Designated Substance Report
Agincourt Road Public School
1250 Agincourt Road, Ottawa, ON
DESIGNATED SUBSTANCE REPORT
AGINCOURT ROAD PUBLIC SCHOOL
1250 AGINCOURT RD., OTTAWA, ONTARIO
Prepared For:
Mr. Greg Welby
Design & Construction
1224 Stittsville Main Street
Stittsville, Ontario.
K2S 0E2
Prepared by:
208-120 Robertson Road
Ottawa, Ontario
K2H 5Z1
Richard Pope, A.Sc.T.
Project Manager
David Morroz, C.E.T.
Principal
May 2012
Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
EXECUTIVE SUMMARY
CM3 Environmental Inc. (CM3) was commissioned by the Ottawa Carleton District School Board (OCDSB)
to conduct a quantitative asbestos survey for Agincourt Road Public School located at 1250 Agincourt
Road, Ottawa, Ontario. This work was completed in order to comply with Ontario Regulation 278/05
“Regulation Respecting Asbestos on Construction Projects and in Buildings and Repair Operations”. A
Designated Substance Survey (DSS) is also required under Section 30 of the Occupational Health and
Safety Act in order to identify and inventory designated substances that may be present.
CM3’s findings are summarized in the following table:
Executive Summary Table – Agincourt Road Public School
Designated Substance
Items of Concern
Recommendations
The
following
materials
were Immediate repair of damaged pipe
confirmed to contain asbestos:
insulation in Room 128.
 Mechanical insulation on pipe
Ensure that all asbestos containing
straight and fittings,
materials that have the potential
 Ceiling tile mastic;
to be damaged during renovation
 Drywall joint compound; and,
or demolition activities are
 Vinyl floor tiles & mastic.
managed following the procedures
The following materials are presumed outlined in Ontario Regulation
to contain asbestos, and were not 278/05.
sampled in order to main the integrity
Asbestos
Core samples of the roofing
of the building component:
membrane should be taken on a
 Roof membrane;
project-by-project basis.
 Exterior plaster on overhang;

and,
Fire resistant doors.
Lead was detected 9 of 11 paint
samples submitted for analysis.
Lead
Lead may be present in solder joints,
glazing on ceramic finishes and on all
copper piping throughout the subject
building.
Implement
an
Asbestos
Management Plan (AMP), as
outlined in Ontario Regulation
278/05.
Routine surveillance of asbestos
containing materials as per
Ontario Regulation 278/05.
It is recommended that if materials
containing lead are to be
disturbed,
then
procedures
outlined in the ministry of labour
“Guideline – Lead on Construction
Projects” should be followed.
In the event of a major renovation
or demolition, ensure that
construction waste materials will
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
Mercury vapour is assumed to be
present within fluorescent light tubes
and High Intensity Discharge (HID)
bulbs that are located in the subject
building.
Mercury
Ozone Depleting
Substances (Also
referred to as
Chlorofluorocarbons)
Polychlorinated
Biphenyls (PCB’s)
Silica
satisfy
the
general
waste
management regulation 558.
If work on mercury containing
materials is likely to produce
mercury dust or fumes, for
example during welding, torch
cutting, grinding, sanding or
sandblasting,
then
proper
precautions should be followed.
Prior to demolition, all fluorescent
light tubes should be packaged
and removed by a licensed
contractor.
ODS’s can be found in applications Prior to handling and/or disposal, a
such as refrigerants in heat pumps, licensed technician should remove
refrigerators,
freezers
and
air all base building CFCs, in
conditioners (A/C).
accordance with the Federal
Halocarbon Regulation, 2003.
PCB’s can be found in equipment such
as
transformers,
capacitors,
electromagnets, heat transfer units,
hydraulic engine and fluorescent lamp
ballasts. Fluorescent lamp ballasts
may contain minor quantities of PCBs
(23.6 g).
Crystalline silica is assumed to be
present in the building within concrete
structures such as walls, floors and
stairs. Silica can also be found in
cement blocks, acoustic tiles and
plaster.
