abi hazmat corp. · abi hazmat corp. page 6 ahera# 1029230 2.0 introduction abi hazmat corp. (abi)...

ABI Hazmat Corp.

PRE – DEMOLITION HAZARDOUS & REGULATED MATERIALS SURVEY

Ministry of Transportation & Infrastructure Grube Pit Trailer #380, Chase, BC

PREPARED FOR:

Debbie Luison Property Management & Land Survey Coordinator

Ministry of Transportation & Infrastructure Southern Interior Region

342-447 Columbia St., Kamloops, BC V2C 2T3

PREPARED BY:

ABI HAZMAT CORP. 200 – 535 Tranquille Road

Kamloops, BC V2B 3H5

October 1, 2019

Grube Pit Trailer #380 September 30, 2019

Chase Gravel Pit PRE-DEMOLITION

Chase, BC HAZARDOUS MATERIALS SURVEY

ABI Hazmat Corp. AHERA# 1029230

TABLE OF CONTENTS

1.0 EXECUTIVE SUMMARY 4

2.0 INTRODUCTION 6

3.0 REGULATIONS & GUIDELINES 7

3.1 Provincial Regulations 7

3.1.2 Hazardous Materials & Demolition/Renovations 7

3.1.3 Hazardous Wastes 7

3.1.4 Asbestos-Containing Materials (ACMs) 8

3.1.5 Lead & Lead-Based Coatings (LBCs) Sections 6.59 to 6.69 – Lead 9

3.1.6 Ozone-Depleting Substances (ODS) 10

3.1.7 Silica Dust 10

3.2 Applicable Federal Legislation 11

3.2.1 Polychlorinated Biphenyls (PCBs) 11

3.2.2 Transportation of Dangerous Goods 12

4.0 RESULTS 13

4.1 ASBESTOS 13

4.2 POLYCHLORINATED BIPHENYLS (PCBS) 14

4.2 LEAD & LEAD-BASED COATINGS (LBCs) 14

4.4 MERCURY CONTAINING MATERIALS 15

4.5 OZONE-DEPLETING SUBSTANCES (ODS) 15

4.6 RESPIRABLE CRYSTALLINE SILICA (RCS) 15

4.7 OTHER POTENTIALLY HAZARDOUS MATERIALS 16





5.0 RECOMMENDATIONS 17

6.0 STATEMENT OF LIMITATIONS 18

7.0 REFERENCES 19

APPENDICES Suspect Asbestos Bulk Sample Laboratory Results Appendix A Suspect Lead Bulk Sample Laboratory Results Appendix B Site Photos Appendix C





1.0 EXECUTIVE SUMMARY

ABI Hazmat Corp. (ABI) was retained by Ministry of Transportation & Infrastructure, to

perform a Pre-Demolition Hazardous and Regulated Materials Survey. The hazardous

materials survey was conducted for the Grube Pit Trailer #380, located at in Chase, BC.

The survey was conducted on September 30,2019 by Ms. Sue Servia Environmental

Technologist EPT. Ms. Servia has completed the AHERA Certification Course required

by WorkSafeBC to conduct Hazmat Surveys.

The objective of the assessment was to identify the types, condition and extent of

hazardous materials that would be impacted during the demolition of the building. The

building is a wood frame approximately 624sq. ft. trailer, with a sheet metal roof and

siding. Trailer main construction Steel transport beams.

It was noted during the inspection of the north facing exterior wall of the trailer, that a

significant impact had occurred in the mid section of the north facing wall. ABI would

recommend that should an abatement take place within the trailer, that the structure be

surveyed by a structural engineer to insure stability of the trailer prior to abatement

commencement. (See Site Photos in Appendix C)

The survey was conducted using both visual and physical assessment techniques.

Samples of materials suspected of containing asbestos and collected include vinyl sheet

floor and drywall joint compounds. In total, five (5) suspect asbestos building material

samples were collected from the building to be analyzed for asbestos content. Three

(3) lead paint samples were collected from the interior of the building. Paint containing

lead greater than the laboratory limit of detection (>20mg/kg or ppm) is considered Lead

Based Paint according to the new WorkSafeBC May 2017 Publication.

