26-092 USCG Air Station Sacramento - Survey Report.pdf

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This is an Asbestos and Lead Survey Report prepared by Advantage Environmental & Safety Services for the United States Coast Guard Air Station Sacramento on July 13, 2026, with results reported on August 4, 2026. The survey examined designated interior areas across first and second floors to identify asbestos-containing materials (ACM) and lead-containing building materials. Forty-three bulk samples representing 91 material layers underwent Polarized Light Microscopy (PLM) analysis for asbestos detection, with 4% chrysotile asbestos identified in the black bituminous mastic beneath 12-inch by 12-inch resilient floor tile at two locations in the Men's Locker Room (Samples 071326-CGMC-29 and -33). No asbestos was detected in the remaining 89 sample layers. Fourteen bulk samples were analyzed for total lead content using flame atomic absorption spectroscopy (EPA Method 7000B), with detectable lead found in nine samples. Three samples exceeded federal regulatory thresholds for lead-based paint (≥0.50% by weight/≥5,000 mg/kg): red paint on kitchen concrete floor (0.509%), white paint on structural steel I-beam (11.0%), and blue paint on the same I-beam (12.4%). Sample Pb12 (blue paint on CMU in MLR hallway) tested at 0.496%, just below the threshold but recommended for management as lead-containing material.

The report recommends that identified floor tile and mastic be removed by a licensed asbestos abatement contractor in compliance with Cal/OSHA and applicable NESHAP requirements prior to renovation or demolition activities. Lead-containing paint and coatings on the I-beam, concrete kitchen floor, and painted CMU wall require personnel awareness of OSHA Lead in Construction Standard (29 CFR 1926.62) compliance, including exposure assessment and appropriate engineering controls. All waste generated from removal of identified ACM and lead-containing materials must be manifested and disposed of in accordance with applicable federal, state, and local regulations. The survey was limited in scope to specific materials and locations shown on sample location diagrams; areas outside the survey scope or unsampled locations should be presumed to contain asbestos or lead and sampled prior to disturbance. Field sampling was performed by Matt Bailey (Cal/OSHA Certified Site Surveillance Technician, CDPH Lead Sampling Technician), with report preparation and review by Kelly Kilpatrick (Cal/OSHA Certified Asbestos Consultant, CDPH Lead Inspector/Assessor and Project Monitor).

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Advantage Environmental & Safety Services

ASBESTOS AND LEAD SURVEY REPORT

United States Coast Guard – Air Station Sacramento

6037 Price Avenue, McClellan Park, California 95652

U.S. Coast Guard Air Station Sacramento – site entrance signage

AESS Job Number: 26-092

Survey / Sample Collection Date: July 13, 2026

Report Date: August 4, 2026

Prepared For: United States Coast Guard – Air Station Sacramento

Prepared By:

Advantage Environmental & Safety Services

1600 Sacramento Inn Way, Suite 127, Sacramento, CA 95815

Asbestos and Lead Survey Report

USCG Air Station Sacramento – Job No. 26-092

Advantage Environmental & Safety Services | Confidential – Prepared for U.S. Coast Guard | Page 2 of 31

1.0 Executive Summary

Advantage Environmental & Safety Services (AESS) was retained to perform an asbestos- and lead-containing materials survey of designated interior areas at the United States Coast Guard (USCG) Air Station Sacramento, located at 6037 Price Avenue, McClellan Park, California 95652 (the “Site”). The survey was performed on July

13, 2026 by Matt Bailey, Certified Site Surveillance Technician (CSST) and Lead Sampling Technician, of AESS, and consisted of representative bulk sampling of suspect asbestos-containing materials (ACM) and suspect lead-containing building materials within first- and second-floor areas identified on the sample location diagrams provided as Figures 1 and 2 (Section 5.3).

Forty-three (43) bulk samples (representing 91 individual material layers) were collected and submitted for

Polarized Light Microscopy (PLM) analysis of asbestos content – forty-two (42) samples (90 layers) under

Schneider Laboratories Order No. 696941, and one (1) point-count sample (1 layer, concrete) under Order No.

