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LEITE ADD BK 6 LT 1A - ZCP 7/2/2026Kodiak Island Borough Community Development Department 710 Mill Bay Road Room 202 Kodiak, Alaska 99615 Phone (907) 486-9363 Fax (907) 486-9396 bcurrie@kodiakak.us Zoning Compliance Permit Permit No. Ct2Z7,U -()TU The following information is to be supplied by the Applicant Property Owner/Applicant: Tommy Cornell — J,QhOUah3 warym 4mok- Mailing Address: 632 W 19th Ave Anchorage Alaska 99503 United States Phone Number: Other Contact Email, etc..: tmmy@cornellpermits.com Legal Description: Subdv: Le e- Ja6J. Block: �_ Lot: Street Address: 1514 Mission Rd Use & Size of Existing Structures: A-3 (PLACE OF RELIGIOUS WORSHIP) 2394 SF Description of Proposed Action: RENOVATION OF (E) SINGLE STORY, WOOD FRAMED, PLACE OF WORSHIP. EXTERIOR PAINT, UPGRADE (E) INTERIOR FINISHES, ROOF REPLACEMENT, ACCESSIBILITY IMPROVEMENTS, REPLACEMENT OF OIL FIRED FURNACE, LIGHTING FIXTURES W/ LED AND MAIN ELEC PANELAND DISCONNECT Applicant Certification: I hereby certify that I will comply with the provisions ofthe Kodiak Island Borough Code and that I have the authority to certify this as the property owner. or as a representative of the property owner. I agree to have identifiable corner markers in place for verification of building setback (yard) requirements. Title: Representative Print Name: Thomas Cornell Date: 1/19/26 Signature: ° Site Plan to include lot boundaries and existing easements and buildings, rop to ation ofnew construction, access points, and vehicular parking area, As -Built required with all improvements changes. This permit is only for the proposed project as described by the applicant. If there are any changes to the proposed project, including its intended use, prior to or during its siting, construction, operation, contact this office immediately to determine iffurther review and approval of the revised project is necessary. THIS FORM DOES NOT AUTHORIZE CONSTRUCTION WHEN A BUILDING PERMIT IS REQUIRED. Staff Compliance Review Does the Project involve EPA v(b Proof of EPA notification provided (if required)? Defined Facility? 'Commerical Buildi gs, — -Required for all demos, renovations disturbing at least UO sq Installations, institutions, and residences feet, 260 lineafeet, or 35 cubic ft of Regulated Asbestos Containing With more than four (4) dwelling unites' Material (RACM) and for renovation that remove load supporting structure` Expiration: Any Zoning Compliance Permit issued is subject to the same expiration, suspension, and revocation provisions as a building permit issued for the same construction permit. Current Zoning: U - I .� Prop. ID: 1JC`7 I t Lot Area: _ 6q Lot Width: Building Height:15 J� Front Yard: a5i Side Yard: �' %nrs� 540iRear Yard: 1 ' -r Parking Plan: ��)j Parking Spaces: As -Built: if Pf 1 Date: 1I'd Payment Verification Staff Certification CDD Staff Signature: Waived: $0.00 0 Less than 1.75 Acres: $30.00 1.76 to 5.00 Acres: $60.00 ❑ 5.01 to 40.00 Acres: $90.00 ❑ 40.01 Acres or more: $120.00 ❑ After the Fact 2X the published amount $0.00 ❑ $60.00 ❑ $120.00 ❑ $180.00 ❑ $240.00 ❑ Transaction Receipt- Success Kodiak Island Borough Kodiak Island Borough Community Development MID:200006988265 710 Mill Bay Road Kodiak, AK 99615 907-486-9323 01/26/2026 09:29AM Remittance ID: Kodiak01262613252863 7 Wal Transaction ID: 346161774 GEOFF WOODS 1005 Red Mills Road WALLKILL, New York 12589 United States MasterCard - 8879 Approval Code: 088468 Sale Amount: $30.00 Tommy Cornell - Jehovahs Witness Kodiak n/a 2026-026 1514 Mission Road Service Fee: $2.00 Service Fee Type: Dual Transaction Total Amount: $32.00 Cardmember acknowledges receipt of goods and/or services in the amount of the total shown hereon and agrees to perform the obligations set forth by the cardmember's agreement with the issuer. Signature click here to continue. KODIAK CONGREGATION OF JEHOVAH'S WITNESSES Physical address: 1514 Mission Rd Kodiak, AK 99615 January 10, 2026 To Whom It May Concern: Mailing address: c/o Joshua Gutierrez 212 Murphy Way Apt 1 Kodiak, AK 99615 This letter is to authorize Geoffrey Woods, Michael Davis, Christopher J. Check, and/or Thomas A. Cornell to represent the owners and titleholders of the property at 1514 Mission Road, Kodiak, Alaska regarding property development, and including any zoning, site or construction improvements that may be pursued or occur in the future. This includes meetings with municipal representatives, permitting, submittal applications and documentation, payments and financial requirements, municipal hearings both private and public, as well as project and process progress approvals and authorizations. Respectfully submitted, W. Smith (Trustee) Date Signature Hazardous Building Materials Survey Project Name / Location: Kingdom Hall Kodiak HBMS Kodiak, AK Prepared For: JW Congregation Support, Inc. Mr. Charlie McKenrick 1005 Red Mills Road Wallkill, NY 12589 Prepared By: Satori Group, Inc. 1310 E 661h Avenue, Suite 2 Anchorage, AK 99518 907-332-0456 Tax ID:92-0176507 Date Submitted: April 3, 2025 GROUP pE Table of Contents ExecutiveSummary......................................................................................................... 1 1.0 Introduction............................................................................................................... 3 1.1 Objective & Inspection Protocol....................................................................................................3 1.2 Building Information....................................................................................................................3 L3 Subcontractors/Vendors................................................................................................................4 2.0 Hazardous Materials Overview................................................................................... 5 2.1 Asbestos........................................................................................................................................ 5 2.2 Lead.............................................................................................................................................. 6 3.0 Other Hazardous Materials......................................................................................... 7 3.1 Polychlorinated Biphenyls (PCBs)................................................................................................7 3.2 Ozone Depleting Sources and Radioactive Materials....................................................................7 3.3 Mercury, Lead and Chemicals......................................................................................................7 3.4 Mold Overview.............................................................................................................................. 8 4.0 Methodology............................................................................................................... 9 4.1 Pre -Sampling Activities.................................................................................................................9 4.2 Asbestos Sampling........................................................................................................................ 9 4.3 Lead Testing and Sampling.........................................................................................................10 4.4 Mold Visual Inspection............................................................................................................... 10 4.5 Mold Air Sampling......................................................................................................................11 5.0 Results & Conclusions.............................................................................................. 12 5.1 Asbestos Findings.......................................................................................................................12 5.2 Lead Findings.............................................................................................................................16 5.3 Mold Findings.............................................................................................................................16 6.0 Limitations............................................................................................................... 18 7.0 Signatory..................................................................................................................18 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 Fax 907.332.0457 www.gosatori.conn Appendices APPENDIX A: Laboratory Results & Chain of Custody Records APPENDIX B: XRF Performance Characteristic Sheet & XRF Data APPENDIX C: Sample Location Diagrams APPENDIX D: Inspector Certifications APPENDIX E: Site Photographs 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 v .gosatori.com Acronyms & Abbreviations ACM Asbestos Containing Materials AHERA Asbestos Hazard Emergency Response Act ASHARA Asbestos School Hazard Abatement Reauthorization Act CFR Code of Federal Regulations COC Chain of Custody EPA Environmental Protection Agency HEPA High Efficiency Particulate Air HBMS Hazardous Building Materials Survey HUD Housing and Urban Development LBP Lead -Based Paint mg/cm2 Milligram per centimeter squared NESHAP National Emissions and Standards for Hazardous Air Pollutants NVLAP National Voluntary Lab Accreditation Program OHMs Other Hazardous Materials OSHA Occupational Safety and Health Administration PCB Polychlorinated Biphenyl PLM Polarized Light Microscopy RCRA Resource Conservation Recovery Act TSCA Toxic Substance Control Act XRF X-Ray Fluorescence 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 1 w vgosatori.com Executive Summary Satori Group, Inc. (herein Satori) was contracted by JW Congregation Support, Inc. (herein Client) to conduct a Hazardous Building Materials Survey (HBMS) for Asbestos Containing Materials (ACM), Lead -Based Paint (LBP), and Mold at Kingdom Hall Kodiak located at 1514 Mission Road in Kodiak, Alaska. The information contained within this report is intended as a guide for workers who may come into contact with hazardous materials during daily routine work, renovations, or demolition activities. If building materials or chemicals are discovered that are not specified in this report, assume materials are hazardous before proceeding. Consider engaging Satori to conduct additional sampling and analysis for proper characterization. Asbestos Summary All asbestos samples collected during this survey inspection were analyzed in compliance with US EPA Polarized Light Microscopy (PLM) Method 600/R-93/116. The Environmental Protection Agency (EPA) and Occupational Safety and Health Administration (OSHA) regulations define ACM as "any material that contains greater than 1% asbestos". A total of twenty (20) samples (45 layers) were collected from Kingdom Hall Kodiak during the sampling process. Based on review of the laboratory analytical data, asbestos was detected in two samples collected during this inspection at concentrations greater than 1%. The following summarizes the materials, with their respective quantities, that were identified as ACM during this inspection: • Gray/various/Beige Sheet Vinyl Flooring in the Utility Room (NW side) (55 SF) • Gray/Red Sheet Vinyl Flooring in the Utility Room (SW side) (same material as above) In addition, four sample layers, A31679-05-Joint Compound, A31679-06-Joint Compound 1, A31679-06-Joint Compound 2, and A31679-07-Joint Compound contained <1 % Chrysotile asbestos. While this is not above the EPA regulatory limit, the presence of asbestos was detected. Materials that contain <1 % asbestos are covered by Occupational Safety and Health Administration (OSHA) asbestos regulations which mandate specific engineering controls, work practices and prohibitions. Based on review of the laboratory analytical data, the remaining samples of suspect materials collected during this inspection contained no detectable levels of asbestos. Lead Summary LBP testing was performed using a VikenTm X-Ray Fluorescence (XRF) analyzer. 1.0 mg/cm2 is the value currently recognized by the US Department of Housing and Urban Development (HUD) as the minimum amount of lead required to be present in paints/finishes in order to be considered lead -based paint. 