Suspect asbestos containing samples were collected and submitted to Coast BC

Hazmat Inspections Inc. to be analyzed in accordance with the WorkSafeBC

Occupational Health & Safety Regulations and/or the National Institute of Occupational

Health and Safety (NIOSH) analytical methods. Suspect asbestos bulk sample results

are in Appendix A of this report. Suspect Lead in Paint/Coatings results are in Appendix

B of this report.





The building was also inspected for possible PCB (polychlorinated biphenyls) containing

fluorescent light ballasts, mercury containing thermostat switches, RCS (respirable

crystalline silica) and other hazardous materials during the inspection.

In summary, the findings from the assessment conclude that asbestos containing

materials are present in the construction materials of the trailer building. These

materials are present in quantities of significance and are of concern to any

contractor involved in the renovations of the building.

Asbestos containing Yellow Vinyl Sheet Flooring was discovered, hidden, under

newer flooring, through-out the washroom and office areas of the building.

All lead paint samples were found to have lead levels ranging from 189 ppm to

520 ppm, above the laboratory LOD (Limit of Detection) of 20 mg/kg or ppm (parts

per million).

Mercury vapour may exist within the fluorescent lighting bulbs of the lighting

fixtures, located in the in the office debris pile and office ceiling area of the

building.

Suspect – PCB ballasts were observed in the debris pile and office ceiling fixtures

building.

Ozone-Depleting Substances (ODS) are suspect due to a small HVAC and boiler

system observed in the Washroom area of the trailer.

(See site photos in Appendix C)





2.0 INTRODUCTION

ABI Hazmat Corp. (ABI) was retained by Ministry of Transportation & Infrastructure to

perform a Pre-demolition Hazardous and Regulated Materials Survey. The hazardous

materials survey was conducted for the Grube Pit Trailer #380, located at in Chase, BC.

The survey was conducted on September 30, 2019, BC. by Ms. Sue Servia

Environmental Technologist EPT and AHERA Certified building inspector for ABI

Hazmat Corporation.

Section 20.112 of the BC OH&S Regulation details the requirements that employers

and owners are responsible for before beginning work on the demolition, renovation

or salvage of machinery, equipment, buildings, or structures. The employer or owner

must inspect the site to identify any asbestos, lead and/or other potentially hazardous

materials that may be handled, disturbed, or removed through renovations.

The objective of the assessment was to identify the types, condition and extent of

hazardous materials that would be impacted during the demolition of the building. The

building exterior is plywood and sheet metal and interior walls were observed to be

constructed of wood panel materials. The majority of the flooring was constructed of

vinyl sheet flooring with a plywood substrate.

The survey was conducted using both visual and physical assessment techniques. In

total, five (5) suspect asbestos building material samples were collected from the

building to be analyzed for asbestos content.

Samples of suspect asbestos were collected and submitted to Coast BC Hazmat

Inspections Inc. to be analyzed in accordance with the WorkSafeBC Occupational

Health & Safety Regulations and the National Institute of Occupational Health and

Safety (NIOSH) analytical methods. Suspect asbestos bulk sample results are included

in Appendix A of this report.





3.0 REGULATIONS & GUIDELINES

3.1 Provincial Regulations

In British Columbia, the management of hazardous building materials in the workplace

is regulated by WorkSafeBC under the Workers’ Compensation Act (effective April 15,

1998), as amended by the Workers’ Compensation (Occupational Health and Safety)

Amendment Act (effective October 1, 1999). Specific requirements of the Occupational

Health and Safety Amendment Act are prescribed in the British Columbia Occupational

Health and Safety (BC OH&S) Regulation.