696944. Asbestos was detected in the black, bituminous mastic layer beneath two 12-inch by 12-inch resilient floor tile samples – Sample 071326-CGMC-29 (1st Floor, Men’s Locker Room [MLR], A wall) and Sample 071326-

CGMC-33 (1st Floor, MLR hallway) – each containing 4% chrysotile asbestos. No asbestos was detected in the remaining 89 sample layers. Fourteen (14) bulk samples were collected and submitted for total lead analysis by flame atomic absorption spectroscopy (EPA Method 7000B). Detectable lead was identified in nine (9) of the fourteen samples. Three of those samples – Pb5 (red paint on the concrete kitchen floor, 5,090 mg/kg / 0.509%), Pb10 (white paint on an 8-inch structural steel I-beam, 110,000 mg/kg / 11.0%), and Pb11 (blue paint on the same I-beam, 124,000 mg/kg / 12.4%) – exceeded the federal regulatory definition of lead-based paint (≥ 0.50% by weight / ≥ 5,000 mg/kg). A fourth sample, Pb12 (blue paint on CMU, 1st Floor MLR hallway), was detected at

0.496% (4,960 mg/kg), just below the regulatory threshold. No lead was detected above the laboratory reporting limit in the remaining five samples (Pb1, Pb7, Pb8, Pb9, and Pb14).

A summary of findings and AESS recommendations is provided in Sections 5.0 and 6.0 of this report. Complete laboratory analytical reports, chain-of-custody documentation, and the sample location diagrams (Figures 1 and

2) are included as Appendices A and B, with applicable personnel certifications provided in Appendix C.

2.0 Introduction and Scope of Work

This report presents the results of a limited asbestos- and lead-containing materials survey conducted by AESS at the request of the United States Coast Guard in connection with planned maintenance, renovation, or abatement-related activities at Air Station Sacramento. The purpose of the survey was to identify the presence and approximate concentration of asbestos and lead in designated suspect building materials so that appropriate handling, abatement, and disposal procedures can be planned prior to disturbance of those materials.

The scope of work performed by AESS included the following:

• A visual survey of designated interior spaces to identify homogeneous areas of suspect asbestos-containing and lead-containing materials.

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• Collection of forty-three (43) representative bulk samples of suspect ACM in general accordance with 40 CFR

Part 763 (AHERA) and EPA Method 600/R-93/116 sampling protocols.

• Collection of fourteen (14) representative bulk samples of suspect lead-containing materials (paint and ceramic tile/glaze).

• Submission of all samples under chain-of-custody to Schneider Laboratories Global, Inc. (Richmond, Virginia), an AIHA-LAP, LLC and NVLAP accredited laboratory, for analysis.

• Preparation of sample location diagrams and this summary report of findings.

This survey was limited to the specific materials, locations, and areas identified by AESS field staff and shown on the sample location diagrams in Figures 1 and 2 (Section 5.3). AESS did not perform a comprehensive, building-wide hazardous materials survey. Refer to Section 7.0, Limitations, for additional information regarding the scope and applicability of this report.

3.0 Site Description

The Site is the USCG Air Station Sacramento facility located at 6037 Price Avenue, McClellan Park, Sacramento

County, California. The areas surveyed include, on the first floor, the kitchen, men’s restroom/shower (MRR) facilities, men’s locker room (MLR) and adjoining hallway, women’s restroom (WRR), and adjacent shop and office areas; and, on the second floor, the crew lounge, duty rooms, snack store, and men’s restroom (MRR) facilities, together with adjoining corridor space, as depicted in the sample location diagrams (Figures 1 and 2, Section 5.3). Suspect materials sampled included ceramic wall and floor tile with associated setting materials

(mortar, thin-set, and grout), painted drywall, painted concrete masonry unit (CMU) walls, painted structural steel (I-beam), 12-inch by 12-inch resilient floor tile and associated black mastic, 2-foot by 4-foot acoustical ceiling tile, epoxy floor coatings and underlying concrete, rubber baseboard and glue, fiberglass-reinforced panel

(FRP) glue, wall panel adhesive, carpet glue, and drywall joint compound/texture systems.