1 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907,332.0456 1 Fax 907.332.0457 1 w .gosatori.mm Based on review of the XRF analyzer results, lead levels (if any) from the surfaces sampled during this inspection fall below this value. Mold Summary A visual assessment for mold was conducted throughout the project areas that involved visually identifying any suspected mold growth or conditions conducive to mold growth. During the inspection, the following conditions were identified: • Discoloration on the ceiling tile in the meeting room Review of the spore trap laboratory results revealed no detectable spores in any interior locations. All regulated materials identified within this report should be removed by workers with proper training. All removed hazardous items must be properly segregated and disposed of in accordance with applicable governing regulations. Trained environmental professionals can assist to guide this process during project designs. 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 www.gosatori.com 1.0 Introduction 1.1 Objective & Inspection Protocol The purpose of Satori's survey inspection is to identify and assess ACM, LBP, and mold at the Kingdom Hall Kodiak, located at 1514 Mission Road in Kodiak, Alaska. Satori's inspection was limited to specific areas and building materials, as requested by the client. Satori's personnel and all necessary equipment/supplies were mobilized on March 20, 2025 by commercial airline for the fieldwork conducted at the subject site on March 21, 2025. The site inspection and sampling were conducted by Ms. Anna Schemer. Ms. Scheiner is a certified AHERA Building Inspector (Building Inspector# TB14-1024-19699) for ACM, certified Lead -Based Paint Inspector (Lead Inspector# LBP-I-1252729-1), certified Residential Mold Inspector (Inspector# CRMI0000046289), and is certified to handle hazardous materials via the HAZWOPER 40-hour course. All appropriate accreditations are attached herewith (Appendix D). The information contained within this report is designed to aid in the management, abatement, and/or disposal of asbestos, lead and/or mold identified. While on -site, Satori's inspector gathered key information in regards to the subject building, such as total square footage of the structure, composition, and condition to guide renovation or demolition activities. The following tasks were completed by Satori's inspector to ensure all necessary information was captured to meet the inspection requirements: • Conduct hazardous building materials survey, including asbestos, lead, and mold inspections, in specific areas as outlined by the Client. • Inventory, locate and assess potential asbestos and lead -containing materials. • Utilize XRF analyzer for the LBP testing. • Conduct visual inspection for mold. • Collect spore trap samples to identify potential mold. • Submit all asbestos and mold samples collected to a certified third -party laboratory for analysis. 1.2 Building Information The subject building is a single story building of approximately 2,100 square feet. The building is currently used as a Kingdom Hall of Jehovah's Witnesses and consists of an auditorium, meeting room, main lobby, two restrooms, and utility room. The building exterior was constructed with wood siding, except for one area near the front door with stone siding, and two separate roof systems. The two roof systems appeared to be of similar construction, with the lower roof portion covering the main lobby and restrooms and the upper portion covering the remaining areas. The building appeared to have two main entrances, with 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 . Fax 907.332.0457 1 www.gosatori.com the front door located on the northwest side and a side door leading to the auditorium on the southwest side. A third exterior door was located on the east side of the building, but remained locked during the inspection. The windows throughout the facility were vinyl with wooden casings, while exterior doors were constructed with metal frames and panels. Additionally, there was an exterior wooden walkway leading to the front door and wrapping around to the northeast side of the building. The building interior was constructed with gypsum wallboard walls, a drop ceiling rile grid, and various types of flooring materials including carpet, sheet vinyl, and vinyl floor tile. Heating, ventilation, and air conditioning (HVAC) ducting was located within the ceiling plenum, and an HVAC unit was located in the utility room. Interior doors were constructed with wooden frames and panels. Additionally, an access hatch to a crawlspace was located in the utility room. However, the crawlspace was not included in the scope of this project and was not inspected as part of this survey. 1.3 Subcontractors/Vendors All physical asbestos samples collected during this inspection were submitted to and analyzed by LA Testing, Inc. (LA Testing), located in Huntington Beach, California. The analysis method was PLM Method 600/R-93/116. LA Testing holds a current National Voluntary Lab Accreditation Program (NVLAP Lab Code: 101384-0) accreditation for all appropriate fields -of - testing. All spore trap mold samples collected during this inspection were submitted to and analyzed by Eurofins EMLab P&K Laboratory (Eurofins), located in San Diego, California. The analysis method was direct microscopic qualitative examination. Eurofrns holds a current Environmental Microbiology Laboratory Accreditation Program (EMLAP Laboratory ID: LAP-160266) accreditation for all appropriate fields -of -testing. 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 1 w .gosatori.com 2.0 Hazardous Materials Overview The following section describes the origin of the hazardous materials (asbestos and LBP), the typical locations the hazardous items can be found in, along with any correlating definitions used when dealing with these materials. 2.1 Asbestos Asbestos is a naturally occurring mineral that can be divided into two mineral groups — serpentine and amphibole. The divisions between the two types of asbestos are based upon the crystalline structure. Serpentines have sheet, or layered like structure where amphiboles have a chain -like structure. Chrysotile, amosite, crocidolite, tremolite, anthophyllite and actinolite make up the list of asbestos fibers. Chrysotile, the only member of the serpentine group, is the most common type of asbestos found in buildings. Approximately 90-95% of asbestos containing material in buildings will consist of Chrysotile in the United States Asbestos is often referred to Suspect Asbestos Containing Materials (ACM) -Floor Tiles and Mastic -Wallboard -Ceiling Texture -Joint Compound -Pipe Insulation -Sound/Fireproofing -Roof Tars and Felts -Cove Base Mastic as "friable" or "non -friable" for classification purposes by the National Emissions and Standards for Hazardous Air Pollutants (NESHAP). Friable asbestos is defined as "crumbled or reduced to powder by hand pressure". Asbestos which is friable or has become friable has a greater likelihood of releasing asbestos fibers into the air, thus having a greater impact on human health. The Asbestos Hazard Emergency Response Act (AHERA) was promulgated in 1986. AHERA mandated that the Environmental Protection Agency (EPA) develop regulations for addressing asbestos in schools. The mandatory AHERA inspector requirement was implemented for any person who performs inspections for ACM on public and commercial buildings; however it failed to include residential apartments or detached single family homes. The Asbestos School Hazard Abatement Reauthorization Act (ASHARA), enacted in 1990 and implemented in 1994, governs the training that asbestos workers, inspectors, supervisors, plan management writers, and abatement designers must receive to become accredited. AHERA instituted the training requirement for any person who inspects for ACM following a recommendation by ASHARA. Asbestos in buildings does not mean an endangerment to workers or occupants unless the condition of the asbestos is damaged or will become damaged or friable due to human or environmental influences. If the building demolition is planned, the EPA requires formal notification 10 business days in advance, regardless of the presence of ACMs. Contractors or property owners submitting EPA notifications must have documentation that an asbestos survey was conducted. Determination regarding the presence or absence of ACMs assist building owners and contractors to mitigate risks to human health and the environment and reduce the potential for regulatory agency citations. 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907,332.0457 1 v .gosatori.conn 2.2 Lead Lead is a heavy, soft, easily worked, silver -bluish metal that is mined out of the earth and has been used for many different applications throughout the centuries. It has been used in pipes, lining for storage vessels, glazing in pottery, added to paint, roofing, electrical conduits, and combined with other metals. Suspect Lead Containine Materials -Paint -Household Dust -Water Pipes and Solders -Batteries -Ceramic Glazes Lead is added to paint for three main reasons: (1) pigment (2) added durability and corrosion control, and (3) as a drying agent. The use of LBP declined due to the introduction of latex and titanium oxide paints. In 1971 Congress made the Lead -Based Paint Poisoning Prevention Act (LBPPPA), which gave a limit to the amount of lead paint could contain. Congress passed legislation to reduce lead -based paint hazards called the Residential Lead Hazard Reduction Act (Title X). The Housing and Urban Development (HUD) agency next created the Guidelines for the Evaluation and Control of Lead -Based Paint Hazards in Housing based on the requirements set forth in Section 402 of Title X. The development of Title X was largely to support reduction of LBP hazards in housing, especially target housing where a potential for childhood lead poisoning exists. The Title X Guidelines use a Federal limit for lead in paint as 1.0 mg/cm2 or more than 0.5% by weight. Section 402 of the Toxic Substance Control Act (TSCA) details the requirements and certifications needed to conduct LBP inspections, risk assessments, and for project designers, supervisors, and abatement workers. OSHA regulates the amount of worker exposure to lead during any disturbance activities as defined in 29 CFR 1926.62 and 29 CFR 1910.1025. Low levels of lead found by XRF testing does not mean that the paints are free of lead; the paints may contain lead, and OSHA regulations apply anytime measurable amounts of lead are present in paints. There are no regulatory requirements to remove LBP from buildings prior to demolition. However, OSHA worker protection requirements must be adhered to by employers and employees when any lead -based materials are disturbed. Burning of lead -based materials is not allowed because lead -based fumes are hazardous. 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 1 www.gosatori.com 3.0 Other Hazardous Materials The following section describes the origin of OHMs, the typical locations the other hazardous items can be found in, along with any correlating definitions used when dealing with these materials. Note that the information contained in Section 3.0 may not be directly related to the inspection services requested or performed by Satori. It is intended as informative background information concerning other potential building hazards, with the objective to protect human health and the environment. 3.1 Polychlorinated Biphenyls (PCBs) PCBs were mainly used for their dielectric and cooling properties in a variety of electric equipment. Additionally, PCBs were also put into various paints and caulking as plasticizers and for corrosion resistance. However, PCBs were identified in the 1960's to be highly toxic to humans and environmentally persistent. PCB production was banned in 1979 by the United States, however, components and products containing PCBs are still found due to the longevity of the material. If components or products containing PCBs are damaged the PCBs can escape and enter and spread through the environment. 3.2 Ozone Depleting Sources and Radioactive Materials Suspect PCBs -Fluorescent Light Ballasts -Paint -Caulk -Cable Insulation -Electrical Equipment -Motor and Hydraulic Oil -Rubber Products Ozone depleting sources (ODS) are found within manufactured refrigerants, solvents, propellants, and foam -blowing agents such as halon fire systems. ODS are split into two groups, Class I - chlorofluorocarbons (CFCs) and Class II — hydrochlorofluorocarbons (HCFCs). Recovery of ODS must be completed by certified technicians according to EPA regulations. Radioactive materials can commonly be found in smoke detectors and older exit signs. Disposal of radioactive sources is required by the United States Nuclear Regulatory Commission (U.S.NRC) under 10 CFR Part 31. 