Att_16_140P8425Q0004_Hazardous_Materials_Survey_FINAL_0004.pdf

COMPREHENSIVE ASBESTOS & LEAD-BASED PAINT,

UNIVERSAL WASTE AND HOUSEHOLD HAZARDOUS

WASTE NESHAP SURVEY REPORT

Crystal Creek Boys Camp Crystal Creek Rd, Ono, CA 96047

Prepared for:

Alanna Gardner

Contracting Officer National Park Service

Contracting Operations (ConOps) West Point Reyes Major Acquisition Buying Office (PORE MABO) alanna_gardner@nps.gov

Prepared by:

March, 2025

2025-182

Crystal Creek Boys Camp Page i

Table of Contents

PURPOSE

EXECUTIVE SUMMARY

ASBESTOS AND LEAD REGULATORY COMPLIANCE

ASBESTOS AND LEAD-BASED PAINT—SURVEY METHODOLOGY

CONCLUSIONS AND RECOMMENDATIONS

APPENDICES

Appendix A Site Maps

Appendix B Asbestos Laboratory Data and Chain-of-Custody

Appendix C Lead XRF Data

Appendix D NESHAP Notification Form

Appendix E Lead Work Pre-Job Notification and Lead In Construction Standard

Appendix F Asbestos & Lead Certifications

Crystal Creek Boys Camp Page 1

Comprehensive Asbestos, Lead-Based Paint, Universal Waste, and

Household Hazardous Waste NESHAP Survey Report

Crystal Creek Boys Camp

Crystal Creek Rd, Ono, CA 96047

PURPOSE

They Crystal Creek Boys Camp located off Crystal Creek Road in Ono, California, has plans to be demolished after suffering damage from the Carr Fire. Guzi-West personnel conducted an asbestos, lead-based paint, universal waste, and household hazardous waste survey in order to determine the presence or absence of these materials at a project location. The survey was conducted in accordance with guidelines established by the

Environmental Protection Agency (EPA), Department of Housing and Urban

Development (HUD), as well as Federal and State of California Occupational Safety and

Health Organization (OSHA). Sampling locations are depicted on the maps provided in

Appendix A; asbestos laboratory data and chain-of-custody is provided in Appendix B;

lead XRF data is provided in Appendix C; a NESHAP Notification Form is provided in

Appendix D; a Lead Work Pre-Job Notification Form and copy of the Lead In Construction

Standard is provided in Appendix E; and a copy of our Asbestos and Lead Certifications are provided in Appendix F.

EXECUTIVE SUMMARY

According to the National Emission Standard for Hazardous Air Pollutants (NESHAP), asbestos-containing building materials (>1% asbestos) must be removed prior to demolition or renovation activities, if the material is considered to be a Regulated

Asbestos-Containing Material (RACM). RACM is generally defined as all friable asbestos containing material and non-friable material, which contains >1% asbestos, and that will become friable during demolition or renovation. A NESHAP notification is required in two circumstances: 1. For any demolition regardless of the presence or absence of asbestos;

NESHAP regulations define a demolition as ‘removing a load-bearing structural member,’ or 2. A renovation that disturbs greater than 160 square feet or 260 linear feet of RACM.

Asbestos containing materials were identified during the survey, however they are

Crystal Creek Boys Camp Page 2 not considered RACM; a NESHAP notification is required regardless due to the project involving a demolition. The NESHAP notification must be submitted a minimum of 10 working days prior to conducting any site disturbance activities.

The table below identifies the asbestos-containing materials identified, their corresponding sample number, material description, approximate location, asbestos type identified by the laboratory, asbestos concentration, final analytical method and photograph of material; please see the asbestos laboratory report provided in Appendix

B and blank NESHAP Notification Form provided in Appendix D.

Asbestos-Containing Materials Identified

GW

Sample

ID

Material Description

Location Asbestos Type(s)

Detected

Asbestos Content

Test Method

Photo

15A- 15B Tan 9”x9” Vinyl Floor

Tile

Building 905, Bathroom

Chrysotile 5% PLM

16A- 16B Black Mastic

Associated with Tan 9”x9”

Vinyl Floor Tile

Building 905, Bathroom

Chrysotile 5% PLM

29A- 29B Cementitious Siding

Building 914, Exterior

Chrysotile 20% PLM

Crystal Creek Boys Camp Page 3

Asbestos-Containing Materials Identified

GW

Sample

ID

Material Description

Location Asbestos Type(s)

Detected

Asbestos Content

Test Method

Photo

30A Silver Paint Building 914, Roof Jack

Chrysotile 0.5% PC-400

33A- 33C Caulking Building 914, Throughout Exterior

Chrysotile 0.5- 1.25% PC-400

35A- 35C Smooth Wall Texture

Building 914, Room 7 & Hallway

Chrysotile 0.25% PC-400

39A- 39B Tan 9”x9” Vinyl Floor Tile

Building 914, Room

Chrysotile 7% PLM

40A- 40B Black Mastic with Tan 9”x9” Vinyl Floor Tile

Building 914, Room

Crystal Creek Boys Camp Page 4

Asbestos-Containing Materials Identified

GW

Sample

ID

Material Description

Location Asbestos Type(s)

Detected

Asbestos Content

Test Method

Photo

42A- 42B Gold 12”x12” Vinyl Floor Tile

Building 914, Bathroom 3

Chrysotile 7% PLM

43A- 43C Light Wall Texture

Building 914, Room

Chrysotile 0.5- 0.75% PC-400

46A- 46B Yellow Mastic with Light Gray 12”x12” Vinyl Floor Tiles

Building 914, Room

Acronyms:

PLM: Polarized Light Microscopy PC-400: Point Count 400 PC-1,000: Point Count 1,000

The silver paint, caulking, smooth wall texture, and light wall texture samples taken from building 914 were re-submitted for analysis by 400 point-count methodology (EPA 600/R-

93/116). If point count laboratory analysis (Point Count 400) shows that a given material

Crystal Creek Boys Camp Page 5 contains less than one percent asbestos, then such material is not considered a hazardous waste by the United States Environmental Protection Agency (USEPA), or the

California Department of Toxic Substances Control (DTSC). As shown in the laboratory report in Attachment B, the silver paint, smooth wall texture, and light wall texture samples taken from building 914 contain less than 1% asbestos. Asbestos material containing less than one percent asbestos is not subject to Cal/OSHA asbestos waste labeling requirements and can be disposed of as general construction debris; however, the acceptance criteria of each California waste facility may differ. The waste acceptor should be contacted, and their individual acceptance criteria abided by, prior to waste transport and disposal.