3.1.2 Hazardous Materials & Demolition/Renovations

Section 20.112 of the BC OH&S Regulation details the requirements that employers

and owners are responsible for before beginning work on the demolition, renovation

or salvage of machinery, equipment, buildings, or structures. The employer or owner

must inspect the site to identify any asbestos, lead and/or other potentially hazardous

materials that may be handled, disturbed, or removed through renovations.

3.1.3 Hazardous Wastes

In British Columbia, environmental matters pertaining to waste generally fall under the

jurisdiction of the British Columbia Ministry of Environment (MoE), pursuant to the

Environmental Management Act. The key waste regulation under the Environmental

Management Act relating to hazardous building materials is the Hazardous Waste

Regulation (HWR), as amended from time to time. The HWR provides the

requirements for the proper handling, storage, transportation, treatment, recycling and

disposal of hazardous wastes in the province. The regulation also outlines the

materials and criteria to be used to characterize waste as hazardous.





3.1.4 Asbestos-Containing Materials (ACMs)

ACMs are regulated under Part 6 (sections 6.1 to 6.32) of the BC OH&S Regulation.

General requirements prescribed in these sections are summarized below:

Section 6.1 – Definitions

An ACM is defined as any manufactured article or other material, other than vermiculite

insulation, that would be determined to contain at least 0.5% asbestos through

analytical testing. Materials other than vermiculite must be tested in accordance with

one of the following methods:

“Asbestos, Chrysotile by XRD, Method 9000” (Issue 2, dated August 15, 1994) in the

NIOSH Manual of Analytical Methods, published by the United States National Institute

for Occupational Safety and Health, Centre for Disease Control;

“Asbestos (bulk) by PLM, Method 9002” (Issue 2, dated August 15, 1994) in the NIOSH

Manual of Analytical Methods, published by the United States National Institute for

Occupational Safety and Health, Centre for Disease Control; or,

“Test Method for the Determination of Asbestos in Bulk Building Materials” (EPA/600/R-

93/116, dated July 1993) published by the United States Environmental Protection

Agency.

Section 6.2 Application

Sections 6.3 to 6.32 apply to a workplace where a worker is or may be exposed to potentially harmful levels of asbestos fibre, including a workplace where asbestos-containing material is present.

Section 6.3 – Exposure Control Plan

For this section of the BC OH&S Regulation, if a worker is or may be exposed to

potentially harmful levels of asbestos, the employer must develop and implement an

exposure control plan meeting the requirements of section 5.54 of the BC OH&S





Regulation. Additionally, and to ensure adequate coordination of the overall plan,

the employer must ensure that it is administered by a properly trained person.

Section 6.4 – ACM Inventory

For this section of the BC OH&S Regulation, the employer must ensure that a qualified

person collects representative samples of the materials in the workplace that the

qualified person suspects contain asbestos, and, through appropriate analysis and

professional judgment, determines whether each of the samples is an ACM.

This section of the BC OH&S Regulation also states that if a qualified person suspects

that an inaccessible material contains asbestos, the material must be treated as

asbestos-containing material unless a qualified person determines that it is not ACM.

WorkSafeBC Manual - Safe Handling of Asbestos, A Manual of Standard Practices

This manual outlines basic information on asbestos and asbestos products, health

hazards requirements for worker protection, safe work procedures and principles that

should be followed in selecting the most suitable technique for the safe abatement

of ACM. This document provides a guide to current practices that are to be followed

in the Province of British Columbia.

3.1.5 Lead & Lead-Based Coatings

(LBCs) Sections 6.59 to 6.69 – Lead

These sections of the BC OH&S Regulation describe specific requirements to:

• Develop and implement an exposure control plan if workers are or may be

exposed to lead;

• Conduct air monitoring if workers are at risk of overexposure to airborne

lead in a construction project;

• Post warning signs at the boundary of work areas where hazardous lead

exposures could occur;

• If lead might contaminate exposed skin or work clothing, meet the

requirements for personal hygiene;

• Keep work area surfaces free of lead dust as much as possible;

• When removing lead dust, use a method that avoids spreading it into other work





areas;

• Instruct and train workers who are at risk of exposure to lead;

• Develop and implement a health protection program if workers are exposed to

potentially hazardous levels of lead; and,

• Maintain records of risk assessments, worker exposures, and worker training.