3.3 Mercury, Lead and Chemicals Gas discharge bulbs associated with building lighting systems may contain hazardous chemicals. Florescent lighting fixtures and bulbs are most commonly associated with indoor environments while HID lamps provide bright light for warehouses, supermarkets, or outdoor applications. Fluorescent bulbs and High Intensity Discharge (HID) lamps are examples of systems utilizing mercury vapor. Depending on the age, PCB ballasts may be used to control the current within the light. Emergency lighting systems are commonly required by building safety codes. Rechargeable lead acid and nickel -cadmium batteries are often found within emergency lighting, exit signs, 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 I Fax 907.332.0457 1 w .gosatori.com and security systems. Typically, incandescent or halogen bulbs are included with emergency lighting and exit signs. Some exit signs are constructed using compact mercury containing fluorescent bulbs. Electrical mechanisms using mercury rely on the electrical conductance and ability of mercury to flow as a liquid at room temperature. Most often applications for using mercury are found in thermostats, light switches, and electrical relays. Various paints, solvents, and other chemicals can pose a threat to human health during the demolition process as well as once disposed. Federal laws such as the Resource Conservation and Recovery Act (RCRA), TSCA, and the Low- Level Radioactive Waste Policy Act (LLRWPA) have specific requirements regarding the disposal of these materials. These materials must be identified, removed, and property disposed of before a building is demolished. 3.4 Mold Overview Whether mold exposure comes from one's home or outdoors, humans are exposed to mold daily and it is impossible to avoid. There are over 100,000 types of molds, coming in various shapes, sizes, and colors, making it difficult to differentiate one type of mold from another. Different types of mold can affect humans in various ways, making it essential to identify the specific mold present to assess potential health hazards. The main ways for mold to enter the body are through inhalation, ingestion, and absorption through the skin. When a person is exposed to elevated levels of mold, the body starts to produce antibodies to attack the mycotoxins entering the body. Reactions to these mycotoxins vary among individuals, however repeated exposure can lead to mold sensitivity in those previously unaffected. Typically, one can expect the following types of symptoms: Allergic Rhinitis — Hay fever -like symptoms caused by exposure to airborne mold species. Reaction can happen within a short amount of time. Bronchopulmonary Mycosis — Established mold spores forming colonies in bronchial passageways, producing mycotoxins. If left untreated, it could produce fibrosis of the lung. Allergic Asthma — A reaction to mold spores causing constriction and inflammation of the lungs, triggering an asthmatic response. It is worth noting that not all molds are known to produce mycotoxins, and their impact on human health is still widely debated. Other terminology to consider when dealing with microbial growth are as follows: Viable — Species of mold that can produce mycotoxins while living. Viable mold can still multiply and increase in concentration. Non -Viable — Species of mold that can produce mycotoxins while dead. Non -viable mold will not grow anymore but can still pose some risks. Spores — A spore is the reproductive structure in fungi that may be used for dissemination and may also be resistant to adverse environmental conditions. 1310 East 66th Avenue, Suite 2 j Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 www.gosatori.com 4.0 Methodology 4.1 Pre -Sampling Activities Satori's field personnel conducted a thorough visual inspection of existing on -site conditions prior to any testing/sampling activities. Sampling was initiated only after developing a sampling plan of suspect materials, based upon a visual inspection of the subject areas. The purpose of the inspection was to identify ACM by bulk sampling, LBP materials by VikenTM XRF sampling, and mold by air sampling. Satori reviews and considers the following information during the pre - sampling activity: • Building floorplans, identifying room numbers and functions. • Review of homogeneous areas and functional spaces. • Identifying assumed asbestos and lead materials in various building substrates. 4.2 Asbestos Sampling The asbestos sampling was conducted in compliance with EPA AHERA standards identified in 40 Code of Federal Regulations (CFR) 763 Subpart E, National Emission Standards for Hazardous Air Pollutants (NESHAP) 40 CFR 61 Subpart M, ASTM E 2356-10, and OSHA 29 CFR 1926.1101. All disturbances during sampling were done using hand tools and water to minimize the potential for any airborne hazards. When possible, repairs were made to areas disturbed to mitigate any further spread of contamination (if it existed). After disturbances were complete, the area was cleaned with a High Efficiency Particulate Air (HEPA) vacuum to ensure exposures to potentially hazardous materials were minimized. The location (building / room), composition or substrate description, and matrix of each bulk sample collected were recorded. The asbestos bulk samples are placed in sealed sample bags, given a unique sample number, and sent to a National Voluntary Lab Accreditation Program (NVLAP) approved laboratory under chain -of -custody protocols. Asbestos bulk samples are typically analyzed by PLM Method 600/R-93/116. 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 Fax 907.332.0457 1 www.gosatori.com The below table outlines the asbestos sampling methodology, as it pertains to material category and required minimum sampling. Type of Suspect Material Minimum Sampling Surfacing Material Less than 1000 ftZ 3 samples 1000 — 5000 ft2 5 samples Greater than 5000 ftZ 7 samples Thermal System Insulation Linear pipe 3 samples Pipe elbow or joint 2 samples Patched area I sample Miscellaneous 2 or more samples per homogeneous area of suspect material 4.3 Lead Testing and Sampling Surfaces were tested for LBP using a VikenTm Pb200e XRF analyzer. The XRF analyzer's calibration was verified according to the manufacturer's specifications and in compliance with the Performance Characteristic Sheet (PCS) developed for the instrument. The XRF analyzer irradiates the paint on a given surface causing the lead in the paint, if present, to emit a characteristic frequency of X-Ray radiation. The instrument identifies and counts these X-rays to determine a lead concentration. The intensity of the radiation is measured by the detector and is related to the amount of lead in the paint. Readings from the XRF analyzer yield a 95% confidence level that the result reflects the true level of lead in the surfaces tested. The lead concentration results are report in milligrams per square centimeter (mg/cm). Quantity of paint tests for components are based on the professional judgement of the EPA Lead Inspector when considering EPA and HUD requirements. LBP is defined as any paint or other coating with lead concentrations greater than 1 mg/cmz, or 0.5% (mass of lead per mass of material) by laboratory analysis, per Title X of the 1992 Housing and Community Development Act. 4.4 Mold Visual Inspection The visual inspection performed at 1514 Mission Road was a non-invasive walk through of the premises, during which the inspector assessed problematic areas that could promote the growth of mold. Areas containing moisture, poor ventilation, and a food source for mold were areas of focus for the inspection. Areas that show signs of previous water damage could also be areas of concern for mold growth. 10 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 1 www.gosatori.com The areas of visual inspection included: • Auditorium • Meeting Room • Main Lobby • Restrooms • Utility Room As a result of the visual inspection, photos with descriptive concerns can be found in Appendix E. 4.5 Mold Air Sampling Air sampling was performed in suspected areas to test for potential presence of airborne mold spores using a Zefon BIO-PUMP 0 Plus sampling pump. Before collecting the samples, the sampling pump was properly calibrated to the correct flow rate using the Air-O-Cell ® Flow Indicator. All air sampling was conducted in accordance with IESO Volume I Standard 1210. The sampling time for the collection of each sample was determined by Table I, provided by IESO Volume I Standard 1210. The cassette was placed onto the end of the pump and the protective seal was removed from the cassette. The pump was turned on and sample collection was conducted according to Table I. After the appropriate amount of time had elapsed, the pump was turned off and the cassette was removed. The cassette was sealed, labeled, and sent to Eurofins for analysis. Table I. Recommended Sampling Times Sampling Conditions Sampling Time (min.) Calm environment with no visible particulates 10 Active environments (occupied indoors, breezy outdoors 5 Highly active environments with visible particulates 1 11 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 1 w .gosatori.com 5.0 Results & Conclusions Satori completed the survey inspection identifying and assessing ACM, LBP, and mold on March 21, 2025. During this inspection, a total of twenty (20) asbestos samples (45 layers) were collected, a total of ninety-five (95) VikenT^i XRF tests were conducted, and a total of five (5) spore trap samples were collected. The following sub -sections provide a summation of the results based on the field observations, field testing, and laboratory analytical data from Satori's inspection of the subject site. 5.1 Asbestos Findings The following table summarizes the results of all bulk samples collected by Satori's inspector during this inspection. Results are based on the findings of the laboratory analytical data. Friablel Bulk Material (Yes/ Material Appx. Asbestos Sam le# Sample Location Color/Description No) Condition Quanti Content2 Lobby — Outside of A31679-01 Meeting Room — Tan/White 2'x2' Tile N/A Good N/A ND Ceiling - 2'x2Tile A31679- Meeting Room — Near Doorway— Tan/White 2'x2' Tile N/A Good N/A ND 02 Ceilin - 2'x2' Tile Lobby — Outside of A31679- Meeting Room— 03-Joint White Joint Compound N/A Good NiA ND Soffit - Textured CompoundOff-White GWB/JC Lobby — Outside of A31679- Meeting Room — Beige Tape N/A Good NA ND 03-Tape Soffit - Textured Off -White GWB/JC Lobby — Outside of A31679- Meeting Room — 03-Gypsum Soffit - Textured Brown/Beige GWB N/A Good N/A ND Wallboard Off -White GWB/JC Women's Restroom A31679- —NW Wall - 04-Joint White Joint Compound N/A Good N/A ND Compound Textured Off -White GWB/JC Women's Restroom A31679- —NW Wall - 04-Gypsum Textured Off -White Brown/White GWB N/A Good N%A ND Wallboard GWB/JC 12 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 Phone 907.332.0456 1 Fax 907.332.0457 1 w .gosatori.com Friable' Bulk Material (Yes/ Material Appx. Asbestos Sam le# Sample Location Color/Description No) Condition Quanti Content2 A31679- Utility Room —NW <1% 05-Joint Wall - Non -Textured White Joint Compound N Damaged 240 SF hrysotile Compound White GWB/JC Utility Room —NW A31679- Wall - Non -Textured Beige Tape N/A Damaged N/A ND 05-Tape White GWB/JC A31679- Utility Room —NW 05-Gypsum Wall - Non -Textured Brown/White GWB N/A Damaged N/A ND Wallboard White GWB/JC Same A31679- Utility Room — NE material 06-Joint Wall -Non-Textured White Joint Compound N Damaged as n <1/o Compound White GWB/JC A31679- hrysotile I 05 Same A31679- Utility Room — NE material 06-Joint Wall - Non -Textured Beige Joint Compound N Damaged as <1% Compound White GWB/JC A31679- l'� sotile 2 05 A31679- Utility Room — NE 06-Gypsum Wall - Non -Textured Brown/White GWB N/A Damaged N/A ND Wallboard White GWB/JC Women's Restroom A31679- — SW Wall - <1% 07-Joint Textured Peach Beige Joint Compound N Good 30 SF hrysotile Compound GWB/JC Women's Restroom A31679- — SW Wall - Beige Tape N/A Good N/A ND 07-Tape Textured Peach GWB/JC Women's Restroom A31679- — SW Wall - 07-Gypsum Textured Peach Brown/White GWB N/A Good N/A ND Wallboard GWB/JC A31679- Auditorium — SE 08-Joint Wall — Decorative White Joint Compound N/A Good N%A ND Compound Column - Textured 1 Peach GWB/JC A31679- Auditorium — SE OS -Joint Wall — Decorative White Joint Compound N/A Good N/A ND Compound Column - Textured 2 Peach GWB/JC 13 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907332.0456 1 Fax 907.332.0457 1 vmv.gosatori.com Friable] Bulk Material (Yes/ Material Appx. Asbestos Sam le# Sample Location Color/Description No) ConditionQuanti Contentz Auditorium — SE A31679- Wall — Decorative Beige Tape N/A Good N/A ND 08-Tape Column - Textured Peach GWB/JC Auditorium — SE A31679- Wall — Decorative 08-Gypsum Brown/White GWB N/A Good N/A ND Wallboard Column -Textured Peach GWB/JC A31679- Utility Room —NW 09-Cove Wall — Cove Base - Gray Cove Base N/A Good N/A ND Base Mastics Utility Room —NW A31679- Wall — Cove Base - Yellow Mastic N/A Good N/A ND Mastic 1 Mastics Utility Room —NW A31679- Wall — Cove Base - Brown Mastic N/A Good N/A ND Mastic 2 Mastics A31679- Utility Room — SW 10-Cove Wall — Cove Base - Gray Cove Base N/A Good N/A ND Base Mastics Utility Room — SW A31679- Wall — Cove Base - White Mastic N/A Good N/A ND 10-Mastic 1 Mastics Utility Room — SW A31679- Wall — Cove Base - Brown Mastic N/A Good N/A ND 10-Mastic 2 Mastics Utility Room — SW A31679- Wall — Cove Base - Beige Backing N/A Good N/A ND 10-Backing Mastics A31679- Utility Room — NW 11-Vinyl Side —Floor - SVF Gray/Various/Beige Vinyl N Good 55 SF 15% Sheet Sheet Flooring hrysotile Flooring1 (2 Layers) Utility Room — NW A31679- Side — Floor - SVF Yellow Mastic N/A Good N/A ND 11-Mastic 1 2 Layers) Utility Room —NW A31679- Side — Floor - SVF Brown Mastic N/A Good N/A ND 11-Mastic 2 (2 Layers) A31679- Utility Room —NW 11-Vinyl Side — Floor - SVF Various/Pink/Beige Vinyl N/A Good N/A ND Sheet Sheet Flooring Floorin 2 (2 Layers) 14 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 1 www.gosatori.com Friable' Bulk Material (Yes/ Material Appx. Asbestos Sam le# Sample Location Color/Description No) ConditionQuanti Content2 A31679- Utility Room — SW 12-Vinyl Side — Floor - SVF White/Blue/Purple Vinyl N/A Good N/A ND Sheet (2 Layers) Sheet Flooring Floorin 1 Utility Room — SW A31679- 12-Mastic 1 Side — Floor - SVF Brown Mastic N/A Good N/A ND 2 Layers) Same A31679- Utility Room — SW material 12-Vinyl Side — Floor -SVF Gray/Red Vinyl Sheet N Good as 20% Sheet (2 Layers) Flooring A31679- hrysotile Flooring 2 I Utility Room — SW A31679- 12-Mastic 2 Side — Floor - SVF Yellow Mastic N/A Good N/A ND 2 Layers) A31679- Lobby — Behind 13-Vinyl Desk — Floor — Tan/White Vinyl Sheet N/A Good N/A ND Sheet Flooring Floorin grown SVF Lobby — Behind A31679- Desk — Floor — Beige Mastic N/A Good N/A ND 13-Mastic Brown SVF A31679- 14-Vinyl Lobby —N Comer— Gray/Tan Vinyl Sheet N/A Good N/A ND Sheet Floor — Brown SVF Flooring Flooring A31679- Lobby — N Corner — Beige Mastic N/A Good N/A ND 14-Mastic Floor —Brown SVF Meeting Room — W A31679-15 Comer — Floor — Yellow Mastic N/A Good N/A ND Carpet Mastic Auditorium — E Brown/Black/Yellow A31679-16 Comer — Floor - N/A Good N/A ND Carpet Mastic Mastic Utility Room — A31679-17 Furnace Ducting — White/Black DEM N/A Good N/A ND Black Dem Utility Room — A31679-18 Furnace Ducting — White/Black DEM N/A Good N/A ND Black Dem 15 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 I Phone 907.332.0456 ; Fax 907.332.0457 1 v .gosatori.com Bulk Sant le# Sample Location Material Color/Description riablei (Yes/ No) Material ConditionQuanti Appx. Asbestos Content2 Exterior — Front A31679-19 Door — Frame — Gray/Clear Caulking N/A Good N/A ND Multi -Color Caulking Exterior — Front A31679-20 Door — Frame — Brown/Black Caulking N/A Good N/A ND Multi -Color Caulking KEY. • GWB = gypsum wall board; JC = joint compound; SVF = sheet vinyl flooring; DEM = duct expansion material; ND = non -detect; N/A = not applicable 'Friability is designated as "Yes' or "No" for all ACM; non -ACM are designated "N/A" (not applicable) for friability. AAsbestos content is given as a percentage and type of asbestos found in a sample layer; all sample layers designated "ND" (non -detect) indicate that no asbestos was detected. The laboratory data pertaining to the materials sampled during this inspection show that asbestos was detected in the following building materials: Gray/Various/Red/Beige Sheet Vinyl Flooring. Satori recommends that the removal and disposal of all ACM be completed by an accredited abatement contractor, and in accordance with all applicable local, state, and federal regulations pertaining to the removal of asbestos. In addition, four sample layers, A31679-05-Joint Compound, A31679-06-Joint Compound 1, A31679-06-Joint Compound 2, and A31679-07-Joint Compound contained <1% Chrysotile asbestos. While this is not above the EPA regulatory limit, the presence of asbestos was detected. Materials that contain <1% asbestos are covered by Occupational Safety and Health Administration (OSHA) asbestos regulations which mandate specific engineering controls, work practices and prohibitions. 5.2 Lead Findings A complete listing of all surfaces (locations, components, conditions, etc.) tested for lead by XRF analyzer can be located in Appendix B of this report. Results from the XRF LBP inspection did not reveal any LBP items. If, during work activities, additional suspect LBP material is discovered that has not been tested, it should be evaluated by qualified personnel prior to disturbance. 5.3 Mold Findings Five (5) spore trap samples were collected from Kingdom Hall Kodiak during this inspection. All samples were sent to Eurofins for analysis. A detailed report of all laboratory data can be found in Appendix A. Interpretation of results is performed in accordance with IESO Volume I Standards 2110 and 2210. 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 1 w .gosatori.com Spore Trap Results Location Auditorium Lobby — Front Desk Meeting Room Utility Room Exterior — Parking Lot Sample Number ST31679-01 ST31679-02 ST31679-03 ST31679-04 ST31679-05 Basidiospores 110 Total Spores/ma <7 <7 <7 <7 110 m'-cubic meter of air Review of the laboratory results indicates that none of the indoor areas inspected contained a detectable number of mold spores at the time of sampling. A low number of Basidiospores was detected in the exterior sample, but Basidiospores were absent from all indoor samples. These spores are considered ubiquitous in nature, are commonly found in gardens, forests, and woodlands, and may release during rain or high humidity. No other spore types were detected in either the exterior or interior samples collected. Upon visual inspection, one area on the ceiling tile in the meeting room appeared to be discolored from previous water intrusion. However, the ceiling tile appeared dry during inspection and the absence of any detectable mold spores in the meeting room suggests that there was no active water intrusion associated with indoor mold growth at the time of inspection. No other conditions commonly associated with mold (e.g., musty odors, additional stained or wet materials, apparent mold growth) were observed. 17 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 www.gosatori.com 6.0 Limitations This inspection report has been prepared for the exclusive use of JW Congregation Support, Inc. Any use which a third -party makes of this report, or any reliance on or decisions to be made based on it, are the responsibility of such third -parties. Satori Group, Inc. accepts no responsibility for damages, if any, suffered by any third -party as a result of decisions made, or actions based on this report. This report is based upon and conducted in accordance with HUD Guidelines and EPA rules in effect at the time of this inspection. Satori has no duty to update this report based on subsequent regulatory changes. 7.0 Signatory This report presents the ACM, LBP, and mold inspections completed by Satori Group, Inc. The survey contains contract and introductory information, regulatory inspection framework, sampling methods, results, and recommendations. Please feel free to contact our office at 907- 332-0456 if there are any questions pertaining to the information contained in this report. Thank you for choosing Satori. Satori Group, Inc. Anna Scheiner Environmental Scientist AHERA Building Inspector # TBI4-1024-19699 EPA Lead Inspector # LBP-I-I252729-1 HAZWOPER # THS-724-19413 CRMI # 0000046289 Alan Caldwell Operations Manager AHERA Building Inspector Certification # TBI4-1024-19617 USEPA Lead -Based Paint Risk Assessor Certification # LBP-R-8196-3 CRMI # 0000039969 18 1310 East 66th Avenue, Suite 2 1 Anchorage, AK 99518 1 Phone 907.332.0456 1 Fax 907.332.0457 1 www.gosatori.com APPENDIX A Laboratory Results & Chain of Custody Records LA Testing 5431 Industrial Drive Huntington Beach, CA 92649 TESTING Tel/Fax: (714) 828-4999 / (714) 8284944 htlpJhvww.LATesting.com / hblatiQlatesting.com Attention: Alan Caldwell Satori Group, Inc 1310 East 66th Avenue Suite 2 Anchorage, AK 99518 Project: 31679 - KINGDOM HALL KODIAK HBMS LA Testing Order: 332508673 Customer ID: 32EHS30 Customer PO: 31679 Project ID: Phone: (907)332-0456 Fax: Received Date: 03/25/2025 10:00 AM Analysis Date: 03/25/2025 - 03/26/2025 Collected Date: Test Report: Asbestos Analysis of Bulk Materials via AHERA Method 40CFR 763 Subpart E Appendix E supplemented with EPA 600IR-931116 using Polarized Light Microscopy Non -Asbestos Asbestos Sample Description Appearance %Fibrous %Non -Fibrous %Type A31679-01 LOBBY -OUTSIDE Tan/White 55%Cellulose 15%Perlile None Detected OF MEETING ROOM Fibrous 20% Min. Wool 10% Non -fibrous (Other) 332508673-0 1 - CEILING -2'X2' Heterogeneous A31679-02 MEETING ROOM- Tan/While 55%Cellulose 15%Perlile None Detected NEAR DOORWAY- Fibrous 20% Min. Wool 10% Non -fibrous (Other) 332508673­0002 CEILING -2'X2'TILE Heterogeneous A31679-03-Joint LOBBY -OUTSIDE White 15%Ca Carbonate None Detected Compound OF MEETING ROOM Non -Fibrous 85% Non -fibrous (Other) -SOFFIT - Homogeneous 332W8673-0003 TEXTURED OFF-WHITE GWB/JC A31679-03-Tape LOBBY -OUTSIDE Beige 90%Cellulose 10% Non -fibrous (Other) None Detected OF MEETING ROOM Fibrous 332WB673-00M - SOFFIT - Homogeneous TEXTURED OFF-WHITE GWB/JC A31679-03-Gypsum LOBBY - OUTSIDE Brown/Beige 10%Cellulose 70%Gypsum None Detected Wallboard OF MEETING ROOM Fibrous 20% Non -fibrous (Other) -SOFFIT - Heterogeneous 332508673-00038 TEXTURED OFF-WHITE GWB/JC A31679-04-Joint WOMEN'S White 15% Ca Carbonate None Detected Compound RESTROOM-NW Non -Fibrous 85% Non -fibrous (Other) WALL -TEXTURED Homogeneous 332508673L004 OFF-WHITE GWB/JC A31679-04-Gypsum WOMEN'S Brown/White 10%Cellulose 70%Gypsum None Detected Wallboard RESTROOM - NW Fibrous 20% Non -fibrous (Other) WALL -TEXTURED Heterogeneous 332508613-0 4,% OFF-WHITE GWB/JC A31679-05-Joint UTILITY ROOM -NW White 5%Ca Carbonate <t%Chrysotile Compound WALL- Non -Fibrous 95% Non -fibrous (Other) NON -TEXTURED Homogeneous 33250667MI105 WHITE GWB/JC A31679-05-Tape UTILITY ROOM - NW Beige 90%Cellulose 10% Non -fibrous (Other) None Detected WALL- Fibrous 332506673-00 0 NON -TEXTURED Homogeneous WHITE GWB/JC A31679-05-Gypsum UTILITY ROOM -NW Brown/White 12%Cellulose 70%Gypsum None Detected Wallboard WALL- Fibrous 18%Non-fiibrous(Other) NON -TEXTURED Heterogeneous 332508673- Ci58 WHITE GWB/JC A31679-06-Joint UTILITY ROOM - NE White 15%Ca Carbonate <1%Chrysotile Compound WALL- Non -Fibrous 85%Non-fbrous(Other) NON -TEXTURED Homogeneous 332508678-0006 WHITE GWB/JC A31679-06-Joint UTILITY ROOM - NE Beige 5%Ca Carbonate <1 % Chrysotile Compound WALL- Non -Fibrous 95% Non -fibrous (Other) NON -TEXTURED Homogeneous 33250867300 WHITEGWB/JC Initial report from: 031261202512:52: 18 ASB PLM 0008 0002-2.31 Printed: 3/26/2025 9:52 AM Page 1 of LA Testing to Testing Order: 332508673 Customer ID: 32EHS30 5431 Industrial Drive Huntington Beach, CA 92649 TESTING TelrFm: (714) 828-4999 / (714) 828-4944 Customer PO: 31679 http:/Avaw.LATesbng.com / hblab@latesling.com Project ID: Test Report: Asbestos Analysis of Bulk Materials via AHERA Method 40CFR 763 Subpart E Appendix E supplemented with EPA 600IR-931116 using Polarized Light Microscopy Non -Asbestos Asbestos Sample Description Appearance % Fibrous % Non -Fibrous % Type A31679-06--Gypsum UTILITY ROOM - NE Brown/White 10% Cellulose 70%Gypsum None Detected Wallboard WALL- Fibrous 20% Non -fibrous (Other) NON -TEXTURED Heterogeneous 3325086734006e WHITE GWB/JC A31679-07-Joint WOMEN'S Beige 10% Ca Carbonate 0 % Chrysolile Compound RESTROOM-SW Non -Fibrous 90% Non -fibrous (Other) WALL -TEXTURED Homogeneous 332508673D 7 PEACH GWB/JC A31679-07-Tape WOMEN'S Beige 90%Cellulose 10%Non-fiibrous(Other) None Detected RESTROOM-SW Fibrous M2508673-007A WALL -TEXTURED Homogeneous PEACH GWB/JC A31679-07-Gypsum WOMEN'S Brown/White 12%Cellulose 70%Gypsum