The caulking, tan 9”x9” vinyl floor tiles and associated mastic (from Building 905), cementitious siding, tan 9”x9” vinyl floor tiles and mastic, gold 12”x12” vinyl floor tiles, and yellow mastic associated with the gray 12”x12” vinyl floor tiles (all from Building 914) are non-friable and contain greater than 1% asbestos. DTSC considers non-friable bulk asbestos-containing waste to be non-hazardous regardless of its asbestos content;

therefore, it is not subject to regulation under Title 22, Division 4.5, of the California Code of Regulations. However, the material must be removed, handled and disposed of in a manner that keeps the material intact to be considered non-friable. The method of removal cannot crumble, pulverize or reduce the material to dust. Sanding, sawing, grinding, chipping or use of power tools is not allowed. If the material cannot be removed without breaking, you must follow the requirements for abatement, and disposal, of friable asbestos-containing materials. Certified asbestos abatement workers must remove all materials containing asbestos that will be disturbed during the subject project, regardless of their asbestos content, due to Cal-OSHA regulations.

As documented in the XRF data log provided in Attachment C, nine (9) interior and exterior surfaces analyzed contain a concentration of lead that meets the regulatory definition of lead-based paint. Additionally, twenty-four (24) interior surfaces analyzed contain a concentration of lead that meets the regulatory definition of lead-containing paint. Given the presence of lead-based paint on nine

Crystal Creek Boys Camp Page 6 interior and exterior surfaces analyzed, Guzi-West recommends that all interior and exterior painted surfaces at the project site be treated as containing lead-based paint. Special engineering practices are required during the disturbance of painted surfaces to protect workers or building occupants. Further, a pre-project notification must be submitted to Cal-OSHA since more than 100 square feet of lead-based paint will be disturbed.

The table on the following page provides the XRF data log sample number, the approximate sample location, the color of the surface analyzed, the substrate from which the surface was analyzed, the lead content found in the surface analyzed, and the lead classification for every surface analyzed that contains lead paint. A discussion on asbestos and lead regulations, XRF measurement interpretation and how regulatory agencies view XRF measurements are presented thereafter. Please see the XRF report provided in Appendix C, and Lead Work Pre-Job Notification Form and copy of the Lead

In Construction Standard provided in Appendix E.

Lead-Based Paint & Lead-Containing Surface Coatings

Sample Number

Location Lead

Concentration Classification

LX1

Exterior South Brown Door – Building 902 0.9 mg/cm2 LCP

LX2 Exterior West Green Concrete Siding – Building 902 1.6 mg/cm2 LBP

LX3 Exterior West Green Window Trim – Building 902 0.9 mg/cm2 LCP

LX4 Exterior South Red Metal Support Post – Building 902 0.4 mg/cm2 LCP

LX5 Exterior South Green Wood Paneling – Building 903 3.1 mg/cm2 LBP

LX6 Interior North White Wood Wall – Bathroom Building 903 1.7 mg/cm2 LBP

LX7 Interior South Wood Window Trim – Building 903 2.0 mg/cm2 LBP

LX8 Interior West Brown Door Trim – Building 903 0.1 mg/cm2 LCP

Crystal Creek Boys Camp Page 7

Location Lead

Concentration Classification

LX9 Interior North White Drywall Wall – Bathroom Building 903 0.1 mg/cm2 LCP

LX10 Interior West White Drywall Wall – Bathroom Building 903 0.1 mg/cm2 LCP

LX11 Interior South White Storage Door – Building 905 1.4 mg/cm2 LBP

LX12 Interior East White Window Trim – Building 905 1.3 mg/cm2 LBP

LX14 Exterior West Red Metal Support Post – Building 905 0.5 mg/cm2 LCP

Lx15 Exterior West Tan Metal Siding Post – Building 905 0.7 mg/cm2 LCP

LX18 Exterior East Brown Door – Building 904

0.2 mg/cm2 LCP

LX19 Exterior North Tan Cinder Block Wall – Building 906 0.3 mg/cm2 LCP

LX22 Interior North White Wood Panel – Building 908 2.7 mg/cm2 LBP

LX23 Interior North White Door Trim – Building 908 0.9 mg/cm2 LCP

LX25 Exterior North Brown Door – Building 908

1.9 mg/cm2 LBP

LX26 Exterior North Tan Metal Siding – Building 908 0.1 mg/cm2 LCP

LX27 Exterior South Tan Metal Siding – Building 908 0.5 mg/cm2 LCP

LX28 Exterior South Silver/Gray Propane Pipe – Propane Area 0.5 mg/cm2 LCP

LX30 Exterior South Gray Concrete Support Pedestal – Propane Area 0.2 mg/cm2 LCP

LX32 Exterior North Brown Metal Support Post – Building 914 0.2 mg/cm2 LCP

LX33 Exterior North Brown Door Trim – Building 914 2.1 mg/cm2 LBP

LX35 Interior East White Wood Paneling – Building 914 0.1 mg/cm2 LCP

LX39 Interior North White Bathroom Paneling – Building 914 0.1 mg/cm2 LCP

Crystal Creek Boys Camp Page 8

Location Lead

Concentration Classification

LX40 Interior West White Wood Paneling – Building 914 0.1 mg/cm2 LCP

LX41 Interior South White Wood Paneling – Building 914 0.1 mg/cm2 LCP

LX44 Exterior West Brown Door Trim – Building 915 0.1 mg/cm2 LCP

LX45 Interior South Tan Metal Siding – Building

0.1 mg/cm2 LCP

LX52 Exterior West Green Window Trim – Water Treatment 0.1 mg/cm2 LCP

LX53 Interior West White Window Trim – Water Treatment 0.1 mg/cm2 LCP

Acronyms:

LBP - lead levels greater than or equal to 1.0 mg/cm², 0.5% by weight, 5,000 mg/kg, 5,000 ppm as defined by USEPA, CDPH, Cal/OSHA LCP - surface coating containing lead in a concentration equal to or greater than 0.009 percent by weight or 90 ppm (90 mg/kg) as defined by CFR and CPSC USEPA - U.S. Environmental Protection Agency CDPH - California Department of Public Health Cal/OSHA - California Occupational Safety and Health Administration CFR – Code of Federal Regulations CPSC - Consumer Product Safety Commission

It should be noted Cal-OSHA regulates any concentration of lead and imposes requirements for employee monitoring to ensure the employee is not exposed above the action level or permissible exposure level. We recommend contractors who have employees who could be exposed to lead at any concentration have training in accordance with the requirements of Title 8, California Code of Regulations, Section

1532.1 and conduct periodic monitoring to ensure employees are not exposed above the action level or permissible exposure level.

Asbestos and Lead Regulatory Compliance

Asbestos

Renovation and demolition projects involving asbestos-containing materials (ACMs) must comply with a range of federal, state, and local regulations designed to ensure safety and environmental protection. The National Emission Standards for Hazardous Air Pollutants

Crystal Creek Boys Camp Page 9

(NESHAP) under 40 CFR Part 61, Subpart M, outlines specific procedures for the notification, handling, and disposal of asbestos. In California, asbestos exposure during construction activities is also regulated by the California Occupational Safety and Health

Administration (Cal/OSHA) under Title 8 CCR 1529, which mandates exposure monitoring, worker protection measures, and training. Additionally, the California Air

Resources Board (CARB) enforces rules regarding asbestos emissions, with local air districts frequently imposing supplementary requirements. Municipalities may also have unique regulations governing asbestos abatement and disposal.

The Asbestos NESHAP regulation specifies work practices to be followed during demolitions and renovations of all structures, installations, and buildings (excluding residential buildings that have four or fewer dwelling units). In addition, the regulations require the owner of the building and/or the contractor to notify the designated state or local air pollution control agency (APCD) in your area before all demolitions, or before renovations of buildings that disturb certain threshold quantities of building materials containing asbestos. Specifically, a NESHAP notification is required in two circumstances: 1. For any commercial, industrial, or multi-residential demolition project regardless of the presence or absence of asbestos; NESHAP regulations define a demolition as ‘removal of a load-bearing structural member,’ or 2. A renovation that disturbs greater than 160 square feet or 260 linear feet of a regulated asbestos-containing material (RACM). RACM is generally defined as all friable asbestos containing material and non-friable material, which contains >1% asbestos, and that will become friable during demolition or renovation. For more information on the NESHAP submittal process, please visit The EPA’s website1.

Worker safety remains a critical priority when handling ACM. Cal/OSHA regulations require contractors to conduct air monitoring to assess airborne asbestos fiber levels in work environments. The permissible exposure limit (PEL) is 0.1 fibers per cubic centimeter (f/cc) of air averaged over an 8-hour workday, with an excursion limit of 1.0 f/cc over a 30-minute period. This monitoring must be performed by qualified individuals trained in asbestos sampling techniques. If exposure levels exceed the PEL, contractors

Crystal Creek Boys Camp Page 10 must establish regulated work areas, post appropriate warning signs, employ engineering controls such as wet methods and local exhaust ventilation, and provide workers with personal protective equipment, including respirators certified for asbestos work.

Worker training and certification are essential components of compliance. All personnel involved in asbestos-related activities must receive specialized training in accordance with Title 8 CCR 1529. Workers directly handling ACM must hold certification from the

California Department of Public Health (CDPH) as required by Title 17 CCR. Supervisors managing abatement projects must also be certified and are responsible for ensuring proper work practices are followed to maintain safety and regulatory compliance.

Given the identification of ACM at the project site, Guzi-West recommends that a licensed asbestos contractor, or licensed consultant such as Guzi-West, develop a comprehensive abatement plan. This plan should include the establishment of regulated work zones to prevent unauthorized access, thorough documentation of air monitoring results, and detailed records of abatement procedures and waste disposal activities. Asbestos waste must be transported and disposed of at approved facilities in compliance with 40 CFR

Part 61 and local landfill regulations. Adherence to these guidelines is essential to protect workers and the public, minimize health risks, and maintain compliance with applicable regulatory standards.

Lead

Utilizing XRF equipment is ideal for quickly and accurately determining lead concentrations in paint and to definitively determine if a painted surface contains concentrations of lead at or above lead-based paint criteria. Lead concentrations in paint below that of lead-based paint can still be regulated however and numerous studies have been completed to correlate XRF measurements with lead concentrations below lead-based paint. The Chevron Research and Technology Company conducted a detailed study in 1995-1996 comparing XRF measurements versus analysis by atomic absorption spectrometry (AAS) in an effort to determine how XRF measurements below 1.0 mg/cm2 compared to measurements by atomic absorption spectrometry. Their findings are often

Crystal Creek Boys Camp Page 11 referred to in the lead paint industry and Guzi-West utilizes their findings to summarize whether a paint is definitively considered a lead-based paint (paint with equal to or greater than 1.0 milligram per square centimeter (mg/cm2), would likely be considered a lead-containing surface coating (paint with concentrations of lead in paint between 0.1 mg/cm2

– 0.9 mg/cm2), or paint which likely contains low levels of lead or no lead at any concentration (paint with concentrations of lead less than 0.1 mg/cm2). The table below presents the information in tabular form for ease of reference and is followed by sample results from the subject project and their designation as either lead-based paint, likely a lead-containing surface coating, and/or likely no measurable concentration of lead present.