Other
Designated The remaining designated substances
Substances
are not usually found in building of this
ii
Non-base building units (i.e.
window A/Cs, refrigerators, and
freezers) should be relocated or
reused rather than destroyed. If
the units will not be relocated,
then a licensed technician should
remove the refrigerants.
Prior to any renovation or
demolition, all ballasts should be
compared to the information
outlined in the 1991 Environment
Canada publication “Identification
of Lamp Ballasts Containing PCBs”
and
removed/disposed
of
accordingly
During renovation or demolition
ensure that work areas are well
ventilated, wash stations are
present for worker protection and
that the maximum allowable
airborne concentration for all silica
forms is not exceeded. All work
should be completed following the
Ministry of Labour “Guideline –
Silica on Construction Projects”.
No recommendations.
Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
type, and are typically part of an
industrial process.
iii
Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
TABLE OF CONTENTS
PART 1 - GENERAL ........................................................................................................................ 1
1.1
1.2
1.3
REGULATORY REQUIREMENTS .................................................................................................................. 1
SCOPE ......................................................................................................................................................... 1
THE SUBJECT FACILITY ............................................................................................................................... 2
PART 2 - DESIGNATED SUBSTANCES ............................................................................................... 3
2.0
ASBESTOS ................................................................................................................................................... 3
2.0.1
2.0.2
2.0.3
2.0.4
2.0.5
2.1
2.2
2.3
2.4
2.5
2.6
Target Materials .......................................................................................................... 3
Analytical Procedure ................................................................................................... 4
Reporting ..................................................................................................................... 4
Drawings ...................................................................................................................... 5
Findings ....................................................................................................................... 5
LEAD ........................................................................................................................................................... 8
MERCURY ................................................................................................................................................... 8
OZONE DEPLETING SUBSTANCES ............................................................................................................... 9
POLYCHLORINATED BIPHENYLS ................................................................................................................. 9
SILICA ....................................................................................................................................................... 10
OTHER DESIGNATED SUBSTANCES .......................................................................................................... 10
PART 3 – RECOMMENDATIONS ................................................................................................... 11
APPENDICES
APPENDIX A – Drawings
APPENDIX B – Analytical Results
APPENDIX C – Other Designated Substances
APPENDIX D – Statement of Limitations
APPENDIX E – Asbestos Inventory Summary Table
TABLES
Table 1 – Paint Analysis, Lead (Pb) Content
Table 2 – Paint Analysis, Mercury (Hg) Content
Page 8
Page 8
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
PART 1 - GENERAL
1.1
REGULATORY REQUIREMENTS
The completion of this survey and the presentation of the findings herein were made to fulfill the
Owner's requirement to complete an inventory of asbestos containing materials (ACMs) to comply with
Ontario Regulation 278/05, “Regulation Respecting Asbestos on Construction Projects and in Buildings
and Repair Operations”.
CM3 further enhanced the survey to include other designated substances regulated under Ontario
Regulation 490/09 of the Occupational Health and Safety Act OHSA. Under Section 30 of the OHSA, a
project owner “shall determine whether any designated substances are present at the project site and
shall prepare a list of all designated substances that are present”.
The following is a list of substances regulated by O.Reg 490/09.











Acrylonitrile
Arsenic
Asbestos
Benzene
Coke Oven Emissions
Ethylene Oxide
Isocyanates
Lead
Mercury
Silica
Vinyl Chloride
The following Hazardous Building Materials are not Designated Substances regulated by 490/09, but
could pose a significant risk to health and safety of workers, occupants, and the environment are
included as part of this report. The Ministry of Labour (MOL) recognizes them as workplace hazards and
enforces worker protection under the General Duty Clause 25(2) (h) of the OHSA. Clause 25(2) (h) states
that the employers are required to “take every precaution reasonable in the circumstances for the
protection of a worker”. In such cases the MOL will refer to industry standards and guidelines for the
safe handling and management of such materials.


1.2
Ozone Depleting Substances (ODSs) - Federal Halocarbon Regulation 2003
Polychlorinated Biphenyls (PCBs) - SOR/2008-273
SCOPE
This report is based on the site inspections conducted April 25th, 2012 by Richard Pope, A.Sc.T. of CM3.