WorkSafeBC Manual – Lead-Containing Paints and Coatings – Preventing Exposure

in the Construction Industry

This manual provides a guide to current practices that are to be followed in the Province

of British Columbia, providing basic information on lead and lead products, health

hazards and requirements for worker protection, safe work procedures and principles

that should be followed in selecting the most suitable technique for the safe abatement

of lead.

3.1.6 Ozone-Depleting Substances (ODS)

Provincial regulatory framework providing the requirements for the safe management,

storage and disposal of ozone-depleting substances are provided in British Columbia

Regulation (BC Reg.) 387/99, as amended from time to time – Ozone-Depleting

Substances Regulation respecting the appropriate management of ozone-depleting

substances within the province of British Columbia.

3.1.7 Respirable Crystalline Silica (RCS)

Sections 6.110–6.115 of the Occupational Health Safety (OHS) Regulation and related

OHS Guidelines have been updated to clarify employer requirements to protect workers

from the harmful effects of silica dust. Changes to the Regulation expand the sections

on rock dust to include specific regulations for protecting workers from the risks of

exposure to respirable crystalline silica (RCS) dust.

Silica is the basic component in sand and rock. It's in construction materials such as:

• Concrete, concrete block, cement, and mortar

• Masonry, tiles, brick, and refractory brick

• Granite, sand, fill dirt, and top soil





• Asphalt-containing rock or stone

• Abrasive used for blasting

Silica is the most common hazard on a work site. Any activity that creates dust can

expose workers to airborne silica. The most common ways to create silica dust are as

follows:

• Chipping, sawing, grinding, hammering, or drilling

• Crushing, loading, hauling, or dumping

• Building demolition

• Power cutting or dressing stone

• Facade renovation, including tuck-point work

• Abrasive or hydro blasting

• Dry sweeping or pressurized air blowing

• Tunneling, excavating, or earth moving

Inhaling silica dust can cause silicosis, a serious and irreversible lung disease. It can

be lethal. Silica damages the lung and causes scar tissue to form. This causes the lung

tissue to become thicker. Silica exposure can also cause lung cancer.

If a worker is or may be exposed to potentially harmful levels of respirable crystalline

silica, the employer must develop and implement an exposure control plan meeting the

requirements of section 6.110-6.115 of the BC OH&S Regulation. Additionally, and to

ensure adequate coordination of the plan, the employer must ensure that it is

administered by a properly trained person.

3.2 Applicable Federal Legislation

3.2.1 Polychlorinated Biphenyls (PCBs)

The PCB Regulations SOR/2008-273 came into force on September 5, 2008. The

purpose of the regulations is to improve the protection of Canada’s environment

and the health of Canadians by minimizing the risks posed by the use, storage and

release of PCBs and by accelerating the elimination of these substances. The

Regulations also set out end-of-use and end-of-storage dates for PCBs. These dates

are listed in Environment Canada’s fact sheet, "PCB Regulations: An Overview."





In addition, Environment Canada has published a report entitled, “Identification of

Lamp Ballasts Containing PCBs”, revised in August 1991. This report can be reference

to determine the PCB-content in fluorescent lamp ballast.

3.2.2 Transportation of Dangerous Goods

The transportation of hazardous wastes is governed under the Transportation of

Dangerous Goods (TDG) Act and Regulations which outline the requirements for

storage, handling, and transportation of hazardous waste, among other products.