None Detected Wallboard RESTROOM-SW Fibrous 18% Non -fibrous (Other) WALL -TEXTURED Heterogeneous 332508673-0 76 PEACH GWB/JC A31679-08-Joint AUDITORIUM - SE White 15%Ca Carbonate None Detected Compound WALL- Non -Fibrous 85% Non -fibrous (Other) DECORATIVE Homogeneous 332506673-W0e COLUMN - TEXTURED PEACH GWB/JC A31679-08-Joint AUDITORIUM - SE White 5%Ca Carbonate None Detected Compound WALL- Non -Fibrous 95% Non -fibrous (Other) DECORATIVE Homogeneous 332508673-0 M COLUMN - TEXTURED PEACH GWB/JC A31679-08-Tape AUDITORIUM - SE Beige 90%Cellulose 10% NonAbrous(Other) None Detected WALL- Fibrous 332508673-0008e DECORATIVE Homogeneous COLUMN - TEXTURED PEACH GWB/JC A31679-08-Gypsum AUDITORIUM - SE Brown/White 10% Cellulose 70%Gypsum None Detected Wallboard WALL- Fibrous 20% Non -fibrous (Other) DECORATIVE Heterogeneous 3325086730008C COLUMN - TEXTURED PEACH GWB/JC A31679-09-Cove Base UTILITY ROOM - NW Gray 100% Non -fibrous (Other) None Detected WALL - COVE BASE Non -Fibrous 332506673-0 9 - MASTICS Homogeneous A31679-09-Mastic 1 UTILITY ROOM - NW Yellow 100% Nan -fibrous (Other) None Detected WALL - COVE BASE Non -Fibrous 332508673.a009A -MASTICS Homogeneous A31679-09-Mastic 2 UTILITY ROOM - NW Brown 100% Non -fibrous (Other) None Detected WALL - COVE BASE Non -Fibrous 332506673-0 9e -MASTICS Homogeneous A31679-10-Cove Base UTILITY ROOM - SW Gray 100% Non -fibrous (Other) None Detected WALL - COVE BASE Non -Fibrous 332NO6734010 -MASTICS Homogeneous A31679-10-Mastic1 UTILITY ROOM -SW White 100% Non -fibrous (Other) None Detected WALL - COVE BASE Non -Fibrous 332508673-0010A -MASTICS Homogeneous A31679-10-Mastic2 UTILITY ROOM -SW Brown 100%Non-fiibrous(Other) None Detected WALL -COVE BASE Non -Fibrous 33150867"0106 -MASTICS Homogeneous Initial report from: 03/26/2025 12:52:18 ASB_PLM_0008_0002 - 2.31 Printed: 3/26/2025 9:52 AM Page 2 of 4 LA Testing LA Testing Order: 332508673 Customer ID: 32EHS30 pjA5431 Industrial Drive Huntington Beach, CA 92649 TeWaoi: (714) 828-4999 / (714) 828-4944 Customer PO: 31679 TESTING h8p:/hnvw.LATesting.com / hblab@la[esting.wm Project ID: Test Report: Asbestos Analysis of Bulk Materials via AHERA Method 40CFR 763 Subpart E Appendix E supplemented with EPA 600IR-931116 using Polarized Light Microscopy Non -Asbestos Asbestos Sample Description Appearance %Fibrous %Non -Fibrous %Type A31679-10-Backing UTILITY ROOM -SW Beige 90%Cellulose 10% Non -fibrous (Other) None Detected WALL - COVE BASE Fibrous 332506673-e01ec - MASTICS Homogeneous A31679-11-Vinyl Sheet UTILITY ROOM - NW GrayNarious/Beige 6% Cellulose 79% Non -fibrous (Other) 15% Chrysotile Flooring 1 SIDE - FLOOR -SVF Fibrous (2 LAYERS) Heterogeneous M2506673-0011 A31679-11-Mastic 1 UTILITY ROOM - NW Yellow 100% Non -fibrous (Other) None Detected SIDE - FLOOR -SVF Non -Fibrous 332508673n 11A (2 LAYERS) Homogeneous A31679-11-Mastic 2 UTILITY ROOM - NW Brown 100% Non -fibrous (Other) None Detected SIDE - FLOOR -SVF Non -Fibrous 332506673-0011B (2 LAYERS) Homogeneous A31679-11-Vinyl Sheet UTILITY ROOM - NW Various/Pink/Beige 100% Non -fibrous (Other) None Detected Flooring SIDE - FLOOR -SVF Non -Fibrous (2 LAYERS) Heterogeneous 332508673-0011C A31679-12-Vinyl Sheet UTILITY ROOM - SW White/Blue/Purple 100% Non -fibrous (Other) None Detected Flooring SIDE - FLOOR -SVF Non -Fibrous (2 LAYERS) Heterogeneous 332508673Z012 A31679-12-Mastic1 UTILITY ROOM -SW Brown 100% Non -fibrous (Other) None Detected SIDE - FLOOR -SVF Non -Fibrous 332506673-001M (2 LAYERS) Homogeneous A31679-12-Vinyl Sheet UTILITY ROOM -SW Gray/Red 10%Cellulose 70%Non-fiibrous(Other) 20%Chrysotile Flooring SIDE - FLOOR -SVF Fibrous (2 LAYERS) Heterogeneous 332508673-00126 A31679-12-Mastic 2 UTILITY ROOM - SW Yellow 100% Non -fibrous (Other) None Detected SIDE - FLOOR -SVF Non -Fibrous 33250e673-0012c (2 LAYERS) Homogeneous A31679-13-Vinyl Sheet LOBBY -BEHIND Tan/White 100% Non -fibrous (Other) None Detected Flooring DESK -FLOOR- Non -Fibrous BROWN SVF Heterogeneous 332506673-0013 A31679-13-Mastic LOBBY -BEHIND Beige 100% Non -fibrous (Other) None Detected DESK -FLOOR- Non -Fibrous 332506673-0013A BROWN SVF Homogeneous A31679-14-Vinyl Sheet LOBBY -N CORNER Gray/Tan 100% Non -fibrous (Other) None Detected Flooring - FLOOR - BROWN Non -Fibrous SVF Heterogeneous 332508673-0014 A31679-14-Mastic LOBBY -N CORNER Beige 100% Non -fibrous (Other) None Detected - FLOOR - BROWN Non -Fibrous 332508673-0014A SVF Homooeneous A31679-15 MEETING ROOM - W Yellow 100% Non -fibrous (Other) None Detected CORNER -FLOOR- Non -Fibrous 332508673-0015 CARPET MASTIC Homogeneous A31679-16 AUDITORIUM - E Brown/Black/Yellow 5%Cellulose 95% Non -fibrous (Other) None Detected CORNER -FLOOR- Fibrous 332508673-0016 CARPET MASTIC Heterogeneous Result Includes a small amount ofinseparable attached mateda/ A31679-17 UTILITY ROOM- White/Black 25%Glass 75% Non -fibrous (Other) None Detected FURNACE DUCTING Fibrous 332506673-0017 - BLACK DEM Homogeneous A31679-18 UTILITY ROOM- White/Black 30%Glass 70% Non -fibrous (Other) None Detected FURNACE DUCTING Fibrous 332608673-0018 - BLACK DEM Homooeneous Initial report from: 03/26/2025 12:52:18 I ASB_PLM_0008_0002 - 2.31 Printed: 3/26/2025 9:52 AM Page 3 of 4 LA Testing LATestingOrder: 332508673 5431 Industrial Drive Huntington Beach, CA 92649 Customer ID: 32EHS30 �TESTIt9O TeUFax: (714) 828-4999 / (714) 828-0944 Customer PO: 31679 http://www.LATesting.com / hblab@latesting.com Project ID: Test Report: Asbestos Analysis of Bulk Materials via AHERA Method 40CFR 763 Subpart E Appendix E supplemented with EPA 600IR-931116 using Polarized Light Microscopy Non -Asbestos Asbestos Sample Description Appearance % Fibrous % Non -Fibrous % Type A31679-19 EXTERIOR - FRONT Gray/Clear 100 % Non -fibrous (Other) None Detected DOOR -FRAME- Non -fibrous 332508673-0019 MULTI -COLOR Homogeneous CAULKING A31679-20 EXTERIOR - FRONT Brown/Black 100 % Non -fibrous (Other) None Detected DOOR -FRAME- Non -Fibrous 332508873-0020 MULTI -COLOR Heterogeneous CAULKING Analyst(s) Kayfin Luciani (17) Pamela Cardoso (22) Ryan Nguyen (6) Michael Chapman, Laboratory Manager or Other Approved Signatory LA Testing maintains liability limited to cost of analysis. Interpretation and use of lest results are the responsibility of the dienl. This report relates only to the samples reported above, and may not be reproduced, except in full, without written approval by IA Testing IA Testing bears no responsibility for sample collection activities or all method limitations. The report reflects the samples as received Results are generated from the field sampling data (sampling volumes and areas, locations, etc.) provided by the client on the Chain of Custody. Samples are within quality control criteria and met method specifications unless otherwise noted. The above analyses were performed in general compliance with Appendix E to Subpart E of 40 CFR (previously EPA 600M14-82-020 -Interim Method') but augmented with procedures outlined in the 1993 ('finar) version of the method. This report must not be used by the client to claim product cartifcalion, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non -friable organically bound materials present a problem maldx and therefore LA Testing recommends gravimetric reduction prior to analysis. Unless requested by the client, building materials manufactured with multiple layers (is Linoleum, wallboard, etc.) are reported as a single sample. Estimation of uncertainty is available on request. Samples analyzed by LA Testing Huntington Beach, CA NVLAP Lab Coda 101384-0, CA ELAP 1406 Initial report from: 03/26/2025 12:52:18 ASB_PLM_0008_0002 - 2.31 Printed: 3/26/2025 9:52 AM Page 4 of 4 OrderID: 332508673 i `r SATORI GROUP z )ELF roe� ryr �E� Customer ID: ° Company Name: p° Street Address: City/State/Zip ° Phone c — Email(s) for Report: Email(s) for Invoice: 1310 E. 661h Ave. #2 Asbestos Chain of Custody Anchorage, AK 99518 Phone:907-332-0456 # 3 3 2 5 0 8 6 7 3 Email: 32EH530 Ik1014 AK acaldwell6a)Ro5atori.com: ascheiner@eosatori.com: esherrer@eosatori.com ilucas@¢osatori.com: cborstad(nlaosatori.com Project Information Project Name/No. Kingdom Hall Kodiak HBMS Satori Project No.: 31679 Sampled By (Name): Anna Scheiner No. of Samples In Shipment: 20 Sampled By (Signature ): ::: Q, P - Turn -Around Time (TAT) ❑ 3 Hours ❑ 4-4.5 Hours ❑ 6 Hours ❑ 32 ❑ 48 Hours ❑ 72 Hours ❑ 96 Hours AHERA ONLY Hours Test Selection PCM Air TEM - Air TEM — Settled Dust ❑ NIOSH 7400 ❑ AHERA 40 CFR, Part 763 ❑ Microvac —ASTM D5755 ❑ NIOSH 7400 w/8hr, TWA ❑ NIOSH 7402 ❑ Wipe —ASTM D6480 ❑ EPA Level II ❑ Qualitative via Filtration Prep PLM — Bulk (reoortina limitl ❑ Qualitative via Drop Mount Prep 111109P L M EPA 600/ft=93/ 'i8'ib) ❑ ELM EPA NOB (<1%) TEM - Bulk Soil -Rock -Vermiculite (reoortina limit*) ❑ POINT COUNT ❑ TEM EPA NOB ❑ PLM EPA 600/R-93/116 w/Milling Prep (<0.25%) ❑ 400 (<0.25%) ❑ 1,000 (<0.1%) ❑ NYS NOB 198.4 (Non-Friabie-NY) ❑ PLM EPA 600/R-93/116 w/Milling Prep (<0.1%) POINT COUNT w/GRAVIMETRIC ❑ TEM EPA 600/R-93/116 w/Milling Prep ❑ TEM EPA 600/R-93/116 w/Milling Prep (<0.1%) ❑ 400 (<0.25%) ❑ 1,000 (<0.1%) (0.1%) ❑ TEM Qualitative via Filtration Prep ❑ NIOSH 9002 (<3%) ❑ TEM Qualitative via Drop Mount Prep ❑ NYS 198.8 (Vermiculite SM-V) ❑ Positive Stop - Clearly Identified Homogenous Areas (HA) Filter Pore Size (Air Samples): ❑ 0.8um ❑ 0.45um Date/Time Sampled Sample Number Sample Location/Description Volume, Area, or HA (Air Monitoring Only) Lobby — Outside of Meeting Room — A31679-01 Ceiling — 2'x2' Tile A31679-02 Meeting Room — Near Doorway — Ceiling —2'x2'Tile Lobby — Outside of Meeting Room — A31679-03 Soffit —Textured Off -White GWB/JC Women's Restroom—NW Wall — A31679-04 Textured Off -White GWB/1C Utility Room —NW Wall — Non -textured A31679-05 White GWB/1C Utility Room —NE Wall — Non -texture A31679-06 White GWB/JC Women's Restroom—SWWaIi— A31679-07 Textured Peach GWB/JC Auditorium — SE Wall — Decorative A31679-08 Column —Textured Peach GWB/JC Instructions Method of Shipment: FedEx Pak Sample Condition Upon Receipt: Relinquished By: Anna Schemer Date/Time 3/24/25 Received By: r ' iJt ate/Time 3.25 'l5 ,bijAt Relinquished By: v Date/Time 12 pm Received By: Date/Time Paqe 1 Of 2 OrderID: 332 #3 3250 86 73 Asbestos Chain of Custody Sample Number Sample Location/Description Volume, Area, or HA Date/Time Sampled (Air Monitoring Only) A31679-09 Utility Room —NW Wall —Cove Base — Mastics A31679-10 Utility Room —SW Wall —Cove Base — Mastics A31679-11 Utility Room —NW Side — Floor —SVF (2 Layers) A31679-12 Utility Room —SW Side — Floor —SVF (2 Layers) A31679-13 Lobby —Behind Desk — Floor — Brown SVF A31679-14 Lobby —N Corner — Floor — Brown SVF A31679-15 Meeting Room —W Corner — Floor — Carpet Mastic A31679-16 Auditorium —E Corner — Floor — Carpet Mastic A31679-17 Utility Room —Furnace Ducting — Black DEM A31679-18 Utility Room —Furnace Ducting — Black DEM A31679-19 Exterior — Front Door — Frame — Multi -Color Caulking A31679-20 Exterior — Front Door — Frame — Multi -Color Caulking Method of Shipment: FedEx Pak Relinquished By: Anna Scheiner Date/Time 3/24/25 Received By: Relinquished By: Date/Time 12 pm Received By: - Sample Condition Upon Receipt: _ Date/Time Date/Time Paqe 2 Of tiff eurofins Built Environment Testing Report for: Mr. Alan Caldwell Sailor! Group Inc. 1310 E. 66th Avenue, Suite #2 Anchorage, AK 99518 Eurofins Built Environment Testing West, LLC Regarding: Project: 31679; Kingdom Hall Kodiak EML ID: 4000211 Approved by: Technical Manager Carlos Rivadeneyra Service SOPs: Spore trap analysis (EB-MY-S-1038) AIHA LAP, LLC accredited service, Lab ID #160266 Dates of Analysis: Spore trap analysis: 03-27-2025 All samples were received in acceptable condition unless noted in the Report Comments portion in the body of the report. Due to the nature of the analyses performed, field blank correction of results is not applied. The results relate only to the samples as received and tested. Information supplied by the client which can affect the validity of results: sample air volume. Eurofins Built Environment Testing West, LLC ("the Company"), a member of the Eurofins Built Environment Testing group of companies, shall have no liability to the client or the client's customer with respect to decisions or recommendations made, actions taken or courses of conduct implemented by either the client or the client's customer as a result of or based upon the Test Results. In no event shall the Company be liable to the client with respect to the Test Results except for the Company's own willful misconduct or gross negligence nor shall the Company be liable for incidental or consequential damages or lost profits or revenues to the fullest extent such liability may be disclaimed by law, even if the Company has been advised of the possibility of such damages, lost profits or lost revenues. In no event shall the Company's liability with respect to the Test Results exceed the amount paid to the Company by the client therefor. Eurofins Built Environment Testing West, LLC's LabServe® reporting system includes automated fail -safes to ensure that all AIHA LAP, LLC quality requirements are met and notifications are added to reports when any quality steps remain pending. Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 1 of 3 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.comBuilt Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 SPORE TRAP REPORT: NON -VIABLE METHODOLOGY Location: ST31679-01: Auditorium ST31679-02: Lobby - Front Desk ST31679-03: Meeting Room ST31679-04: Utility Room ST31679-05: Exterior - Parking Lot Comments (see below) None None None None None LabID-Version$: 19904840-1 19904841-1 19904842-1 19904843-1 19904844-1 Analysis Date: 03/27/2025 03/27/2025 03/27/2025 03/27/2025 03/27/2025 raw ct. spores/m3 raw ct. spores/m3 raw Ct. spores/m3 ravv CL spores/m3 raw ct. spores/m3 Ascos ores Basidios ores 1 2 110 Bi olaris/Drechslera group Botrvtis Chaetomium Clados orium Curvularia E icoccum Fusarium M rothecium Ni ros ora Other colorless P nicillium/As er illus tnest Pithom ces Rusts Smuts Periconia Myxomycetes Stachybotrys St nth lium Torula Ulocladium Zygmycetes Back ound debris 1-4+ 3+ 3+ 3+ 3+ < 1+ Hyphal fra ments/m3 < 7 < 7 < 7 < 7 < 13 Pollen/m3 < 7 < 7 < 7 < 7 < 13 Skin cells 1-4+ < I+ < 1+ 1+ < 1+ None Sam le volume liters 150 150 150 150 75 16 TOTAL RE m3 < 7 < 7 1 <7 1 1 Comments: Spore types listed without a count or data entry were not detected during the course of the analysis for the respective sample, indicating a raw count of <1 spore. t The spores of Aspergillus and Penicillium (and others such as Acremonium, Paecilomyces) are small and round with very few distinguishing characteristics. They cannot be differentiated by non -viable sampling methods. Also, some species with very small spores are easily missed, and may be undercounted. ttBackground debris indicates the amount of non -biological particulate matter present on the trace (dust in the air) and the resulting visibility for the analyst. It is rated from 1+ (low) to 4+ (high). Counts from areas with 4+ background debris should be regarded as minimal counts and may be higher than reported. It is important to account for samples volumes when evaluating dust levels. The analytical sensitivity is the spores/mA3 divided by the raw count, expressed in spores/mA3, per spore and per sample. For more information regarding analytical sensitivity, please contact QA by calling the laboratory. t A "Version" indicated by -"x" after the Lab ID# with a value greater than I indicates a sample with amended data. The revision number is reflected by the value of "x". § Total Spores/m3 has been rounded to two significant figures to reflect analytical precision. Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 2 of 3 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.comBuilt Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 SPORE TRAP REPORT: NON -VIABLE METHODOLOGY PROJECT ANALYST AND SIGNATORY REPORT Project Analyst Analyst: Sara Pezzini The test report shall not be reproduced except in full, without written approval of the laboratory. The report must not be used by the client to claim product certification, approval, or endorsement by AIHA LAP, LLC, or any agency of the federal government. The Company reserves the right to dispose of all samples after a period of thirty (30) days, according to all state and federal guidelines, unless otherwise specified. $ A "Version" indicated by JY' after the Lab ID# with a value greater than I indicates a sample with amended data. The revision number is reflected by the value of "x". Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 3 of 3 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.comBuilt Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 MoldRANGETM: Extended Outdoor Comparison Outdoor Location: ST31679-05, Exterior - Parking Lot Fungi Identified Outdoor Typical Outdoor Data by Datet Typical Outdoor Data by Location$ data Month: March State: AK spores/m3 low med high freq % low med high fireal % Generally able to grow indoors* Alternaria - 7 27 210 26 7 53 1,100 4 Bipolaris/Drechslera group - 7 13 160 8 - - - I Chaetomium - 7 13 180 7 13 13 130 4 Cladosporium - 27 230 4,800 80 22 160 9,500 66 Curvularia - 7 13 230 7 - - - < 1 Nigrospora - 7 13 110 8 - - - < 1 Penicillium/Aspergillus types - 13 150 1,700 53 22 210 2,400 71 Stachybotrys - 7 13 770 2 - - - 2 Torula - 7 13 210 5 - - - 1 Seldom found growing indoors** Ascospores - 13 150 2,900 69 17 590 15,000 74 Basidiospores 110 13 270 7,700 86 22 530 28,000 81 Rusts - 7 13 310 10 7 53 300 10 Smuts, Periconia, Myxomycetes - 7 27 370 45 7 53 270 27 § TOTAL SPORES/m3 110 t The Typical Outdoor Data by Date represents the typical outdoor spore levels across North America for the month indicated. The last column represents the frequency of occurrence. The low, medium, and high values represent the 2.5, 50, and 97.5 percentile values of the spore type when it is detected. For example, if the frequency of occurrence is 63% and the low value is 53, it would mean that the given spore type is detected 63% of the time and, when detected, 2.5% of the time it is present in levels above the detection limit and below 53 spores/m3. These values are updated periodically, and if enough data is not available to make a statistically meaningful assessment, it is indicated with a dash. t The Typical Outdoor Data by Location represents the typical outdoor spore levels for the region indicated for the entire year. As with the Typical Outdoor Data by Date, the four columns represent the frequency of occurrence and the typical low, medium, and high concentration values for the spore type indicated. These values are updated periodically, and if enough data is not available to make a statistically meaningful assessment, it is indicated with a dash. § Total Spores/m3 has been rounded to two significant figures to reflect analytical precision. * The spores in this category are generally capable of growing on wet building materials in addition to growing outdoors. Building related growth is dependent upon the fungal type, moisture level, type of material, and other factors. Cladosporium is one of the predominant spore types worldwide and is frequently present in high numbers. Penicillium/Aspergillus species colonize both outdoor and indoor wet surfaces rapidly and are very easily dispersed. Other genera are usually present in lesser numbers. ** These fungi are generally not found growing on wet building materials. For example, the rusts and smuts are obligate plant pathogens. However, in each group there are notable exceptions. For example, agents of wood decay are members of the basidiomycetes and high counts of a single morphological type of basidiospore on an inside sample should be considered significant. Interpretation of the data contained in this report is left to the client or the persons who conducted the field work. This report is provided for informational and comparative purposes only and should not be relied upon for any other purpose. "Typical outdoor data" are based on the results of the analysis of samples delivered to and analyzed by Eurofins Built Environment Testing and assumptions regarding the origins of those samples. Sampling techniques, contaminants infecting samples, unrepresentative samples and other similar or dissimilar factors may affect these results. In addition, Eurofins Built Environment Testing may not have received and tested a representative number of samples for every region or time period. Eurofins Built Environment Testing hereby disclaims any liability for any and all direct, indirect, punitive, incidental, special or consequential damages arising out of the use or interpretation of the data contained in, or any actions taken or omitted in reliance upon, this report. Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page I of 2 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak MoldRANGE7m: Extended Outdoor Comparison PROJECT ANALYST AND SIGNATORY REPORT Project Analyst Analyst: Sara Pezzini Eurofms Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.com/Built Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 The test report shall not be reproduced except in full, without written approval of the laboratory. The report must not be used by the client to claim product certification, approval, or endorsement by any agency of the federal government. The Company reserves the right to dispose of all samples after a period of thirty (30) days, according to all state and federal guidelines, unless otherwise specified. I A "Version" indicated by -"x" after the Lab ID# with a value greater than 1 indicates a sample with amended data. The revision number is reflected by the value of "x". Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 2 of 2 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.com/Built Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 MoldSTATrm: Supplementary Statistical Spore Trap Report Outdoor Summary: ST31679-05: Exterior - Parking Lot Species detected Outdoor sample spores/m3 <I00 1K I0K >100K Typical outdoor ranges Orth America) Freq. o Ascospore Basidiospore Cladosporiu Penicillium/Aspergillus type Smuts, Periconia, Myxomycete Total < 13 13 - 210 - 5,200 13 - 370 - 22,000 27 - 450 - 7,900 20 - 200 - 2,600 7 - 53 - 720 73 88 87 59 62 I10 < 13 < 13 < 13 The "Typical outdoor ranges" and "Freq. %" columns show the typical low, medium, and high spore counts per cubic meter and the frequency of occurrence for the given spore type. The low, medium, and high values represent the 2.5, 50, and 97.5 percentile values when the spore type is detected. For example, if the low value is 53 and the frequency of occurence is 63%, it would mean that we typically detect the given spore type on 63 percent of all outdoor samples and, when detected, 2.5% of the time it is present in levels below 53 spores/m3. Indoor Samples Location: ST31679-01: Auditorium % of outdoor total Friedman chi- Agreement ratio** Spearman rank MoldSCORE**** spores/m3 square* (indoor/outdoor) correlation*** (indoor/outdoor) (indoor variation) (indoor/outdoor) Result: < I% dF: N/A Result: 0.0000 dF: N/A Score: 100 Result: N/A Result: N/A Result: Low Critical value: N/A Critical value: N/A Inside Similar: N/A Outside Similar: N/A Species Detected Spores/m3 <100 IK (OK >IOOK None Detecte < 7 Location: ST31679-02: Lobby - Front Desk % of outdoor total Friedman chi- Agreement ratio** Spearman rank MoldSCORE**** spores/m3 square* (indoor/outdoor) correlation*** (indoor/outdoor) (indoor variation) (indoor/outdoor) Result: < 1% dF: N/A Result: 0.0000 dF: N/A Score: 100 Result: N/A Result: N/A Result: Low Critical value: N/A Critical value: N/A Inside Similar: N/A Outside Similar: N/A Species Detected Spores/m3 400 IK IOK >IOOK None Detecte < 7 Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 1 of 4 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.comBuilt Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 MoldSTATTm: Supplementary Statistical Spore Trap Report Location: ST31679-03: Meetina Room % of outdoor total Friedman chi- Agreement ratio** Spearman rank MoldSCORE**** spores/m3 square* (indoor/outdoor) correlation*** (indoor/outdoor) (indoor variation) (indoor/outdoor) Result: < 1% dF: N/A Result: 0.0000 dF: N/A Score: 100 Result: N/A Result: N/A Result: Low Critical value: N/A Critical value: N/A Inside Similar: N/A Outside Similar: N/A Species Detected Spores/m3 <I00 I 10K >100K None Detecte < 7 Location: ST31679-04: Utility Room % of outdoor total Friedman chi- Agreement ratio** Spearman rank MoldSCORE**** spores/m3 square* (indoor/outdoor) correlation*** (indoor/outdoor) (indoor variation) (indoor/outdoor) Result: < 1% dF: N/A Result: 0.0000 dF: N/A Score: 100 Result: N/A Result: N/A Result: Low Critical value: N/A Critical value: N/A Inside Similar: N/A Outside Similar: N/A Species Detected Spores/m3 <100 1K IOK >100K None Detecte < 7 * The Friedman chi-square statistic is a non -parametric test that examines variation in a set of data (in this case, all indoor spore counts). The null hypothesis (110) being tested is that there is no meaningful difference in the data for all indoor locations. The alternative hypothesis (used if the test disproves the null hypothesis) is that there is a difference between the indoor locations. The null hypothesis is rejected when the result of the test is greater than the critical value. The critical value that is displayed is based on the degrees of freedom (dF) of the test and a significance level of 0.05. ** An agreement ratio is a simple method for assessing the similarity of two samples (in this case the indoor sample and the outdoor summary) based on the spore types present. A score of one indicates that the types detected in one location are the same as that in the other. A score of zero indicates that none of the types detected indoors are present outdoors. Typically, an agreement of 0.8 or higher is considered high. *** The Spearman rank correlation is a non -parametric test that examines correlation between two sets of data (in this case the indoor location and the outdoor summary). The null hypothesis (HO) being tested is that the indoor and outdoor samples are unrelated. The alternative hypothesis (used if the test disproves the null hypothesis) is that the samples are similar. The null hypothesis is rejected when the result of the test is greater than the critical value. The critical value that is displayed is based on the degrees of freedom (dF) of the test and a significance level of 0.05. Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 2 of 4 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.com/Built Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 MoldSTATTm: Supplementary Statistical Spore Trap Report **** MoldSCORETM is a specialized method for examining air sampling data. It is a score between 100 and 300, with 100 indicating a greater likelihood that the airborne indoor spores originated from the outside, and 300 indicating a greater likelihood that they originated from an inside source. The Result displayed is based on the numeric score given and will be either Low, Medium, or High, indicating a low, medium, or high likelihood that the spores detected originated from an indoor source. Eurofins Built Environment Testingreserves the right to, and may at anytime, modify or change the MoldScore algorithm without notice. Interpretation of the data contained in this report is left to the client or the persons who conducted the field work. This report is provided for informational and comparative purposes only and should not be relied upon for any other purpose. "Typical outdoor ranges" are based on the results of the analysis of samples delivered to and analyzed by Eurofins Built Environment Testing Testing and assumptions regarding the origins of those samples. Sampling techniques, contaminants infecting samples, unrepresentative samples and other similar or dissimilar factors may affect these results. With the statistical analysis provided, as with all statistical comparisons and analyses, false -positive and false -negative results can and do occur. Eurofins Built Environment Testing hereby disclaims any liability for any and all direct, indirect, punitive, incidental, special or consequential damages arising out of the data contained in, or any actions taken or omitted in reliance upon, this report. Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 3 of 4 Client: Satori Group Inc. CIO: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofmsus.com/Built Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 MoldSTATTM: Supplementary Statistical Spore Trap Report PROJECT ANALYST AND SIGNATORY REPORT Project Analyst Analyst: Sara Pezzini The test report shall not be reproduced except in full, without written approval of the laboratory. The report must not be used by the client to claim product certification, approval, or endorsement by any agency of the federal government. The Company reserves the right to dispose of all samples after a period of thirty (30) days, according to all state and federal guidelines, unless otherwise specified. I A "Version' indicated by -"x" after the Lab ID# with a value greater than I indicates a sample with amended data. The revision number is reflected by the value of "x". Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 4 of 4 Client: Satori Group Inc. C/Cl: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.comBuilt Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 MoldSCORETm: Spore Trap Report Outdoor Sample: ST31679-05 Exterior - Parking Lot Fungi Identified Outdoor sample spores/m3 <I00 IK WK >100N Raw count Spores/ m3 General!y able to grow indoors* Altemana ND < 13 Bi olaris/Drechstera group ND < 13 Chaetomium ND < 13 Clados orium ND < 13 Curvularia ND < 13 Ni ros ora ND < 13 Penicillium/As er illus typestypest ND < 13 Stachybotrys ND < 13 Torula ND < 13 Seldom found growing indoors** Ascos ores ND < 13 Basidios ores 2 110 Rusts ND < 13 Smuts Periconia M xom cetes ND < 13 Total 107 Location: ST31679-01 Auditorium Fungi Identified Indoor sample spores/m3 <loo IK 10K 1100N Raw count Spores/ m3 General!y able to grow indoors* Altemaria ND < 7 Bi olaris/Drechslera group ND < 7 Chaetomium ND < 7 Clados orium ND < 7 Curvularia ND < 7 Ni os ora ND < 7 Penicillium/As er illus t es ND < 7 Stach bo s ND < 7 Torula ND < 7 Seldom found growingindoors** Ascos ores ND < 7 Basidios ores ND < 7 Rusts ND < 7 Smuts Periconia M xom cetes ND < 7 Total N/A tl tl tt Eurnfins Built Environment Testing West, LLC EMLab ID: 4000211, Page I of 4 Eurnfins Built Environment Testing West, LLC EMLab ID: 4000211, Page I of 4 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak MoldSCORETM: Spore Trap Report Location: ST31679-02 Lobby -Front Desk Eurofins Built Environment Testing West, LLC 9445 Famham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.curofinsus.com/Built Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 Fungi Identified Indoor sample spores/m3 q00 1K 10K >100K Raw count Spores/ m3 Generally able to grow indoors* Altemaria ND < 7 Bi olaris/Drechslera group ND <7 Chaetomium ND < 7 Clados orium ND < 7 Curvularia ND < 7 Nigrospora I ND < 7 Penicillium/As er illus typest ND <7 Stachybotrys ND < 7 Tomla ND < 7 Seldom found rowing indoors** Ascos ores ND < 7 Basidios ores ND <7 Rusts ND < 7 Smuts Periconia M xom cetes ND < 7 Total N/A Location: ST31679-03 Meetin¢ Room Fungi Identified Indoor sample spores/m3 400 IK 10K >100K Raw count Spores/ m3 Generally able to grow indoors* Altemaria ND < 7 Bi olaris/Drechslera group ND < 7 Chaetomium ND < 7 Clados orium ND < 7 Curvularia ND < 7 Ni ros ora ND < 7 Penicillium/As er illus typesf ND < 7 Stachybotrys ND < 7 Tonda ND < 7 Seldom found growing indoors** Ascos ores ND < 7 Basidios ores ND < 7 Rusts ND < 7 Smuts Periconia M xom cetes ND <7 Total N/A MoldSCOREt 100 200 300 Seem 11 1' Eurolins Built Environment Testing West, LLC EMLab ID: 4000211, Page 2 of 4 11 1' Eurolins Built Environment Testing West, LLC EMLab ID: 4000211, Page 2 of 4 Eurolins Built Environment Testing West, LLC EMLab ID: 4000211, Page 2 of 4 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak MoldSCORETm: Spore Trap Report Location: ST31679-04 UtilityRoom Eurofms Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.com/Built Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 Fungi Identsed Indoor sample spores/m3 <100 IK tOK >100 Raw Count Spores/ m3 Generally able to grow indoors* Altemaria NO < 7 Bi olaris/Drechslera group NO < 7 Chaetomium NO < 7 Clados orium NO < 7 Curvularia NO < 7 Nigrospora NO < 7 Penicillium/As er illus typest NO < 7 Stachybotrys NO < 7 Tomla NO < 7 Seldom found growing indoors** Ascos ores ND < 7 Basidios ores NO < 7 Rusts ND < 7 Smuts Periconia M xom cetes ND < 7 Total N/A tl 1' 11 200 300 Score * The spores in this category are generally capable of growing on wet building materials in addition to growing outdoors. Building related growth is dependent upon the fungal type, moisture level, type of material, and other factors. Cladosporium is one of the predominant spore types worldwide and is frequently present in high numbers. Penicillium/Aspergillus species colonize both outdoor and indoor wet surfaces rapidly and are very easily dispersed. Other genera are usually present in lesser numbers. ** These fungi are generally not found growing on wet building materials. For example, the rusts and smuts are obligate plant pathogens. However, in each group there are notable exceptions. For example, agents of wood decay are members of the basidiomycetes and high counts of a single morphological type of basidiospore on an inside sample should be considered significant. }The spores of Aspergillus and Penicillium (and others such as Acremonium, Paecilomyces) are small and round with very few distinguishing characteristics. They cannot be differentiated by non -viable sampling methods. $Rated on a scale from 100 to 300. A rating less than 150 is low and indicates a low probability of spores originating inside. A rating greater than 250 is high and indicates a high probability that the spores originated from inside, presumably from indoor mold growth. A rating between 150 and 250 indicates a moderate likelihood of indoor fungal growth. MoldSCORE is NOT intended for wall cavity samples. It is intended for ambient air samples in residences. Using the analysis on other samples (like wall cavity samples) will lead to misleading results. Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 3 of 4 * The spores in this category are generally capable of growing on wet building materials in addition to growing outdoors. Building related growth is dependent upon the fungal type, moisture level, type of material, and other factors. Cladosporium is one of the predominant spore types worldwide and is frequently present in high numbers. Penicillium/Aspergillus species colonize both outdoor and indoor wet surfaces rapidly and are very easily dispersed. Other genera are usually present in lesser numbers. ** These fungi are generally not found growing on wet building materials. For example, the rusts and smuts are obligate plant pathogens. However, in each group there are notable exceptions. For example, agents of wood decay are members of the basidiomycetes and high counts of a single morphological type of basidiospore on an inside sample should be considered significant. }The spores of Aspergillus and Penicillium (and others such as Acremonium, Paecilomyces) are small and round with very few distinguishing characteristics. They cannot be differentiated by non -viable sampling methods. $Rated on a scale from 100 to 300. A rating less than 150 is low and indicates a low probability of spores originating inside. A rating greater than 250 is high and indicates a high probability that the spores originated from inside, presumably from indoor mold growth. A rating between 150 and 250 indicates a moderate likelihood of indoor fungal growth. MoldSCORE is NOT intended for wall cavity samples. It is intended for ambient air samples in residences. Using the analysis on other samples (like wall cavity samples) will lead to misleading results. Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 3 of 4 Client: Satori Group Inc. C/O: Mr. Alan Caldwell Re: 31679; Kingdom Hall Kodiak Mo1dSCORETm: Spore Trap Report PROJECT ANALYST AND SIGNATORY REPORT Project Analyst Analyst: Sara Pezzini Eurofins Built Environment Testing West, LLC 9445 Farnham Street, Suite 103, San Diego, CA 92123 (833) 465-5857 www.eurofinsus.com/Built Date of Sampling: 03-21-2025 Date of Receipt: 03-25-2025 Date of Report: 03-27-2025 The test report shall not be reproduced except in full, without written approval of the laboratory. The report must not be used by the client to claim product certification, approval, or endorsement by any agency of the federal government. The Company reserves the right to dispose of all samples after a period of thirty (30) days, according to all state and federal guidelines, unless otherwise specified. $ A "Version' indicated by -"x" after the Lab ID# with a value greater than I indicates a sample with amended data. The revision number is reflected by the value of N". 