The area of the survey is outlined in the drawing in APPENDIX A.
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
Non-destructive survey techniques were employed during the site reconnaissance. The visual inspection
and sampling was limited to readily accessible areas. The survey did not include the demolition of fixed
ceilings or walls, or other areas to examine concealed conditions. Samples were obtained to update
facility asbestos records and in order to bring the facility into compliance with Ontario Regulation
278/05 “Regulation Respecting Asbestos on Construction Projects and in Buildings and Repair
Operations”. Suspect ACMs and paint samples for lead analysis were sent for analysis to Steve Moody
Micro Services, LLC in Farmers Branch, Texas.
The designated substances mentioned above may be present in partial and non-accessed areas and
concealed spaces (i.e. wall and ceiling cavities). Furthermore, materials located within wall cavities
could not be observed in order to determine their condition. In addition, CM3 would extrapolate
quantities based on quantities observed in fully accessible locations.
This designated substance survey report has been prepared using the information provided to CM3 by
the OCDSB, through information obtained during the site reconnaissance and analytical data.
The survey does not refer to substances that may be present in the day-to-day usage for other
specialized equipment or areas in buildings (i.e. portable equipment, lead shields, fume hoods, etc.).
There is a possibility that materials may exist which could not be reasonably identified within the scope
of this assessment, or which were not apparent during previous site visits.
In addition, some of the 11 designated substances are not usually found in construction materials, or
buildings of this type. They are typically part of an industrial process not applicable to this survey.
1.3
THE SUBJECT FACILITY
The subject facility is a two storey educational institution located at 1250 Agincourt Road, in Ottawa,
Ontario. The school is approximately 53,261ft2 and was constructed in five phases. The first phase
constructed in 1958 runs parallel to Agincourt Road, and the 1959 phase connects at the north elevation
and extends northward. The 1962 wing connected to the 1958 phase at its south elevation and extends
westward. In addition to the library was built in 1973, while an addition to the gymnasium was
completed in 1989.
The exterior façade is brick construction. The core of the building is reinforced concrete with a
corrugated metal deck over open web steel joists. A crawlspace area is located beneath the entire
school footprint.
The building is heated via a hot water pipe loop system with perimeter radiators. The water is heated
via gas fired boilers located in the main floor Mechanical Room.
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
PART 2 - DESIGNATED SUBSTANCES
2.0
ASBESTOS
Asbestos is a generic term describing a number of naturally occurring fibrous metamorphic minerals of
the hydrous magnesium silicate variety that differ in chemical composition and are suitable for use as
non-combustible, non-conducting and chemically resistant materials. The different types of asbestos
which may be found in building materials are Chrysotile, Amosite, Tremolite, Actinolite or Anthrophylite.
They belong to two major mineral groups; Serpentines and Amphiboles. Serpentine minerals are flexible
and curly whereas amphibole fibres tend be straight with a fine fibre density that increases the
likelihood of becoming and remaining airborne when disturbed. Chrysotile is a Serpentine and Amosite,
Crocidolite, Tremolite, Actinolite, and Anthrophylite are Amphiboles.
The physical characteristics and chemical properties of asbestos made it very useful for a wide variety of
products to strengthen them, provide heat or electrical insulation, offer fire or chemical resistance,
and/or to absorb sound.
In Ontario, any building material containing 0.5% or more asbestos (by weight) is recognized as an
asbestos containing material (ACM).
ACMs are categorized as friable or non-friable in order to show how easily they may release asbestos
fibres when disturbed.
A material that is friable is one which can be crumbled, pulverized or powdered by hand pressure. If a
friable ACM is damaged or disturbed, it presents an inhalation risk because asbestos fibres are more
easily released into the air. Examples of friable materials include sprayed fireproofing on structural
steelwork, thermal insulation on mechanical systems, or textured finishes.
A non-friable asbestos product is one in which the asbestos fibres are bound or locked into the product
matrix, so that the fibres are not readily released. Such a product would present a risk for fibre release
only when it is subject to significant abrasion through activities such as sanding or cutting with electric
power tools. Examples of non-friable asbestos products include vinyl asbestos floor tiles, acoustic ceiling
tiles, and asbestos cement products.