4.0 Survey Methodology

4.1 Asbestos Sampling and Analysis

Suspect ACM was identified by visual inspection and grouped into homogeneous areas based on material type, color, texture, and apparent date of installation. Representative bulk samples were collected from each homogeneous area using wetting techniques and dedicated sampling tools to minimize fiber release, double-bagged, labeled, and submitted under chain-of-custody to Schneider Laboratories Global, Inc. Samples were analyzed by Polarized Light Microscopy (PLM) in accordance with EPA Method 600/R-93/116 and 40 CFR Part

763, Appendix E, Subpart E; one sample (concrete) was additionally analyzed by 400-point count in accordance with EPA Method 600/R-93/116 and California Air Resources Board (CARB) Method 435. Materials composed of multiple layers (e.g., tile / setting bed / grout, or drywall / joint compound / texture) were analyzed and reported by individual layer.

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4.2 Lead Sampling and Analysis

Suspect lead-containing painted surfaces and ceramic tile/glaze were sampled by removing a representative bulk chip or section of material. Samples were submitted under chain-of-custody to Schneider Laboratories Global, Inc. and analyzed for total lead content by flame atomic absorption spectroscopy in accordance with EPA

Method 7000B. Results are reported in milligrams of lead per kilogram of sample (mg/kg, equivalent to parts per million) and as percent lead by dry weight.

5.0 Summary of Findings

5.1 Asbestos Analytical Results

Forty-three bulk samples, representing 91 analyzed material layers, were submitted for PLM analysis under

Schneider Laboratories Order Nos. 696941 (42 samples / 90 layers) and 696944 (1 point-count sample / 1 layer, Sample 071326-CGMC-C1, concrete). Asbestos (4% chrysotile) was detected in the black, bituminous mastic layer of two 12-inch by 12-inch floor tile samples: Sample 071326-CGMC-29 (1st Floor MLR, A wall) and Sample

071326-CGMC-33 (1st Floor MLR hallway). No asbestos fibers were detected in any of the remaining 89 analyzed layers. The laboratory noted that three samples (071326-CGMC-19, -20, and -36), submitted as suspect 2-foot by

4-foot acoustical ceiling tile, were received as drywall rather than acoustical tile; these samples were analyzed and reported as received, and no asbestos was detected in these layers. A summary of sampled materials is provided in Table 1; the complete laboratory report is included as Appendix A.

Table 1. Asbestos (PLM) bulk sample summary – Schneider Laboratories Order Nos. 696941 and 696944. MRR = Men’s Restroom;

WRR = Women’s Restroom; MLR = Men’s Locker Room.

Sample ID Location Material Sampled Asbestos Result

071326-CGMC-1 2nd Flr Crew Lounge B Wall Drywall, taping mud None Detected

071326-CGMC-2 2nd Flr Snack Store B Wall Drywall, taping mud None Detected

071326-CGMC-3 2nd Flr Snack Store C Wall Baseboard, glue None Detected

071326-CGMC-4 2nd Flr Snack Store C Wall Carpet glue None Detected

071326-CGMC-5 2nd Flr Crew Lounge D Wall Carpet glue None Detected

071326-CGMC-6 2nd Flr Crew Lounge D Wall Baseboard, glue None Detected

071326-CGMC-7 2nd Flr Crew Lounge B Wall 2x4 acoustic tile None Detected

071326-CGMC-8 2nd Flr Crew Lounge C Wall 2x4 acoustic tile None Detected

071326-CGMC-9 2nd Flr MRR Under Sink 4" ceramic wall tile (grey), thin-set, grout None Detected