4.0 RESULTS

4.01 Table 1 - Suspect Asbestos Laboratory Results

Sample ID Location Material Type Asbestos Type & Amount Approx. Quantity

SS-1576 Inside

Washroom Area

Debris Pile

Filler Compound Non-Detected

Mesh Non-Detected

SS-1577 Washroom

Floor Area

Vinyl Sheet

(Top layer)

Non-Detected

Vinyl Sheet

(Backing)

Non-Detected

SS-1578 Laundry Room

Floor Area

Vinyl Sheet

(Top layer)

Non-Detected

Vinyl Sheet

(Backing)

Non-Detected

SS-1579 Washroom

Office

Composite

flooring sample

Vinyl Sheet

(Top layer)

Non-Detected

Vinyl Sheet

(Backing)

30% Chrysotile Asbestos 528 Sq. ft

SS-1580 Washroom,

Wall/Sink Area

Mastic Non-Detected

Samples highlighted in RED are ASBESTOS CONTAINING.

4.1 ASBESTOS

Vinyl Sheet Flooring (VFT) Materials:

Asbestos containing yellow Vinyl Sheet Flooring materials were observed as

hidden flooring in the washroom and back office areas only. The sheet flooring

materials were sampled and found to contain 30% Chrysotile asbestos in the

paper backing. These VSF materials were observed to be in good to fair condition.

Prior to any demolition activities taking place which could disturb the asbestos

containing vinyl sheet flooring materials, the materials must first be removed and

disposed of in accordance with applicable regulations. Due to the high friability and

high asbestos content, the removal of these materials will pose a high risk of

asbestos exposure to the workers involved. Therefore, as a minimum, HIGH RISK





asbestos safe work procedure will be required for the removal of the asbestos

containing vinyl sheet flooring materials.

4.2 POLYCHLORINATED BIPHENYLS (PCBS)

Fluorescent light fixtures were observed within the debris pile/ Office area of the

building. The ballast within the lighting fixture inspected were observed to be Suspect

PCB containing.

If a light fixture with a PCB containing ballast is discovered, it must be removed from

the fixture and disposed of in accordance with applicable regulations. If the lighting

ballast does not contain PCBs, it will be stated on the ballast label as “no PCBs” and

all ballasts not labelled as non-PCB containing must be treated as PCB containing.

Environment Canada has published a report entitled, “Identification of Lamp Ballasts

Containing PCBs”, revised in August 1991. This report can be referenced to

determine the PCB-content in fluorescent lamp ballast.

4.3 LEAD & LEAD BASED COATINGS (LBC)

4.3.1 TABLE 2 - SUSPECT LEAD IN PAINT RESULTS TABLE

Sample ID Location Material Type Amount Present

(PPM)

Approx. Quantity

SS-1581 Washroom Wall Paint Chip

(Blue)

520 290 Sq. Ft

SS-1582 Laundry Room

Wall

Paint Chip

(Yellow)

189 96 Sq. Ft

SS-1583 Washroom

Wall

Paint Chip

(White)

241 290 Sq. Ft

ALL paint samples collected from within the interior paint colours (Blue, Yellow,

White) are above the laboratory 20 mg/kg or 20 ppm LOD (limit of detection) for

Lead.

These materials will require an Exposure Control Plan and site-specific lead

paint safe work procedures (precautions during demolition).





ABI recommends reference to WorkSafeBC publication “WorkSafeBC - Safe Work

Practices for Handling Lead”, May 2017. This manual provides a guide to current

practices that are to be followed in the Province of British Columbia, providing basic

information on lead and lead products, health hazards and requirements for worker

protection, safe work procedures and principles that should be followed in selecting the

most suitable technique for the safe abatement of LBCs.

Lead may exist in the old copper soldering joints within wall/ceiling cavities.

Suspect lead containing roof vent pipe materials should also be separated from

regular waste and disposed of in accordance with applicable regulations.

4.4 MERCURY CONTAINING MATERIALS

A mercury containing thermostat switch was not observed within the building

during the hazardous materials assessment. Should they be discovered during

the demolition they must first be removed and disposed of in accordance with

applicable regulations. Mercury containing switches are not considered to be a hazard

to workers removing them, if care is taken to ensure that the switches remain intact when

removed.