Where suspect-ACM could not be sampled, or in order to maintain the integrity of the building
component (i.e. roofing membranes), these materials are referred to as Presumed Asbestos-Containing
Materials (PACMs). PACMs are treated as though they are ACMs until laboratory analysis proves
otherwise. Typically, PACM samples are collected and submitted for analysis on a project-by-project
basis.
2.0.1
Target Materials
Asbestos was used widely in construction materials including but not limited to:


Insulation (i.e., pipe runs, boilers, fittings, and gaskets);
Spray-on coating/fireproofing;
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012







Cement products including cement sheets and exterior shingles and fences;
Drywall joint compound filler;
Plasters and decorative interior finishes;
Acoustical ceiling tiles;
Roofing felts and shingles;
Vinyl floor tiles and sheet flooring; and
Mastics, tars, glues, and caulking.
In order to fully assess the potential presence/absence for the above materials CM3 personnel employ a
methodical room-by-room field procedure. This procedure requires the inspector to observe and note
the following building components:







2.0.2
Floor
Wall
Ceiling
Structure
Mechanical/Electrical
Other
Exterior
Analytical Procedure
Suspect materials were primarily assessed by visual inspection. Based on this inspection, select samples
were collected from discrete locations using industry-accepted, safe sampling techniques that include
the pre-wetting of materials and concealment of materials after collection.
The number of samples collected is based on the amount of suspect building materials present and the
sampling criteria outlined in Table 1 “Bulk Materials Samples” of Ontario Regulation 278/05.
All samples were submitted to Steve Moody Micro Services, LLC for analysis. Samples were analyzed by
polarized light microscopy with dispersion staining, following USEPA method 600/R-93/116. Steve
Moody Micro Services, LLC. participates in the National Voluntary Laboratory Accreditation Program
(NVLAP # 102056-0). All samples were submitted on a positive stop basis, meaning that subsequent
samples of like materials were not analyzed if the preceding sample was confirmed to contain asbestos.
The laboratory analytical reports are presented in APPENDIX B.
2.0.3
Reporting
CM3 provides all building information, methodology, laboratory results, and findings within the report.
All information respecting detailed findings, quantities, access issues, conditions, and action items are
reported.
As part of the reporting process CM3 utilizes the following criteria for evaluation of the condition of
mechanical insulation (on boilers, breaching, ductwork, piping, tanks, equipment etc.).
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
GOOD
FAIR
POOR
Insulation is completely covered in jacketing and exhibits no evidence of damage or
deterioration. No insulation is exposed. Includes conditions where the jacketing has
minor surface damage (i.e., scuffs or stains), but the jacketing is not penetrated.
Minor penetrating damage to jacketed insulation (cuts, tears, nicks, deterioration or
delamination) or undamaged insulation that has never been jacketed. Insulation is
exposed but not showing surface disintegration. The extent of missing insulation
ranges should be minor to none.
Original insulation jacket is missing, damaged, deteriorated or delaminated. Insulation
is exposed and significant areas have been dislodged. Damage cannot be readily
repaired.
The evaluation of mechanical insulation may be limited by the number of observations made and
building components such as ducts or full height walls that obstruct observations. It is not possible to
observe each foot of mechanical insulation from all angles.
The condition evaluation of all other type of ACMs may vary from the above and is described in the
findings below.
2.0.4
Drawings
CM3 has presented the overall findings, sample locations, general survey notes, and approximate
locations of ACMs on the drawings presented in APPENDIX A.
2.0.5
Findings
Suspect ACMs were collected from discrete random locations throughout the building and submitted for
analysis on a positive stop basis.
Interior Finishes
The interior wall and ceiling finishes primarily consist of various plaster finishes. In summary, no plaster
finishes were found to contain asbestos within the school. Interior finishes in each phase of
construction were sampled separately based on colour and/or texture and in accordance with Table 1 of
Ontario Regulation 278/05.