XRF Measurement AAS Comparable Measurement Paint Classification

=/> 1.0 mg/cm2 =/> 5,000 ppm Lead-Based Paint

0.1 mg/cm2 – 0.9 mg/cm2

90 ppm – 4,999 ppm Lead-Containing Paint

< 0.1 mg/cm2 <90 ppm Likely paint with very low levels of lead or no lead

Given the presence of lead-based paint identified on multiple structures, we recommend that all painted surfaces at the project site be treated as lead-based paint. Contractors conducting renovation and maintenance work impacting painted surfaces containing lead should take the presence of lead into account and use appropriate lead-safe work practices, including containment and post-work cleaning. The project will need to comply with various governmental and regulatory agency requirements, including: Code of

Federal Regulations (CFR) 29 CFR 1926, Construction Standards; 40 CFR Parts 261, 265, and 268, Hazardous Waste Management; 40 CFR Part 745, Lead: Identification of

Dangerous Levels of Lead; 40 CFR Part 745, Subpart E, Lead Renovation, Repair, and

Painting Program (RRP); 49 CFR Parts 172, 173, 178, and 179, Hazardous Material

Transportation; and California Code of Regulations (CCR) 8 CCR 1532.1, Lead in

Construction.

Crystal Creek Boys Camp Page 12

Cal/OSHA regulates all concentrations of lead, requiring employee exposure monitoring to ensure that workers are not exposed above the action level or permissible exposure limit (PEL) as set forth under Title 8 CCR 1532.1. The contractor must conduct worker breathing zone exposure monitoring, known as personal air monitoring, to determine the airborne concentration of lead in the work environment. Air monitoring is required by

Cal/OSHA and must be carried out daily or until a negative exposure assessment (NEA) is achieved. If a NEA cannot be established, air monitoring should continue throughout the duration of the project to ensure workers are utilizing appropriate protection. Until an employee exposure assessment determines that workers are not exposed to lead levels above the PEL, contractors should treat workers as though they are exposed above the

PEL and must implement protective measures accordingly. Personal air monitoring should be conducted by a qualified individual familiar with the methods of air monitoring in accordance with Title 8 CCR 1532.1. If airborne concentrations exceed the action level, worker protections should be instituted, and documentation of the source of lead emissions should be provided. In the event that air monitoring shows exposure to lead above 30 micrograms per cubic meter of air (µg/m³), known as the Cal/OSHA Action

Level, or 50 µg/m³, known as the PEL, the contractor must document that exposed workers have received action level training and, if necessary, CDPH certification. CDPH certification is required for workers exposed to lead above the PEL in a building accessible to the public, as defined by Title 17 CCR, Division 1, Chapter 8, Article 1.

The contractor must implement specific work protocols when performing tasks that involve the disturbance of lead-containing surfaces, including: the establishment of a regulated work area, posting of warning signage, hygiene controls, the use of wet methods to reduce dust generation, the use of HEPA vacuums, and the use of personal protective equipment (PPE), including respirators when appropriate. All workers engaged in lead-related construction activities must receive lead hazard training. The level of training depends on their role, and contractors must maintain records confirming the training of all personnel, particularly if air monitoring shows exposure above the action level or PEL. The contractor should only use workers who are trained and medically qualified for lead-related work, and workers performing tasks that could expose them to

Crystal Creek Boys Camp Page 13 lead above the action level or PEL must undergo medical evaluation and biological monitoring for lead as required by Title 8 CCR 1532.1. Guzi-West also recommends that the contractor comply with all necessary respiratory protection protocols and use only medically qualified workers for tasks expected to result in airborne lead exposures above the action level.

ASBESTOS & LEAD—SURVEY METHODOLOGY

Guzi-West personnel collected suspected asbestos-containing building materials at the subject structure on March 18, 2025. Following collection of the samples, the asbestos samples were double bagged and then delivered to PEL Laboratory, LLC, under chain-of-custody, for identification of asbestos content. Meanwhile, painted surfaces were analyzed by using an X-Ray Fluorescent (XRF) gun on site for identification of lead concentrations. Each suspect asbestos-containing material (ACM) identified, was bulk sampled in general accordance with sampling guidelines established by the

Environmental Protection Agency and 29 CFR 1926.1101. Each suspect painted surface was analyzed in accordance with EPA, HUD, CDPH and OSHA protocols. The following summarizes the sampling procedures utilized.

Bulk samples were collected by qualified Guzi-West personnel using appropriate sampling tools and leak-tight containers.

Decontamination of bulk sampling tools was used to prevent the spread of secondary contamination to subsequent bulk samples.

Each sample was individually numbered, recorded on a Sample Log, and submitted under chain-of-custody documentation to accredited laboratories.

The locations of all samples were marked on a site map for the project, please see Appendix A.

The asbestos samples were analyzed by the methodology specified under App.

E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116.

The lead samples were analyzed by using a Viken Pb200i XRF on-site.

Crystal Creek Boys Camp Page 14

CONCLUSIONS AND RECOMMENDATIONS

As explained in detail in the Executive Summary, numerous asbestos-containing materials were identified during the survey. The caulking, tan 9”x9” vinyl floor tiles and associated mastic (from Building 905), cementitious siding, tan 9”x9” vinyl floor tiles and mastic, gold 12”x12” vinyl floor tiles, and yellow mastic associated with the gray 12”x12” vinyl floor tiles (all from Building 914) are non-friable and contain greater than 1% asbestos. DTSC considers non-friable bulk asbestos-containing waste to be non-hazardous regardless of its asbestos content; therefore, it is not subject to regulation under Title 22, Division 4.5, of the California Code of Regulations. However, the material must be removed, handled and disposed of in a manner that keeps the material intact to be considered non-friable. The method of removal cannot crumble, pulverize or reduce the material to dust. Sanding, sawing, grinding, chipping or use of power tools is not allowed. If the material cannot be removed without breaking, you must follow the requirements for abatement, and disposal, of friable asbestos-containing materials.

Certified asbestos abatement workers must remove all materials containing asbestos that will be disturbed during the subject project, regardless of their asbestos content, due to

Cal-OSHA regulations. A NESHAP notification is required due to the project involving a demolition. The NESHAP notification must be submitted a minimum of 10 working days prior to conducting any site disturbance activities; a blank NESHAP notification form is provided in Appendix D.