071326-CGMC-10 2nd Flr MRR Under Sink 2" ceramic floor tile (white), mortar, grout None Detected

071326-CGMC-11 2nd Flr MRR D Wall Drywall, taping mud None Detected

071326-CGMC-12 2nd Flr MRR C Wall 4" ceramic wall tile (grey), glue, mortar, grout None Detected

071326-CGMC-13 2nd Flr MRR C Wall 2" ceramic floor tile (white), mortar, grout None Detected

071326-CGMC-14 1st Flr Kitchen Floor Epoxy flooring material (brown) None Detected

071326-CGMC-15 1st Flr Kitchen Floor Epoxy flooring material (brown) None Detected

071326-CGMC-16 1st Flr Kitchen Ceiling 2x4 acoustic ceiling None Detected

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071326-CGMC-17 1st Flr MRR C Wall Drywall None Detected

071326-CGMC-18 1st Flr MRR B Wall Drywall None Detected

071326-CGMC-19 1st Flr MRR near C Wall Ceiling 2x4 acoustic ceiling (rec’d as drywall)* None Detected

071326-CGMC-20 1st Flr MRR near A Wall Ceiling 2x4 acoustic ceiling (rec’d as drywall)* None Detected

071326-CGMC-21 1st Flr MRR C Wall FRP glue None Detected

071326-CGMC-22 1st Flr MRR A Wall FRP glue None Detected

071326-CGMC-23 1st Flr MRR Shower Wall (Left) Epoxy flooring material (green) None Detected

071326-CGMC-24 1st Flr MRR Shower Wall (Left) 4" ceramic wall tile (blue), grout, mortar None Detected

071326-CGMC-25 1st Flr MRR Shower Wall (Left) 4" ceramic wall tile (white), grout, mortar None Detected

071326-CGMC-26 1st Flr MRR Shower Floor (Left) 2" ceramic floor tile (white), thin-set, grout None Detected

071326-CGMC-27

1st Flr MRR Shower Floor (Right)

2" ceramic floor tile (white), thin-set, grout None Detected

071326-CGMC-28 1st Flr MLR Floor Middle Epoxy flooring material (green) None Detected

071326-CGMC-29 1st Flr MLR A Wall 12x12 floor tile, mastic 4% Chrysotile (mastic layer)

071326-CGMC-30 1st Flr MLR A Wall Baseboard, glue None Detected

071326-CGMC-31 1st Flr MLR Hallway Texture, taping mud, drywall None Detected

071326-CGMC-32 1st Flr MLR Hallway Baseboard, glue None Detected

071326-CGMC-33 1st Flr MLR Hallway 12x12 floor tile, mastic 4% Chrysotile (mastic layer)

071326-CGMC-34 1st Flr MLR Hallway Texture, taping mud, drywall None Detected

071326-CGMC-35 1st Flr WRR D Wall Taping mud, drywall None Detected

071326-CGMC-36 1st Flr WRR Center Ceiling 2x4 acoustic tile (rec’d as drywall)* None Detected

071326-CGMC-37 1st Flr WRR B Wall Wall panel, glue None Detected

071326-CGMC-38 1st Flr WRR D Wall Wall panel, glue None Detected

071326-CGMC-39 1st Flr WRR A Wall 6"x4" ceramic wall tile (beige), glue, grout None Detected

071326-CGMC-40 1st Flr WRR A Wall 2" ceramic floor tile (brown), thin-set, grout None Detected

071326-CGMC-41 1st Flr WRR D Wall 2" ceramic floor tile (brown), thin-set, grout None Detected

071326-CGMC-42 1st Flr WRR D Wall 6"x4" ceramic wall tile (beige), glue, grout None Detected

071326-CGMC-C1 1st Flr Kitchen Floor Concrete (grey) – 400 point count None Detected

* Sample submitted as suspect acoustical ceiling tile but received by the laboratory as drywall; result applies to the material as received.

The actual acoustical ceiling tile at these three locations, if present, has not been characterized.