Drywall finishes are also present throughout the school, but in smaller random areas. However, the
1973 addition to the library was observed to be finished primarily with drywall. Five (5) samples of the
drywall joint compound were collected and submitted for analysis. Sample DJC-01-A was confirmed to
contain 2% chrysotile asbestos. Due to the random nature of asbestos in surfacing materials such as
drywall compound, all drywall joint compound in the 1973 library addition is considered to be ACM.
None of the remaining other drywall finishes sampled were found to contain asbestos.
Exterior Finishes
The exterior of the building is masonry brick construction. Plaster finishes were observed to at the east
exterior entrance overhang of the 1962 phase of construction. In order to maintain the integrity of
plaster finish no samples were collected, and therefore the material is presumed to be ACM until
laboratory analysis proves otherwise.
5
Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
Flooring
The interior flooring primarily consisted of vinyl floor tiles, carpet, and terrazzo. Three (3) samples of
each vinyl floor tile present within the facility were collected and submitted for analysis. The list
summarizes the visual description and location of all asbestos-containing vinyl floor tiles present in the
school:
 12” x 12” - Gold Brown (5% Chrysotile Asbestos)
 Room 111.
 9” x 9” - Brown with White Streaks (5% Chrysotile Asbestos)
 Room 109, Room 157, Room 160, Room 162, Room 164.
 9” x 9” – Grey (5% Chrysotile Asbestos)*
 Room 103.
 9” x 9” – White with Black Streaks (3% Chrysotile Asbestos)
 Room 126, Room 130.
 9” x 9” – Grey with Black Streaks (5% Chrysotile Asbestos)*
 Room 166, Room 151.
 12” x 12” – Grey with Black Streaks (5% Chrysotile Asbestos)
 Room 212, Room 222.
 9” x 9” – Dark Grey with White Streaks (5% Chrysotile Asbestos)
 Room 207, Room 209.
 9” x 9” – Grey with White Streaks (5% Chrysotile Asbestos)*
 Room 201, Room 202, Room 203, Room 205, Room 208, Room 210.
Please note: * indicates floor tile mastic also contains asbestos. Floor tile mastics were found to contain
5% chrysotile asbestos.
None of the remaining vinyl floor tiles sampled were found to contain asbestos.
Carpet and wood finishes were also present. CM3 inspected below these finishes where accessible, and
without damaging the material but access was limited. It is possible that asbestos-containing floor
finishes are present beneath ACMs or other non-asbestos applications.
Ceiling Tiles
Various styles and patterns of ceiling tiles were observed throughout the school. Three (3) samples of
each ceiling tile were collected and submitted for laboratory analysis. In summary, no ceiling tiles were
found to contain asbestos.
Where 1’ x 1’ ceiling tiles were found to be adhered to plaster or other ceiling finishes three (3) samples
of the mastic were collected and submitted for analysis. Ceiling tile mastic collected from the 1959
phase of construction (sample CTM-02-A) was confirmed to contain 2% chrysotile asbestos. Due to the
random nature of asbestos in materials such as mastic, all ceiling tile mastic present throughout the
1959 phase of construction is considered ACM. Ceiling tile mastic is present throughout the corridors,
and various classrooms in the 1959 addition. None of the remaining mastic samples was found to
contain asbestos.
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
Pipe Systems
Various pipe systems were observed. The straight pipe runs were insulated fibreglass, anti-sweat wrap
or asbestos-containing corrugated paper commonly referred to as ‘aircell’ (50% Chrysotile). Pipe fittings
(i.e. elbows, valves, joints and T-connections) were observed to be insulated with fibreglass or parging
cement. The parging cement insulation on pipe fittings is a PACM.
A large majority of asbestos containing pipe insulation was removed from the facility in 2006. All
asbestos-containing insulation was removed from the pipe systems located in the crawlspace and boiler
room.
Asbestos-containing insulation is expected to be present within the ceiling spaces, wall cavities, and
water closets. Due to the hard wall and/or ceiling finishes (with limited access panels) CM3 could not
fully assess these spaces without destructive survey techniques. Therefore, it is presumed that
asbestos-containing insulation is present within wall cavities and ceiling spaces. Specifically, pipe chases
at and between washrooms where no access is available are expected to house ACMs.