Both lead-containing paint, and lead-based paint were identified at the subject project;

please see the XRF report provided in Appendix C. Since lead-based paint was identified and greater than 100 square feet will be disturbed as part of the project, a pre-project notification must be submitted to Cal-OSHA at least 24 hours prior to any disturbance, a template is provided in Appendix E. Prospective contractors should have training in accordance with the requirements of Title 8, California Code of Regulations, Section

1532.1 and ensure proper worker protection is utilized during any disturbance of paint containing lead.

Crystal Creek Boys Camp Page 15

Asbestos and lead regulations are complicated and are subject to change. The intent of the above information is to advise you of some of the regulations that may affect you, but is not intended to be an all-encompassing discussion of asbestos and lead waste regulations. The sole purpose of this investigation and of this report is to assess the site with respect to asbestos-containing materials and painted surfaces containing regulated levels of lead. Guzi-West is not responsible for identifying asbestos-containing building materials beyond the defined project scope. This report has been prepared on behalf of and for the exclusive use of National Park Service and is subject to and issued in connection with the agreement and the provisions thereof.

APPENDIX A

Site Maps

Datum: North American Datum 1983 Projection: StatePlane California I FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Site Map

Water Fountain

Propane Tank

Water Tanks

906905

0 25 50 75 100 feet

Last Modified On: 3/21/2025 Project Number: 2025-182

Crystal

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Creek Road

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as architectural or engineering plans.

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Building 902 & 903

MIDDLE ROOM

FRONT

ROOM

BACK ROOM

BATHROOM

10b

10a

2b

6b

3b

1b

5b

4b

7b

3a

5a

8a

7a 6a

1a

9a

2a

4a

1c

6c 7c

Lx10

Lx4

Lx1

Lx2

Lx3

Lx9

Lx8

Lx7

Lx6

Lx5

0 5 10 15 20 feet

Last Modified On: 3/21/2025 Project Number: 2025-182

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Building 904

0 1 2 3 4 5 feet

11b

11a

Lx17

Lx18

Lx16

Last Modified On: 3/21/2025 Project Number: 2025-182

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Building 905 & 906

0 5 10 15 feet

FRONT

AREA

STORAGE 3

STORAGE 2

STORAGE 1

BACK AREA

90615a-b

16a-b

14a-b

13b

12b

18b

13a

12a

17a

18aLx11

Lx12

Lx13 Lx15

Lx14

Lx20

Lx19

Lx21

Last Modified On: 3/21/2025 Project Number: 2025-182

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Building 908

23b

19b

20a

21a

22a

23a

19a

Lx22

Lx27

Lx24

Lx23

Lx25

Lx26

0 5 10 15 feet

Last Modified On: 3/21/2025 Project Number: 2025-182

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Propane Tank

0 3 6 9 12 feet

48b

48a

Lx28

Lx29

Lx30

Last Modified On: 3/21/2025 Project Number: 2025-182

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Building 915

0 1 2 3 4 5 feet

MAIN AREA

28b

27b

26b

28a

27a

24a

25a

26a

28c

27c

Lx43 Lx44

Lx45

Lx46

Lx48

Lx47

Last Modified On: 3/21/2025 Project Number: 2025-182

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Building 914

HALL

BR 3

BR2

BR1

44a-b 47a-b

36a-b

39a-b

42a-b

40a-b

41a-b

37a-b

38a-b

45a-b

46a-b

33b-c 35b-c

43a-c

32b

34b

29b

29a

30a 31a

34a

33a

35a

32a

34c

Lx42 Lx37

Lx36

Lx35

Lx34

Lx40

Lx41

Lx39

Lx38

Lx31 Lx33

Lx32

Lx49

Lx50

0 3 6 9 12 feet

Last Modified On: 3/21/2025 Project Number: 2025-182

P e r g o l a F r a m i n g

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Water Treatment

Building 208

52a-b

50a-b 49a-c

53b

53a

57a

51a

50c

Lx51

Lx52

Lx53

0 5 10 15 20 feet

Last Modified On: 3/21/2025 Project Number: 2025-182

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

FIPS 0401 Feet Cartographer: Taylor Bradley

Crystal Creek Boys Camp Water Fountain

WATER FOUNTAIN

54a-b

0 5 10 15 20 feet

Last Modified On: 3/21/2025 Project Number: 2025-182

NOT TO SCALE - FOR APPROXIMATION ONLY

Crystal Creek Road Ono, CA 96047

North

Asbestos Samples

Non-Detect

Positive Asbestos Sample

Lead Samples

Non-Detect

Lead-Based Paint

Lead-Containing Paint

Disclaimer: Sample locations on map are estimated. They do not represent all homogenous areas where this material may be found. Map is not intended to function as

APPENDIX B

Asbestos Laboratory Data and Chain-of-Custody

Client:

Project Name:

Project Address:

Project No.:

Methodology:

T/A Time:

Project Contact :

PEL Sample No.

Client

Sample No.:

Composition Color Description

Asbestos

Presence/Absence

& Type (if present)

Non-Asbestos

Fiber Type

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected

14A Layered Off-White

Joint

Compound

Calcium

Carbonate

15 7A Homogeneous Off-White Texture

Calcium

Carbonate

13A Layered Off-White

Joint

Compound

Calcium

Carbonate

14 6C Layered Off-White Drywall Gypsum

12A Layered Off-White

Joint

Compound

Calcium

Carbonate

13 6B Layered Off-White Drywall Gypsum

11 5B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

12 6A Layered Off-White Drywall Gypsum

8 4A Homogeneous Yellow Mastic Glue

9 4B Homogeneous Yellow Mastic Glue

7 3B Homogeneous Off-White Window Glaze

Calcium

Carbonate

Window Glaze

Calcium

Carbonate

3 1C Homogeneous Gray Concrete

Calcium

Carbonate Quartz

4 2A Homogeneous Off-White Window Glaze

Calcium

Carbonate

Concrete

Calcium

Carbonate Quartz

5 2B Homogeneous Off-White Window Glaze

Calcium

Carbonate

6 3A Homogeneous Off-White

Non-Fibrous Matrix Types

App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116 Received By: Bobby Ingram

