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".
Eurofins Built Environment Testing West, LLC EMLab ID: 4000211, Page 4 of 4
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4
HEURESIS PCS September 2022
Performance Characteristic Sheet
EFFECTIVE DATE: September 1, 2022
MANUFACTURER AND MODEL:
Make: Heuresis
Models: Model Pb200i, Pb200e
Source: "Co, 5 mCi (nominal -new source)
FIELD OPERATION GUIDANCE
OPERATING PARAMETERS:
Action Level 1.0 mg/cm2
XRF CALIBRATION CHECK LIMITS:
0.8 to 1.2 mg/cm2 (inclusive)
Not applicable
INCONCLUSIVE RANGE OR THRESHOLD:
ACTION LEVEL MODE
SUBSTRATE
THRESHOLD (mg/Cm2)
READING DESCRIPTION
Results not corrected for substrate bias on any
Brick
1.0
substrate
Concrete
1.0
Drywall
1.0
Metal
1.0
Plaster
1.0
Wood
1.0
Page 1 of 4
HEURESIS PCS September 2022
BACKGROUND INFORMATION
EVALUATION DATA SOURCE AND DATE:
This sheet is supplemental information to be used in conjunction with Chapter 7 of the HUD Guidelines for the
Evaluation and Control of Lead -Based Paint Hazards in Housing ("HUD Guidelines"). 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
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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