 Description: Tan putty material with white/green paint Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Binder/Filler, Calcareous particles, Paint NDNone Detected None Detected ND
18094459Lab ID: Client Sample #:
Location: NPS Fort Vancouver Barracks
11176-250QA
Layer 1 of 1 Description: Off-white compressed fibrous material Non-Fibrous Materials: Other Fibrous Materials:% Asbestos Type: %
Binder/Filler, Fine particles NDNone Detected Chrysotile 82%
Note: If samples are not homogeneous, then subsamples of the components were analyzed separately. All bulk samples are analyzed using both EPA 600/R-93/116 and 600/M4-82-020 Methods with the following measurement uncertainties for the reported % Asbestos (1%=0-3%, 5%=1-9%, 10%=5-15%, 20%=10-30%, 50%=40-60%). This report relates only to the items tested. If sample was not collected by NVL personnel, then the accuracy of the results is limited by the methodology and acuity of the sample collector. This report shall not be reproduced except in full, without written approval of NVL Laboratories, Inc. It shall not be used to claim product endorsement by NVLAP or any other agency of the US Government
Client Alla PrysyazhnyukAnalyzed by:
Matt MacfarlaneReviewed by:
09/27/2018 Date:
09/30/2018Date:
Sampled by:
Matt Macfarlane, Asbestos Lab Supervisor
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EHS International 1818557.00
Company NVL Batch Number
Total Number of Samples
NPS Fort Vancouver Barracks
5 DaysTAT
9/28/2018Due Date 8:00 AMTime
(206) 254-4279Fax roryp@ehsintl.comEmail
Project Manager Mr. Rory Peterson
(206) 381-1128
(425) 766-8342Cell
Phone
Rush Samples
Rush TAT NoAH
11176-001Project Name/Number: Project Location:
Sample ID Description A/RLab ID
ASBESTOS LABORATORY SERVICES
Subcategory
Item Code
PLM Bulk
Metals ASB-02 EPA 600/R-93-116 Asbestos by PLM <bulk>
1011 SW Klickitat Way. Suite 104 Seattle, WA 98134
Address
11176-165QA1 A18094453
11176-208QA2 A18094454
11176-221QA3 A18094455
11176-227QA4 A18094456
11176-231QA5 A18094457
11176-244QA6 A18094458
11176-250QA7 A18094459
11176-269QA8 A18094460
11176-281QA9 A18094461
11176-282QA10 A18094462
11176-307QA11 A18094463
11176-315QA12 A18094464
11176-323QA13 A18094465
Office Use Only Print Name Company Date TimeSignature
Faxed Emailed
Company Date TimeSignature ClientSampled by
Emily SchubertReceived by
ClientRelinquished by
Alla PrysyazhnyukAnalyzed by Results Called by
NVL
NVL
9/21/18 9/27/18
Print Name
Entered By: Emily Schubert
Date: 9/21/2018 Time: 9:05 AM
Special Instructions:
Appendix B
APPENDIX B
Lead Laboratory Reports and Field Data Forms
RE: Metals Analysis; NVL Batch # 1818559.00
Dear Mr. Peterson, September 21, 2018
EHS International Rory Peterson
1011 SW Klickitat Way. Suite 104 Seattle, WA 98134
Enclosed please find the test results for samples submitted to our laboratory for analysis.
Preparation of these samples was conducted following protocol outlined in EPA Method SW 846 -3051 unless stated otherwise. Analysis of these samples was performed using analytical instruments in accordance with U.S. EPA, NIOSH, OSHA and other ASTM methods.
For matrix materials submitted as paint, dust wipe, soil or TCLP samples, analysis for the presence of total metals is conducted using published U.S. EPA Methods. Paint and soil results are usually expressed in mg/Kg which is equivalent to parts per million (ppm). Lead (Pb) in paint is usually expressed in mg/Kg (ppm) , Percent (%) or mg/cm2 by area. Dust wipe sample results are usually expressed in ug/wipe and ug/ft2. TCLP samples are reported in mg/L (ppm). For air filter samples, analyses are conducted using NIOSH and OSHA Methods. Results are expressed in ug/filter and ug/m3. Other matrix materials are analyzed accordingly using published methods or specified by client. The reported test results pertain only to items tested and are not blank corrected.
For recent regulation updates pertaining to current regulatory levels or permissible exposure levels, please call your local regulatory agencies for more details.
This report is considered highly confidential and will not be released without your approval.
Samples are archived for two weeks following analysis. Samples that are not retrieved by the client are discarded after two weeks.
Thank you for using our laboratory services. if you need further assistance please feel free to call us at 206-547-0100 or 1-888-NVLLABS.
Sincerely, Shalini Patel, Lab Supervisor
Analysis Report Total Lead (Pb)
NPS Fort Vancouver Barracks
EHS InternationalClient:
1011 SW Klickitat Way. Suite 104 Seattle, WA 98134
Mr. Rory PetersonAttention:
Address:
Project Location: Samples Received: 13 Samples Analyzed: 13
Client Project #: 11176-001
Batch #: 1818559.00
Date Received: 9/21/2018
Lab ID Client Sample # Sample Weight (g)
Results in mg/Kg
Results in percent
RL in mg/Kg
Matrix: Bulk Method: EPA 3051/7000B
18094468 11176-Pb01 0.2648 38 41000 4.1
18094469 11176-Pb02 0.2722 37 < 37 0.0037<
18094470 11176-Pb03 0.3194 31 < 31 0.0031<
18094471 11176-Pb04 0.3357 30 < 30 0.0030<
18094472 11176-Pb05 0.2942 34 36 0.0036
18094473 11176-Pb06 0.3343 30 < 30 0.0030<
18094474 11176-Pb07 0.2000 50 60000 6.0
18094475 11176-Pb08 0.1934 52 < 52 0.0052<
18094476 11176-Pb09 0.1939 52 1700 0.17
18094477 11176-Pb10 0.2697 37 47 0.0047
18094478 11176-Pb11 0.1936 52 920 0.092
18094479 11176-Pb12 0.3352 30 160000 16
18094480 11176-Pb13 0.1877 53 17000 1.7
ClientSampl…
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