Domestic water pipes insulated with asbestos-containing aircell and parging cement insulation were
observed randomly throughout the school. The following asbestos containing insulation was observed
throughout the school:
 Room 128 – 12ft Aircell;
 Teacher’s Lounge – 12ft aircell and 3 pipe fittings;
 Principal’s Office – 15ft aircell and 4 pipe fittings; and,
 Room 209 – 2 pipe fittings.
Asbestos-containing aircell insulation in Room 128 was observed to be damaged and exposed at the
pipe end located at the floor level.
Air Handling Units and Ductwork
Air handling units (AHU) and ductwork were observed to be un-insulated or insulated with non-asbestos
applications of fiberglass.
Other Materials
In order to maintain the integrity of the roof membrane and exterior plaster finishes on overhang, no
samples were collected as part of this investigation. Therefore, at this time the roof membrane is
presumed ACM.
Similarly, no samples of the interior fire door insulation were collected. Two (2) fire resistant doors are
located in and around in the Boiler Room. At this time the fire resistant doors are presumed to contain
ACMs.
Three (3) samples of cove base moulding were collected from Room 111 and submitted for analysis.
None of the samples were found to contain asbestos; therefore there are no concerns with regards to
asbestos.
A summary listing all samples and their contents is provided as part of the analytical data in APPENDIX
B.
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
2.1
LEAD
Lead is a naturally occurring metal element and is the most common metal found in the environment.
Pure metallic lead was primarily used to make products such as electric storage batteries, ammunition,
solder, radiation shields, pipes and sheaths for electric cables. The most common organic lead
compounds are tetraethyl (TEL) and tetra methyl (TML) lead that were used as anti-knock agents in
gasoline. Inorganic lead compounds such as lead oxides, chromates, carbonates and nitrates are
commonly found in insecticides, pigments, paints, frits, glasses, plastics and rubber compounds.
A total of eleven (11) samples of paint were collected throughout the facility and submitted for analysis.
Sample ID
P-01
P-02
P-03
P-04
P-05
P-06
P-07
P-08
P-09
P-10
P-11
Table 1: Paint Analysis, Lead (Pb) Content
Description
MDL
Yellow, Wall, Room 103
5
Blue, Wall, Copier Room
5
Yellow, Wall, Room 120
5
Blue, Door, Stairwell
5
Yellow, Wall, Corridor
5
Beige, Wall, Boiler Room
5
Beige, Wall, Room 211
5
Beige, Wall, Gym Equip.
5
Room
Yellow, Wall, Room 128
5
Baby Blue, Wall, Room 210
5
Beige, Door, Gym
5
PPM (Pb)
1020
<5
6
4010
1820
1170
485
1190
2010
1770
<5
A variety of paints were observed throughout the building. The paint samples submitted for analysis
represent the overall majority of paint that exists within the facility. Paints that exist on a single door, a
cabinet, a small area, etc., may be considered lead based paint and should be tested prior to
renovations.
Lead was detected 9 of 11 paint samples submitted for analysis. Painted surfaces were observed to be
in GOOD condition at the time of the investigation.
Lead may be present in solder joints, glazing on ceramic finishes and on all copper piping throughout the
subject building.
2.2
MERCURY
Mercury may be commonly found in thermostats, fluorescent lamp tubes and High Intensity Discharge
(HID) light bulbs. Mercury vapor is assumed to be present in fluorescent lamp tubes and HID light bulbs
found throughout the facility. Mercury may also be used as a preservative in paints.
Sample ID
P-01
Table 2: Paint Analysis, Mercury (Hg) Content
Description
MDL
PPM (Hg)
Yellow, Wall, Room 103
2
<2
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
P-02
P-03
Blue, Wall, Copier Room
Yellow, Wall, Room 120
2
2
<2
<2
P-04
P-05
P-06
P-07
P-08
Blue, Door, Stairwell
Yellow, Wall, Corridor
Beige, Wall, Boiler Room
Beige, Wall, Room 211
Beige, Wall, Gym Equip.