1 1A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

2 1B Homogeneous Gray

3-day Analyzed By: Bobby Ingram

Jeff Hunter Sample Date: 3/19/2025

Guzi-West PEL Client No.: 1

Crystal Creek Boys Camp PEL Work Order No.: 12503136

Crystal Creek Boys Camp, Whiskeytown Date Received: 3/19/2025

2025-182 Date Analyzed: 3/19-20/25

10 5A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

5200 Industrial Way, Suite F | Anderson, CA 96007 | 530-261-2046

Asbestos Reporting Template Anderson REV 1.1 Page 1 of 8

Project Address:

Project No.:

Methodology:

Sample No.:

Composition Color Description

Asbestos

Presence/Absence

& Type (if present)

Non-Asbestos

Fiber Type % Non-Fibrous Matrix Types

App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116 Received By: Bobby Ingram

3-day Analyzed By: Bobby Ingram

Jeff Hunter Sample Date: 3/19/2025

Guzi-West PEL Client No.: 1

Crystal Creek Boys Camp PEL Work Order No.: 12503136

Crystal Creek Boys Camp, Whiskeytown Date Received: 3/19/2025

2025-182 Date Analyzed: 3/19-20/25

5200 Industrial Way, Suite F | Anderson, CA 96007 | 530-261-2046

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected Glass Fibers 100

No Asbestos Detected Glass Fibers 100

No Asbestos Detected Cellulose 75

Glass Fibers 20

No Asbestos Detected Cellulose 75

Glass Fibers 20

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected Cellulose 95

No Asbestos Detected Cellulose 95

Chrysotile 5.00

Chrysotile 5.00

Chrysotile 5.00

Chrysotile 5.00

32 16A Homogeneous Black Mastic Glue

33 16B Homogeneous Black Mastic Glue

30 15A Homogeneous Tan Vinyl Floor Tile

Calcium

Carbonate Binder

31 15B Homogeneous Tan Vinyl Floor Tile

Calcium

Carbonate Binder

28 14A Homogeneous Off-White

Acoustical

Ceiling Tile Paint

29 14B Homogeneous Off-White

Acoustical

Ceiling Tile Paint

26 13A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

27 13B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

24 12A Homogeneous Off-White Window Glaze

Calcium

Carbonate

25 12B Homogeneous Off-White Window Glaze

Calcium

Carbonate

22 11A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

23 11B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

20 10A Homogeneous Off-White

Acoustical

Ceiling Tile Paint

21 10B Homogeneous Off-White

Acoustical

Ceiling Tile Paint

18 8A Homogeneous Pink Insulation

19 9A Homogeneous Yellow Insulation

16 7B Homogeneous Off-White Texture

Calcium

Carbonate

17 7C Homogeneous Off-White Texture

Calcium

Carbonate

Asbestos Reporting Template Anderson REV 1.1 Page 2 of 8

Project Address:

Project No.:

Methodology:

Sample No.:

Composition Color Description

Asbestos

Presence/Absence

& Type (if present)

Non-Asbestos

Fiber Type % Non-Fibrous Matrix Types

App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116 Received By: Bobby Ingram

3-day Analyzed By: Bobby Ingram

Jeff Hunter Sample Date: 3/19/2025

Guzi-West PEL Client No.: 1

Crystal Creek Boys Camp PEL Work Order No.: 12503136

Crystal Creek Boys Camp, Whiskeytown Date Received: 3/19/2025

2025-182 Date Analyzed: 3/19-20/25

5200 Industrial Way, Suite F | Anderson, CA 96007 | 530-261-2046

No Asbestos Detected Glass Fibers 100

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected Glass Fibers 100

No Asbestos Detected Glass Fibers 100

No Asbestos Detected Glass Fibers 100

No Asbestos Detected Glass Fibers 15

No Asbestos Detected Glass Fibers 15

No Asbestos Detected Glass Fibers 100

No Asbestos Detected Glass Fibers 100

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

49 27B Layered Off-White Drywall Gypsum

49A Layered Off-White

Joint

Compound

Calcium

Carbonate

48 27A Layered Off-White Drywall Gypsum

48A Layered Off-White

Joint

Compound

Calcium

Carbonate

46 26A Homogeneous Off-White Window Glaze

Calcium

Carbonate

47 26B Homogeneous Off-White Window Glaze

Calcium

Carbonate

44 24A Homogeneous Yellow Insulation

45 25A Homogeneous Pink Insulation

42 23A Homogeneous Pink

Electrical

Conduit Binder

43 23B Homogeneous Pink

Electrical

Conduit Binder

40 21A Homogeneous Yellow Insulation

41 22A Homogeneous White Insulation

38 19B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

39 20A Homogeneous Pink Insulation

36 18B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

37 19A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

34 17A Homogeneous Pink Insulation

35 18A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

Asbestos Reporting Template Anderson REV 1.1 Page 3 of 8

Project Address:

Project No.:

Methodology:

Sample No.:

Composition Color Description

Asbestos

Presence/Absence

& Type (if present)

Non-Asbestos

Fiber Type % Non-Fibrous Matrix Types

App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116 Received By: Bobby Ingram

3-day Analyzed By: Bobby Ingram

Jeff Hunter Sample Date: 3/19/2025

Guzi-West PEL Client No.: 1

Crystal Creek Boys Camp PEL Work Order No.: 12503136

Crystal Creek Boys Camp, Whiskeytown Date Received: 3/19/2025

2025-182 Date Analyzed: 3/19-20/25

5200 Industrial Way, Suite F | Anderson, CA 96007 | 530-261-2046

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

Chrysotile 20.00

Chrysotile 20.00

Chrysotile 0.50

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

Chrysotile 0.50

Chrysotile 1.25

Chrysotile 0.75

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

64 34B Layered Off-White Drywall Gypsum

64A Layered Off-White

Joint

Compound

Calcium

Carbonate

63 34A Layered Off-White Drywall Gypsum

63A Layered Off-White

Joint

Compound

Calcium

Carbonate

400 Point Count 33B Homogeneous Off-White Caulk

Calcium

Carbonate

400 Point Count 33C Homogeneous Off-White Caulk

Calcium

Carbonate

59 32B Homogeneous Black

Moisture

Barrier Tar

400 Point Count 33A Homogeneous Off-White Caulk

Calcium

Carbonate

57 31A Homogeneous Black Mastic Glue

58 32A Homogeneous Black

Moisture

Barrier Tar

55 29B Homogeneous Gray

Cementitious

Siding

Calcium

Carbonate Binder

400 Point Count 30A Homogeneous Silver Paint

53 28C Homogeneous Off-White Texture

Calcium

Carbonate

54 29A Homogeneous Gray

Cementitious

Siding

Calcium

Carbonate Binder

51 28A Homogeneous Off-White Texture

Calcium

Carbonate

52 28B Homogeneous Off-White Texture

Calcium

Carbonate

50 27C Layered Off-White Drywall Gypsum

50A Layered Off-White

Joint

Compound

Calcium

Asbestos Reporting Template Anderson REV 1.1 Page 4 of 8

Project Address:

Project No.:

Methodology:

Sample No.:

Composition Color Description

Asbestos

Presence/Absence

& Type (if present)

Non-Asbestos

Fiber Type % Non-Fibrous Matrix Types

App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116 Received By: Bobby Ingram

3-day Analyzed By: Bobby Ingram

Jeff Hunter Sample Date: 3/19/2025

Guzi-West PEL Client No.: 1

Crystal Creek Boys Camp PEL Work Order No.: 12503136

Crystal Creek Boys Camp, Whiskeytown Date Received: 3/19/2025

2025-182 Date Analyzed: 3/19-20/25

5200 Industrial Way, Suite F | Anderson, CA 96007 | 530-261-2046

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

Chrysotile 0.25

Chrysotile 0.25

No Texture Present

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

Chrysotile 7.00

Chrysotile 7.00

Chrysotile 5.00

Chrysotile 5.00

No Asbestos Detected

78 40B Homogeneous Black Mastic Glue

79 41A Homogeneous Gray Vinyl Floor Tile

Calcium

Carbonate Binder

76 39B Homogeneous Tan Vinyl Floor Tile Vinyl

77 40A Homogeneous Black Mastic Glue

74 38B Homogeneous Yellow Mastic Glue

75 39A Homogeneous Tan Vinyl Floor Tile Vinyl

72 37B Homogeneous Gray

Sheet Vinyl

Flooring Vinyl

73 38A Homogeneous Yellow Mastic Glue

70A Layered Yellow Mastic Glue

71 37A Homogeneous Gray

Sheet Vinyl

Flooring Vinyl

69A Layered Yellow Mastic Glue

70 36B Layered Brown Cove Base Rubber

68 35C Texture

69 36A Layered Brown Cove Base Rubber

400 Point Count 35A Homogeneous Off-White Texture

Calcium

Carbonate

400 Point Count 35B Homogeneous Off-White Texture

Calcium

Carbonate

65 34C Layered Off-White Drywall Gypsum

65A Layered Off-White

Joint

Compound

Calcium

Asbestos Reporting Template Anderson REV 1.1 Page 5 of 8

Project Address:

Project No.:

Methodology:

Sample No.:

Composition Color Description

Asbestos

Presence/Absence

& Type (if present)

Non-Asbestos

Fiber Type % Non-Fibrous Matrix Types

App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116 Received By: Bobby Ingram

3-day Analyzed By: Bobby Ingram

Jeff Hunter Sample Date: 3/19/2025

Guzi-West PEL Client No.: 1

Crystal Creek Boys Camp PEL Work Order No.: 12503136

Crystal Creek Boys Camp, Whiskeytown Date Received: 3/19/2025

2025-182 Date Analyzed: 3/19-20/25

5200 Industrial Way, Suite F | Anderson, CA 96007 | 530-261-2046

No Asbestos Detected

No Asbestos Detected

Chrysotile 7.00

No Asbestos Detected

Chrysotile 7.00

Chrysotile 0.75

Chrysotile 0.50

Chrysotile 0.75

No Asbestos Detected Cellulose 95

No Asbestos Detected Cellulose 95

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

Chrysotile 5.00

No Asbestos Detected

Chrysotile 5.00

No Asbestos Detected

No Asbestos Detected

89 45B Homogeneous Gray Vinyl Floor Tile

Calcium

Carbonate Binder

86 44A Homogeneous Off-White

Acoustic

Ceiling Tile Paint

87 44B Homogeneous Off-White

Acoustic

Ceiling Tile Paint

88 45A Homogeneous Gray Vinyl Floor Tile

Calcium

Carbonate Binder

400 Point Count 43B Homogeneous Off-White Texture

Calcium

Carbonate

400 Point Count 43C Homogeneous Off-White Texture

Calcium

Carbonate

82A Layered Black Mastic Glue

400 Point Count 43A Homogeneous Off-White Texture

Calcium

Carbonate

81A Layered Black Mastic Glue

82 42B Layered Yellow Mastic Glue

80 41B Homogeneous Gray Vinyl Floor Tile

Calcium

Carbonate Binder

81 42A Layered Yellow Mastic Glue

92 47A Layered Gray Cove Base Rubber

92A Layered Yellow Mastic Glue

91 46B Layered Yellow Mastic Glue

91A Layered Black Mastic Glue

90 46A Layered Yellow Mastic Glue

90A Layered Black Mastic Glue

Asbestos Reporting Template Anderson REV 1.1 Page 6 of 8

Project Address:

Project No.:

Methodology:

Sample No.:

Composition Color Description

Asbestos

Presence/Absence

& Type (if present)

Non-Asbestos

Fiber Type % Non-Fibrous Matrix Types

App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116 Received By: Bobby Ingram