5.2 Lead Analytical Results

Fourteen bulk samples (Schneider Laboratories Order No. 696944) were submitted for total lead analysis.

Detectable lead was identified in nine of the fourteen samples. Three samples – Pb5 (red paint on the concrete kitchen floor, 5,090 mg/kg / 0.509%), Pb10 (white paint on an 8-inch structural steel I-beam, 110,000 mg/kg /

11.0%), and Pb11 (blue paint on the same I-beam, 124,000 mg/kg / 12.4%) – exceeded the current federal regulatory threshold defining lead-based paint (0.50% by weight / 5,000 mg/kg). A fourth sample, Pb12 (blue paint on CMU, 1st Floor MLR hallway), was detected at 0.496% (4,960 mg/kg), just below that threshold. Lower concentrations of lead were also detected in Samples Pb2, Pb3, Pb4, Pb6, and Pb13. No lead was detected above the laboratory reporting limit in Samples Pb1, Pb7, Pb8, Pb9, and Pb14. Results are summarized in Table 2; the complete laboratory report is included as Appendix B.

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Table 2. Lead bulk sample summary – Schneider Laboratories Order No. 696944. Federal lead-based paint threshold (as of 7/1/26):

0.50% by weight / 5,000 mg/kg.

Sample ID Location Material Sampled Result % by Wt.

Pb1 2nd Flr Crew Lounge A Wall White paint on drywall <30.8 mg/kg <0.00308%

Pb2 2nd Flr MRR Under Sink 4" ceramic wall tile (grey) 121 mg/kg 0.0121%

Pb3 2nd Flr MRR Under Sink 2" ceramic floor tile (white) 12.9 mg/kg 0.00129%

Pb4 1st Flr Kitchen A Wall White paint on CMU 448 mg/kg 0.0448%

Pb5 1st Flr Kitchen Floor Red paint on concrete 5,090 mg/kg 0.509%

Pb6 1st Flr Kitchen C Wall Tan paint on CMU 733 mg/kg 0.0733%

Pb7 1st Flr MRR Shower Wall (Left) 4" ceramic wall tile (white) <15.6 mg/kg <0.00156%

Pb8 1st Flr MRR Shower Wall (Left) 4" ceramic wall tile (blue) <11.8 mg/kg <0.00118%

Pb9 1st Flr MRR Shower Floor (Left) 2" ceramic floor tile (white) <10.7 mg/kg <0.00107%

Pb10 1st Flr MLR C Wall White paint on 8" steel I-beam 110,000 mg/kg 11.0%

Pb11 1st Flr MLR C Wall Blue paint on 8" steel I-beam 124,000 mg/kg 12.4%

Pb12 1st Flr MLR Hallway Blue paint on CMU 4,960 mg/kg 0.496%

Pb13 1st Flr WRR A Wall 2" ceramic floor tile (brown) 27.0 mg/kg 0.0027%

Pb14 1st Flr WRR A Wall 6"x4" ceramic wall tile (beige) <16.0 mg/kg <0.0016%

5.3 Sample Location Diagrams

Figures 1 and 2 depict the approximate location of each asbestos (PLM) and lead (Pb) sample collected during the July 13, 2026 survey, on the second and first floors, respectively. Yellow highlighting indicates no asbestos or lead was reported for that sample location; violet highlighting denotes the two locations where asbestos was detected in the floor tile mastic (Samples 071326-CGMC-29 and -33, both on the 1st floor); red highlighting denotes sample locations where lead was detected, as discussed in Section 5.2. No positive asbestos or lead results were identified on the 2nd floor (Figure 1).

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Figure 1. Sample location diagram, 2nd Floor, USCG Air Station Sacramento (Job No. 26-092).

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Figure 2. Sample location diagram, 1st Floor, USCG Air Station Sacramento (Job No. 26-092).