Mercury vapour will be present in any fluorescent light tubes. Avoid breaking

the ballast and inhaling the mercury vapour. Fluorescent light tubes can be

recycled to capture the mercury or saved for re-use in the new lighting.

4.5 OZONE-DEPLETING SUBSTANCES (ODS)

Heating/cooling HVAC unit was observed within the trailer. Suspect ODS containing

refrigerants encountered within the units must be properly captured and disposed of by

a licensed refrigeration mechanic or taken to a proper disposal facility in accordance

with applicable regulations.





4.6 RESPIRABLE CRYSTALLINE SILICA (RCS)

Suspect RCS (respirable crystalline silica materials were not observed on site.

4.7 OTHER POTENTIALLY HAZARDOUS MATERIALS

No significant signs of mold were observed within the building. Hazardous materials

such as paint cans, chemicals, compressed gas cylinders, oil containers, batteries, etc.

encountered during demolition, must be separated from the demolition waste and will

require proper disposal in accordance with applicable regulations. Note: Paint cans

were observed in the office area of the trailer.





5.0 RECOMMENDATIONS

Prior to any renovation work that may impinge upon the hazardous materials within the

building, the following must be performed:

1.) The removal of asbestos containing materials from the building must be performed

following the risk assessment provided in the results section of this report and by a

competent abatement/demolition contractor. The abatement contractor must have site

specific work procedures on site prior to the start of any work activities.

2.) If any suspect asbestos-containing materials are encountered within walls, above

ceilings, or under floors during demolition activities, the work in the immediate area must

stop and the supervisor must be informed. The supervisor should contact ABI Hazmat

Corp. for further directions and potentially update the risk assessment if the materials

are found to be asbestos containing.

3.) Any lead plumbing drain joints and/or vent pipes discovered within the building must

be separated from the building waste prior to renovation/demolition and disposed of

properly in accordance with applicable regulations. Lead Based Paint materials will

require reference to WorkSafeBC publication “WorkSafeBC - Safe Work Practices

for Handling Lead”, May 2017. This manual provides a guide to current practices

that are to be followed in the Province of British Columbia, providing basic

information on lead and lead products, health hazards and requirements for worker

protection, safe work procedures and principles that should be followed in selecting

the most suitable technique for the safe abatement of LBCs

4.) Mercury containing fluorescent light tubes impacted during the demolition will need

to be re-cycled and or disposed of in accordance with applicable regulations.

5.) Hazardous materials such as paint cans, chemicals, compressed gas cylinders, oil

containers, batteries, etc. must be separated from the renovation waste and will require

proper disposal in accordance with applicable regulations.





6.0 STATEMENT OF LIMITATIONS

This report is intended to direct the Client's attention to recognised environmental

conditions and to potential sources of environmental contamination. The findings and

conclusion regarding contamination of the property are based solely on the extent of

observations and information gathered during the survey. Nothing in the report is

intended to express any legal opinion upon environmental liabilities relating to the site

or whether operations legally conformed with relevant legislative requirements.

Also, it must be understood that changing circumstances in the physical environment,

the use of the property, as well in changes in any substances stored, used, handled at

the property, could radically alter the conclusions and information contained in this

report. Therefore, it is important that the property is periodically re-evaluated and the

client kept informed as to developments, which may impact the property. This report is

not intended as contract specifications.

Survey Conducted and Report Prepared By:

ABI Hazmat Corp.

Sue Servia Environmental Technologist EPT AHERA Certified Building Inspector C18-29463 Approved By:

_____________________

James McArthur, AScT, ABI (AHERA# 1029230)

President





7.0 REFERENCES

1) USEPA. 1985. U.S. Environmental Protection Agency. "Guidance for Controlling

Asbestos-Containing Materials in Buildings". Washington, DC: Office of Toxic

Substances, USEPA.

2) Lory EE, Coin DC. 1981. "Management Procedure for Assessment of Friable

Asbestos Insulating Material". Port Hueneme, CA: Civil Engineering Laboratory, Naval

Construction Battalion Center.