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Performance parameters shown on this sheet are calculated using test results on building components in the HUD archive. Testing was conducted on 146 test samples in November 2015, with two separate instruments running software version 2.1-2 in Action Level test mode. The actual source strength of each instrument on the day of testing was approximately 2.0 mCi; source ages were approximately one year. OPERATING PARAMETERS Performance parameters shown in this sheet are applicable only when properly operating the instrument using the manufacturer's instructions and procedures described in Chapter 7 of the HUD Guidelines. XRF CALIBRATION CHECK: The calibration of the XRF instrument should be checked using the paint film nearest 1.0 mg/cm2 in the NIST Standard Reference Material (SRM) used (e.g., for NIST SRM 2579, use the 1.02 mg/cm2 film). If the average (rounded to 1 decimal place) of three readings is outside the acceptable calibration check range, follow the manufacturer's instructions to bring the instrument into control before XRF testing proceeds. SUBSTRATE CORRECTION VALUE COMPUTATION: Chapter 7 of the HUD Guidelines provides guidance on correcting XRF results for substrate bias. Supplemental guidance for using the paint film nearest 1.0 mg/cmz for substrate correction is provided: XRF results are corrected for substrate bias by subtracting from each XRF result a correction value determined separately in each house for single-family housing or in each development for multifamily housing, for each substrate. The correction value is an average of XRF readings taken over the NIST SRM paint film nearest to 1.0 mg/cmz at test locations that have been scraped bare of their paint covering. Compute the correction values as follows: Using the same XRF instrument, take three readings on a bare substrate area covered with the NIST SRM paint film nearest 1 mg/cmz. Repeat this procedure by taking three more readings on a second bare substrate area of the same substrate covered with the NIST SRM. Compute the correction value for each substrate type where XRF readings indicate substrate correction is needed by computing the average of all six readings as shown below. For each substrate type (the 1.02 mg/cmz NIST SRM is shown in this example; use the actual lead loading of the NIST SRM used for substrate correction): Correction value = (1st + 2nd + 3rd + 4th + 5th + 6th Reading)/6 - 1.02 mg/cmz Repeat this procedure for each substrate requiring substrate correction in the house or housing development. EVALUATING THE QUALITY OF XRF TESTING: Randomly select ten testing combinations for retesting from each house or from two randomly selected units in multifamily housing. Conduct XRF re -testing at the ten testing combinations selected for retesting. Page 2 of 4 HEURESIS PCS September 2022 Determine if the XRF testing in the units or house passed or failed the test by applying the steps below. Compute the Retest Tolerance Limit by the following steps: Determine XRF results for the original and retest XRF readings. Do not correct the original or retest results for substrate bias. In single-family and multi -family housing, a result is defined as a single reading. Therefore, there will be ten original and ten retest XRF results for each house or for the two selected units. Calculate the average of the original XRF result and the retest XRF result for each testing combination. Square the average for each testing combination. Add the ten squared averages together. Call this quantity C. Multiply the number C by 0.0072. Call this quantity D. Add the number 0.032 to D. Call this quantity E. Take the square root of E. Call this quantity F. Multiply F by 1.645. The result is the Retest Tolerance Limit. Compute the average of all ten original XRF readings. Compute the average of all ten re -test XRF readings. Find the absolute difference of the two averages. If the difference is less than the Retest Tolerance Limit, the inspection has passed the retest. If the difference of the overall averages equals or exceeds the Retest Tolerance Limit, this procedure should be repeated with ten new testing combinations. If the difference of the overall averages is equal to or greater than the Retest Tolerance Limit a second time, then the inspection should be considered deficient. Use of this procedure is estimated to produce a spurious result approximately 1 % of the time. That is, results of this procedure will call for further examination when no examination is warranted in approximately 1 out of 100 dwelling units tested. TESTING TIMES: In the Action Level paint test mode, the instrument takes the longest time to complete readings close to the Federal standard of 1.0 mg/cm2. The table below shows the mean and standard deviation of actual reading times by reading level for paint samples during the November 2015 archive testing. The tested instruments reported readings to one decimal place. No significant differences in reading times by substrate were observed. These times apply only to instruments with the same source strength as those tested (2.0 mCi). Instruments with stronger sources will have shorter reading times and those with weaker sources, longer reading times, than those in the table. Mean and Standard Deviation of Reading Times in Action Level Mode by Reading Level Reading (mg/cm' Mean Reading Time seconds Standard Deviation seconds < 0.7 3.48 0.47 0.7 7.29 1.92 0.8 13.95 1.78 0.9 —1.2 15.25 0.66 1.3 —1.4 6.08 2.50 > 1.5 1 3.32 1 0.05 Page 3 of 4 HEURESIS PCS September 2022 CLASSIFICATION OF RESULTS: XRF results are classified as positive if they are greater than or equal to the stated threshold for the instrument (1.0 mg/cmz), and negative if they are less than the threshold. DOCUMENTATION: A report titled Methodology for XRF Performance Characteristic Sheets (EPA 747-R-95-008) provides an explanation of the statistical methodology used to construct the data in the sheets, and provides empirical results from using the recommended inconclusive ranges or thresholds for specific XRF instruments. The report may be downloaded at hftp://www2 epa.gov/lead/methodologv-xrf-performance-characteristic-sheets-epa-747-r-95- 008-september-1997. This XRF Performance Characteristic Sheet (PCS) was developed by QuanTech, Inc., under a contract with the XRF manufacturer. Page 4 of 4 APPENDIX C Sample Location Diagrams Auditorium Window 1 Front Desk Utility Women's Lobby Lobby Lobby Window 2 Window 1 Auditorium Window 2 �$. Auditorium/Meeting Room Interior Window Meeting Room Men's Restroom Auditorium Kingdom Hall Kodiak General Layout AN SATORIGROUP ,; toy, �o 1310 E 66th Ave, Ste 2, Anchorage, AK 99518 Auditorium Window 3 Auditorium Window 4 Auditorium Window 5 I Anna Scheiner I Anna Scheiner Project # 31679 04/03/2025 Lobby XX = Sample Non -Detect XX = Sample >1%Asbestos XX = Sample d% Asbestos = Sample Location = Doorway JL AL Meeting Room Auditorium /I Kingdom Hall Kodiak Asbestos Sample Locations ?a CO NG iO SATORIGROUP 1310 E 66th Ave, Ste 2, Anchorage, AK 99518 Project Designer: Anna Scheirer Project Contact: Anna Scheirer Project # 31679 Date: 04/03/2025 APPENDIX D Inspector Certifications 1* s, �1 4J O Q J x c R i f ow co N O N v N 7 O 7 El *7N3`Ob/yo w a rye E�hP F1'VIRONM N CN N to N cL m J c O U r N U M N O N Cl) T 7 U H M IUl r 1 � J �7 N �l eu ~ PSI O rri O � a . e�.� 1� C.� M ti Q O tm a N O ell O M O r 0 V a 00 Q 4 o� 0 DO 51-I (0 I A Gib cz r 0 U O � q V N R Na � � H H N 0 p LA b x U U� h y r u �a cc LO a o� W I co Q d 7 Q 9 w 0 M s I -1 M�04) � Cl u U �b FFN n G Lai m c MCI 0 v fi 5 ow N O N w N N 0 U M im c 0 Mn 0 C N E 0. 0 N N Q) N Of 06 N co E N L U C J *ON3Ob,y0 N � � a FVVIRONo M op a m J c O w r Q1 i N O N N N N LI 0 U Ee c 0 a m U1 0 � W O cd U a H � v goy � v H CN w� o z� a3 UQ APPENDIX E Site Photographs 10 Satori Group, Inc. Sample# Date I Time Location Sample# Date Time Location N/A 3/21/25 10:15 Kingdom Hall Kodiak —Main Lobby N/A 3121/25 10:15 Kingdom Hall Kodiak —Main Lobby am am Description of Photo: Photo of the main lobby and front entryway. Description of Photo: Photo of the main lobby and doorways to the restrooms and meeting room. kk Sample# Date Time Location Sample# Date Time Location N/A 3121125 10:20 Kingdom Hall Kodiak —Lobby Front N/A 3/21/25 10:20 Kingdom Hall Kodiak --Meeting Room am Desk am Description of Photo: Photo of the front desk in the lobby. Description of Photo: Photo of the meeting room. 1310 E. 660' Avenue, Ste. 2 — Anchorage, AK 99518 — Ph 907.332.0456 Fax 907.332.0457 www.gosatori.com 1T � I Satori Group, Inc. Sample# Date Time Location Sample# Date Time Location N/A 3121/25 10:20 Kingdom Hall Kodiak —Meeting Room N/A 3/21125 10:20 Kingdom Hall Kodiak —Auditorium am am Description of Photo: Photo of the meeting room with view of the Description of Photo: Photo of the auditorium as seen from the front interior window connecting with the auditorium. desk. i r Sample# Date Time Location Sample# Date Time Location N/A 3/21/25 10:21 Kingdom Hall Kodiak —Auditorium N/A 3121/25 10:15 Kingdom Hall Kodiak —Utility Room am am Description of Photo: Photo of the auditorium as seen from the exte- Description of Photo: Photo of the utility room with HVAC unit. rior. 1310 E. 66`h Avenue, Ste. 2 — Anchorage, AK 99518 — Ph 907.332.0456 Fax 907.332.0457 www.gosatori.co k Satori Group, Inc. Sample# Date Time Location Sample# Date Time Location N/A 3/21/25 10:15 1 Kingdom Hall Kodiak—Women's Re- NIA 3/21/25 10:15 Kingdom Hall Kodiak—Men's Re- am stroom am 1 stroom Description of Photo: Photo of the women's restroom. Description of Photo: Photo of the men's restroom. Sample# Date Time Location Sample# Date Time Location N/A 3/21125 10:23 Kingdom Hall Kodiak —Exterior N/A 3/21/25 10:24 Kingdom Hall Kodiak —Exterior am am Description of Photo: Photo of the front of the building with entry- Description of Photo: Photo of the southwest side of the building way, wooden walkway, and a mix of wood and stone siding. with entry leading to the auditorium. 1310 E. 66 h Avenue, Ste. 2 -- Anchorage, AK 99518 — Ph 907.332.0456 Fax 907.332.0457 www.gosatori.com Aft uVW' Satori Group, Inc. s Sample # Date Time Location Sample # Date Time Location N/A 3/21/25 10:24 Kingdom Hall Kodiak —Exterior N/A 3121/25 10:49 Kingdom Hall Kodiak —Meeting Room am am Description of Photo: Photo of the southeast side of the building with Description of Photo: Photo of the discolored ceiling tile on the west view of the locked entryway. side of the meeting room. / v Sample# Date Time Location Sample# Date Time Location A31679- 3121125 8:25 Kingdom Hall Kodiak —Utility Room A31679- 3121125 8.30 Kingdom Hall Kodiak —Utility 05 am 06 am Description of Photo: Photo of sample A31679-05 collected from the Description of Photo: Photo of sample A31679-06 collected from the j gypsum wallboard(oint compound wall in the utility room. Sample gypsum wallboardfjoint compound wall in the utility room. Sample contained <1% chrysotile asbestos. contained <1% chrysotile asbestos. 1310 E. 660i Avenue, Ste. 2 — Anchorage, AK 99518 — Ph 907.332.0456 Fax 907.332.0457 www.gosatori.com , s Satori Group, Inc. 0 V- Sample# Date Time Location Sample# Date Time Location A31679- 3/21/25 8:53 1 Kingdom Hall Kodiak—Women's Re- A31679- 3/21/25 9:25 Kingdom Hall Kodiak —Utility Room 07 am strocm 11 am Description of Photo: Photo of sample A31679.07 collected from the Description of Photo: Photo of sample A31679-11 collected from gypsum wallboardfjoint compound wall in the women's restroom. two layers of sheet vinyl flooring in the utility room. Sample con - Sample contained <1% chrysotile asbestos. tained 15% chrysotile asbestos. 1 Sample# Date Time Location Sample# Date Time Location A31679- 3/21/25 1 9:36 1 Kingdom Hall Kodiak --Utility Room ST31679- 3/21/25 8:21 Kingdom Hall Kodiak —Auditorium 12 am 01 am Description of Photo: Photo of sample A31679-12 collected from Description of Photo: Photo of sample ST31679-01 collected from two layers of sheet vinyl flooring in the utility room. Sample con- the auditorium. tained 20% chrysotile asbestos. 1310 E. 66°' Avenue, Ste. 2 — Anchorage, AK 99518 -- Ph 907.332.0456 Fax 907.332.0457 www�osatori.com Satori Group, Inc. i Sample# Date Time Location Sample# Date Time Location ST31679- 3121/25 8:05 Kingdom Hall Kodiak —Lobby Front ST31679- 3121/25 7:53 Kingdom Hall Kodiak —Meeting Room 02 am Desk 03 am Description of Photo: Photo of sample ST31679-02 collected from Description of Photo: Photo of sample ST31679-03 collected from the front desk in the lobby. the meeting room. l ,i j I Sample # Date Time Location Sample # Date Time Location ST31679- 3121125 7:41 Kingdom Hall Kodiak —Utility Room ST31679- 3/21/25 8:36 1 Kingdom Hall Kodiak —Exterior 04 am 05 am Description of Photo: Photo of sample ST31679-04 collected from Description of Photo: Photo of sample ST31679-05 collected from the utility room. the parking lot. 1310 E. 660' Avenue, Ste. 2 — Anchorage, AK 99518 — Ph 907.332.0456 Fax 907.332.0457 www.gosatori.com