6.0 Conclusions and Recommendations

6.1 Asbestos

Asbestos-containing material (ACM) was identified in the black, bituminous mastic underlying 12-inch by 12-inch resilient floor tile at two locations on the 1st floor: the A wall of the Men’s Locker Room (MLR) (Sample 071326-

CGMC-29) and the adjoining MLR hallway (Sample 071326-CGMC-33). Both mastic layers contained 4% chrysotile asbestos. No other asbestos-containing materials were identified among the 89 remaining sample layers collected within the areas surveyed.

Under 40 CFR Part 61, Subpart M (NESHAP), floor tile and associated mastic of this type is typically classified as

Category I nonfriable ACM in its current, undisturbed condition. Category I nonfriable ACM that is removed intact, without sanding, grinding, cutting, or abrading, and that is not in poor condition, is generally not subject to NESHAP notification and specialized work-practice requirements; however, if the material will be rendered friable during removal (e.g., by mechanical abrasion) or if the quantity disturbed meets the regulatory threshold, Shawn Jenkins Highlight

Shawn Jenkins Highlight

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NESHAP notification and handling requirements apply. Independent of NESHAP classification, disturbance of the identified ACM is subject to the Cal/OSHA Asbestos Construction Standard (8 CCR Section 1529), which requires use of a registered asbestos abatement contractor, a Certified Asbestos Consultant-developed removal specification, competent-person oversight, and appropriate engineering controls and personal protective equipment for Class I and Class II asbestos work.

• AESS recommends that the identified floor tile and mastic (Sample locations 071326-CGMC-29 and -33, 1st

Floor MLR) be removed by a licensed and registered asbestos abatement contractor in accordance with

Cal/OSHA and, if applicable, NESHAP requirements prior to any renovation, flooring replacement, or demolition activity affecting these areas.

• Waste generated from removal of the identified ACM should be manifested and disposed of as asbestos-containing waste material in accordance with applicable federal, state, and local regulations.

• The remaining 89 sampled material layers did not contain asbestos above the laboratory reporting limit and are not subject to asbestos-specific handling requirements based on these results; however, three samples

(071326-CGMC-19, -20, and -36) were noted by the laboratory as not matching the material described on the chain-of-custody (submitted as acoustical ceiling tile, received as drywall). The actual acoustical ceiling tile at these locations, if present, has not been characterized and should be sampled prior to disturbance.

• As with all limited surveys, any suspect material encountered outside the scope of this survey, or any location not represented by a collected sample, should be presumed to contain asbestos or should be sampled and analyzed prior to disturbance.

6.2 Lead

Detectable lead was confirmed in nine of the fourteen samples collected. Three samples exceeded the federal regulatory definition of lead-based paint (≥ 0.50% by weight / ≥ 5,000 mg/kg): Sample Pb5 (red paint on the concrete kitchen floor, 1st Floor Kitchen), at 0.509% (5,090 mg/kg); Sample Pb10 (white paint on an 8-inch structural steel I-beam, 1st Floor MLR, C wall), at 11.0% (110,000 mg/kg); and Sample Pb11 (blue paint on the same I-beam), at 12.4% (124,000 mg/kg). A fourth sample, Pb12 (blue paint on CMU, 1st Floor MLR hallway), was detected at 0.496% (4,960 mg/kg) — just below the regulatory threshold, but confirming the presence of lead at a concentration AESS recommends be managed as lead-containing material. Lower concentrations of lead, below the federal LBP threshold but above the laboratory reporting limit, were also detected in Samples

Pb2, Pb3, Pb4, Pb6, and Pb13 (ceramic tile and painted CMU surfaces). No lead was detected above the laboratory reporting limit in Samples Pb1, Pb7, Pb8, Pb9, and Pb14. AESS recommends the following:

• Personnel performing demolition, cutting, grinding, sanding, or removal of the painted I-beam surfaces

(Samples Pb10/Pb11), the painted concrete kitchen floor (Sample Pb5), and the painted CMU wall in the

MLR hallway (Sample Pb12) should be made aware that these materials contain lead at or approaching levels requiring compliance with the OSHA Lead in Construction Standard (29 CFR 1926.62), including exposure assessment, engineering controls, and personal protective equipment as warranted by the specific task performed.