3) WorkSafeBC BC. “Occupational Health and Safety Regulations”.

4) WorkSafeBC BC, 2012 Editions. “Safe Work Practices for Handling Asbestos”.

5) WorkSafeBC, May 2017 Edition. ““Safe Work Practices for Handling Lead”.

APPENDIX A

Suspect Asbestos Laboratory Bulk Sample Results

O: 604 593 8275 F: 604 593 8276 CLIENT ID: ABI Hazmat Corp.

WWW.BCHAZMATINSPECTIONS.CA SAMPLES SUBMITTED BY: Sue Servia [email protected] LOCATION: Okanagan Shuswap District, Chase

#220-19358 96 AVENUE DATE ANALYZED: Sept 30/2019

COAST BC HAZMAT INSPECTIONS INC.SURREY, BC V4N 4C1 BCHI ID: 21179

BCHI CLIENT SAMPLE MATERIAL OTHER MATERIAL ASBESTOS TYPE

SAMPLE ID SAMPLE ID LOCATION TYPE & AMOUNT & AMOUNT

21179-1 SS-1576 Inside washroom, Area, Filler compound Cellulose 2% Not Detected

Debris pile Non fibrous 98%

Mesh Fiberglass>99% Not Detected

21179-2 SS-1577 Washroom area, Floor Vinyl sheet, Vinyl top Non fibrous>99% Not Detected

Vinyl sheet, Backing Cellulose 30% Non fibrous 70%

Not Detected

21179-3 SS-1578 Laundry room, Floor Vinyl sheet, Vinyl top Non fibrous>99% Not Detected

Vinyl sheet, Backing Cellulose 30% Non fibrous 70%

Not Detected

21179-4 SS-1579 Washroom, Office, Floor Vinyl sheet, Vinyl top Non fibrous>99% Not Detected

Vinyl sheet, Backing Non fibrous 70% Chrysotile 30%

21179-5 SS-1580 Washroom, Wall Mastic Non fibrous>99% Not Detected

Analytical Method: NIOSH 9002 Analyst: Baraa Habash

Coast BC Hazmat Inspections Inc. participates in the AIHA bulk asbestos

proficiency analytical testing program, participant number 223436

APPENDIX B

Suspect Lead in Paint Laboratory Results

O: 604 593 8275 F: 604 59 CLIENT ID: ABI Hazmat

WWW.BCHAZMATINSPECTIO SAMPLES SUBMITTED BY: Sue Servia

INFO@BCHAZMATINSPECTIO LOCATION: Okanagan Shuswap District, Chase

#220-19358 96 AVENUE DATE ANALYZED: Sept 30/2019

COAST BC HAZMAT INSPECTIONS INC. SURREY, BC V4N 4C1 BCHI ID: 21179-1

XRF LEAD RESULTS

BCHI

CLIENT

SAMPLE

MATERIAL

COLOR

LEAD

Variance +/-

Result

SAMPLE ID

SAMPLE ID

LOCATION TYPE CONCENTRATION (PPM)

Positive/Negative

21179-1-1

SS 1581 Washroom, Wall

Paint chip Blue 520 24 Positive

21179-1-2

SS 1582 Laundry room, Wall

Paint chip Yellow 189 18 Positive

21179-1-3

SS 1583 Washroom, Wall

Paint chip White 241 18 Positive

Equipment Used: Bruker Titan 500 XRF Analyzer Analyst: Caitlin Paulson

Health Canada states samples > 90 PPM to be Lead Containing

APPENDIX C

Site Photos

Additional site photos are available upon request

“Asbestos Containing Vinyl Sheet Flooring “Described as yellow in colour with flower Design”

HVAC & Boiler Systems: Located in the Washroom Area.

Fluorescent Tube Lighting Fixtures: Located in the office area of the trailer.

Paint Cans Observed in the office area

Structural Impact Area

abi hazmat corp. · abi hazmat corp. page 6 ahera# 1029230 2.0 introduction abi hazmat corp. (abi)...

Documents