3-day Analyzed By: Bobby Ingram

Jeff Hunter Sample Date: 3/19/2025

Guzi-West PEL Client No.: 1

Crystal Creek Boys Camp PEL Work Order No.: 12503136

Crystal Creek Boys Camp, Whiskeytown Date Received: 3/19/2025

2025-182 Date Analyzed: 3/19-20/25

5200 Industrial Way, Suite F | Anderson, CA 96007 | 530-261-2046

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected Cellulose 10

Glass Fibers 2

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected Glass Fibers 100

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

No Asbestos Detected

105 53A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

106 53B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

103 52A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

104 52B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

101 50C Homogeneous Off-White Texture

Calcium

Carbonate

102 51A Homogeneous Yellow Insulation

99 50A Homogeneous Off-White Texture

Calcium

Carbonate

100 50B Homogeneous Off-White Texture

Calcium

Carbonate

98 49C Layered Off-White Drywall Gypsum

98A Layered Off-White

Joint

Compound

Calcium

Carbonate

97 49B Layered Off-White Drywall Gypsum

97A Layered Off-White

Joint

Compound

Calcium

Carbonate

96 49A Layered Off-White Drywall Gypsum

96A Layered Off-White

Joint

Compound

Calcium

Carbonate

94 48A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

95 48B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

93 47B Layered Gray Cove Base Rubber

93A Layered Yellow Mastic Glue

Asbestos Reporting Template Anderson REV 1.1 Page 7 of 8

Project Address:

Project No.:

Methodology:

Sample No.:

Composition Color Description

Asbestos

Presence/Absence

& Type (if present)

Non-Asbestos

Fiber Type % Non-Fibrous Matrix Types

App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116 Received By: Bobby Ingram

3-day Analyzed By: Bobby Ingram

Jeff Hunter Sample Date: 3/19/2025

Guzi-West PEL Client No.: 1

Crystal Creek Boys Camp PEL Work Order No.: 12503136

Crystal Creek Boys Camp, Whiskeytown Date Received: 3/19/2025

2025-182 Date Analyzed: 3/19-20/25

5200 Industrial Way, Suite F | Anderson, CA 96007 | 530-261-2046

No Asbestos Detected

No Asbestos Detected

Analyst

Signature: Date of Report :

Reviewer

Signature: Date of Report :

107 54A Homogeneous Gray Concrete

Calcium

Carbonate Quartz

108 54B Homogeneous Gray Concrete

Calcium

Carbonate Quartz

3/20/2025

3/20/2025

PEL Laboratories is accredited under the California Environmental Laboratory Accredidation Program (CAELAP) 3109 , for performing polarized light microscopy (PLM) analyses under methods known as App. E to Sub. E of 40 CFR Part 763 and EPA/600/R-93/116. This report must not be used to claim product endorsement by CAELAP or any other agency of the U.S.

Government. These results relate only to the samples tested and must not be reproduced, except in full, without the approval of the laboratory. Although PLM analysis is commonly performed to determine the presence or absence of asbestos in building materials, the EPA methods acknowledge that analysis by PLM is subject to limitations and for certain materials, such as vermiculite and vinyl floor tiles, a more sophisticated methodology may be necessary.

Asbestos Reporting Template Anderson REV 1.1 Page 8 of 8

APPENDIX C

Lead XRF Data

REQUESTED SERVICES – XRF FIELD READINGS

INFORM OCCUPANTS AND ENSURE NO ONE IS PRESENT ON WALL OPPOSITE READINGS

Sample No. / L

XRF

READING

(mg/cm2)

PAINT

CONDITION

Intact/Fair/

Poor

Notes

Page 1 of

Contact Information Project Information

Company: Phone: Project Name:

Contact: Cell Phone: Project Location:

Account #: E-mail: Job Number:

Sam p le d By: Name: Date: PROJECT SAMPLES TAKEN: LEAD ASB MOLD RADON BIO NESHAP: Yes No

5200 Industrial Way Suite F, Anderson, CA 96007

888-351-8189 | info@guziwest.com

Project Information

Company: Project Name: Project Location:

Sampled By

Page 2 of

5200 Industrial Way Suite F, Anderson, CA 96007

888-351-8189 | info@guziwest.com

REQUESTED SERVICES – XRF FIELD READINGS

INFORM OCCUPANTS AND ENSURE NO ONE IS ON WALL OPPOSITE READINGS

Sample No.

XRF

READING

(mg/cm2)

PAINT

CONDITION

Intact/Fair/

Poor

NOTES

Sampled By

Page 3 of

5200 Industrial Way Suite F, Anderson, CA 96007

888-351-8189 | info@guziwest.com

REQUESTED SERVICES – XRF FIELD READINGS

INFORM OCCUPANTS AND ENSURE NO ONE IS ON WALL OPPOSITE READINGS

Sample No.

XRF

READING

(mg/cm2)

PAINT

CONDITION

Intact/Fair/

Sampled By

Page 4 of

5200 Industrial Way Suite F, Anderson, CA 96007

888-351-8189 | info@guziwest.com

REQUESTED SERVICES – XRF FIELD READINGS

INFORM OCCUPANTS AND ENSURE NO ONE IS ON WALL OPPOSITE READINGS

Sample No.

XRF

READING

(mg/cm2)

PAINT

CONDITION

Intact/Fair/

APPENDIX D

NESHAP Notification Form

State of California California Environmental Protection Agency Air Resources Board

ED/ESB/DSS – 151 (REV 09/15)

POSTMARK: _______________

DATE RECEIVED: _______________

NOTIFICATION #: _______________

ASBESTOS NESHAP NOTIFICATION OF DEMOLITION AND RENOVATION FORM

Attention – This Form is for Non-Delegated Air Districts in California Only

(More Information http://www.arb.ca.gov/enf/asbestos/asbestos.htm)

I. TYPE OF NOTIFICATION: (check one)

ORIGINAL | CANCELED | REVISION (IF REVISION, WRITE REVISION #: _________)

II. FACILITY INFORMATION (Identify Owner, Removal Contractor, and Other Operator)

Owner Name:

Address:

City: County: State: ZIP:

Contact: Telephone:

Asbestos Removal Contractor:

Address:

City: State: ZIP:

Contact: Telephone: Title:

Demolition Contractor:

Address:

City: State: ZIP:

Contact: Telephone: Title:

III. TYPE OF OPERATION: (check one)

DEMOLITION | ORDERED DEMOLITION | RENOVATION | EMERGENCY RENOVATION

IV. IS ASBESTOS PRESENT? (check one)

YES | NO

Please attach Asbestos Inspection Report (40 CFR 61.145(a) )

What Asbestos Containing Materials are Going to be Removed:

V. NAME OF…