• Debris and waste generated from removal or disturbance of the identified lead-containing paint and coatings should be evaluated for appropriate hazardous waste characterization (e.g., TCLP or California

TTLC) prior to disposal, consistent with California hazardous waste regulations.

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• The remaining sampled ceramic tile and painted surfaces with lower detected lead concentrations (Samples

Pb2, Pb3, Pb4, Pb6, and Pb13) should also be handled in accordance with OSHA lead-in-construction requirements when disturbed, notwithstanding that they fall below the federal lead-based paint threshold.

• As with asbestos, any suspect painted, coated, or glazed material outside the scope of this survey should be presumed to contain lead or should be sampled prior to disturbance.

7.0 Report Limitations

This report has been prepared for the exclusive use of the United States Coast Guard for the specific Site, scope, and purpose described herein. The findings and conclusions are based on conditions observed and materials sampled at the time of the July 13, 2026 field survey and on the analytical results provided by Schneider

Laboratories Global, Inc. AESS did not sample every material or every location within the facility; materials of similar appearance located in inaccessible or concealed areas were not inspected. Actual conditions may vary from those described in this report, and this report should not be relied upon as a comprehensive, building-wide hazardous materials survey. This report is not intended, and should not be used, as a bidding or specification document for abatement work without further review and, if necessary, additional sampling by AESS.

8.0 Certification

Field sample collection for this survey was performed by Matt Bailey of AESS. This report was prepared and reviewed by Kelly Kilpatrick, Certified Asbestos Consultant (CAC), of AESS. Copies of applicable state certifications held by field and reporting personnel are included as Appendix C.

Matt Bailey

Field Sampling Technician

Cal/OSHA Certified Site Surveillance Technician (CSST) No. 25-7954, exp. 08/15/2027

CDPH Lead Sampling Technician Certificate No. LRC-00013695, exp. 01/23/2027

Kelly Kilpatrick

Report Preparer / Reviewer

Cal/OSHA Certified Asbestos Consultant (CAC) No. 24-7696, exp. 08/16/2027

CDPH Lead Inspector/Assessor Certificate No. LRC-00009599, exp. 01/11/2027

CDPH Lead Project Monitor Certificate No. LRC-00011326, exp. 06/05/2027

CDPH Lead Sampling Technician Certificate No. LRC-00000010, exp. 04/20/2027

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Appendix A – Laboratory Analytical Report: Asbestos (PLM)

Schneider Laboratories Global, Inc. – Order No. 696941, including chain-of-custody documentation.

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Appendix B – Laboratory Analytical Report: Lead

Schneider Laboratories Global, Inc. – Order No. 696944, including total lead (AA) results for fourteen bulk samples (Pb1–Pb14), the point-count PLM asbestos analysis for Sample 071326-CGMC-C1 (concrete), and chain-of-custody documentation.

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Appendix C – Personnel Certifications

State of California certifications held by AESS personnel performing and preparing this survey.

Matt Bailey – Field Sampling Technician

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Kelly Kilpatrick – Report Preparer / Reviewer

1.0 Executive Summary
2.0 Introduction and Scope of Work
3.0 Site Description
4.0 Survey Methodology
4.1 Asbestos Sampling and Analysis
4.2 Lead Sampling and Analysis
5.0 Summary of Findings
5.1 Asbestos Analytical Results
5.2 Lead Analytical Results
5.3 Sample Location Diagrams
6.0 Conclusions and Recommendations
6.1 Asbestos
6.2 Lead
7.0 Report Limitations
8.0 Certification
Appendix A – Laboratory Analytical Report: Asbestos (PLM)
Appendix B – Laboratory Analytical Report: Lead
Appendix C – Personnel Certifications
Matt Bailey – Field Sampling Technician
Kelly Kilpatrick – Report Preparer / Reviewer

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