Room
Yellow, Wall, Room 128
Baby Blue, Wall, Room 210
Beige, Door, Gym
2
2
2
2
2
<2
<2
<2
<2
<2
2
2
2
<2
<2
<2
P-09
P-10
P-11
A variety of paints were observed throughout the building. The paint samples submitted for analysis
represent the overall majority of paint that exists within the facility. Paints that exist on a single door, a
cabinet, a small area, etc., may contain a high concentration of mercury and should be tested prior to
renovations.
Mercury content in all paint samples submitted for analysis was found to be below the method
detection limit.
2.3
OZONE DEPLETING SUBSTANCES
Chlorofluorocarbons (CFCs) have been widely used in many industrial, commercial and residential
applications. They can be found in applications such as refrigerants in heat pumps, refrigerators,
freezers and air conditioners (A/C); blowing agents for plastics, foam product and insulation; cleaning
agents for metals, electronic equipment and components; and as dry-cleaning fluids.
CFCs located at the subject building include refrigerants in window/ condensing units, and refrigerators.
2.4
POLYCHLORINATED BIPHENYLS
Polychlorinated Biphenyls (PCB’s) can be found in equipment such as transformers, capacitors,
electromagnets, heat transfer unit, hydraulic engine and fluorescent lamp ballasts. The PCB Regulations
(SOR/2008-273) outlines the requirements for the storage, labeling, reporting and disposal of PCB
containing equipment. The regulation also restricts the storage of PCB containing equipment from 100
m from sensitive sites and requires that all PCB equipment is removed from service prior to December
31, 2025. There are also several government policies and guidelines that outline safe practices for the
handling and storage of PCB containing material. Fluorescent lamp ballasts may contain minor
quantities of PCBs (23.6 g).
Random suspect fluorescent lamp ballasts were inspected during the site reconnaissance and compared
to the information outlined in the 1991 Environment Canada publication “Identification of Lamp Ballasts
Containing PCBs”. No PCB containing lamp ballasts were observed in the facility, however due to the
large quantity of light fixtures in a building this size it is impractical to inspect all ballasts. Therefore, it is
possible that additional PCB-containing light ballasts do exist within the facility.
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Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
2.5
SILICA
Free crystalline silica is expected to be present within all concrete and mortar based building materials
as well as acoustic ceiling tiles.
2.6
OTHER DESIGNATED SUBSTANCES
All other designated substances are not found in most buildings, and are usually exclusive to industrial
processes. A summary of all other designated substances is provided in APPENDIX C.
10
Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
PART 3 – RECOMMENDATIONS
Prior to the undertaking of any project that may alter the building this report should be reviewed in full.
Furthermore, a targeted designated substance survey may be required to meet project specific
concerns.
Asbestos
Disturbance of friable and non-friable asbestos is regulated by Ontario Regulation 278/05.
The following materials were confirmed to contain asbestos:




Mechanical insulation on pipe straight and fittings,
Ceiling tile mastic;
Drywall joint compound; and,
Vinyl floor tiles & mastic.
The following materials are presumed to contain asbestos, and should be sampled on a project specific
basis. Samples were not collected in order to main the integrity of the building component:



Roof membrane;
Exterior plaster finish on overhang; and,
Fire resistant doors (Boiler Room).
Prior to renovation or demolition, the project owner must ensure that any ACMs that have the potential
to be disturbed are removed or enclosed. Workers conducting this activity must be adequately trained
and supplied with sufficient personal protective equipment. In addition, the maximum allowable
airborne fibre concentration for asbestos should not be approached or exceeded.
The asbestos inventory table presented in APPENDIX E thoroughly outlines the location, friability, and
action required for all asbestos containing materials observed within the facility.
The following is a list of action items for the facility.
1.
2.
Immediate repair of damage pipe insulation in Room 128.
Implement an AMP, as outlined in Ontario Regulation 278/05. Routine surveillance of all ACMs
identified should be conducted as part of the Asbestos Management Plan.
Lead
If work on lead containing materials is likely to produce lead dust or fumes, for example during welding,
torch cutting, grinding, sanding or sandblasting, then proper precautions should be followed. As best
industry practice, CM3 recommends that the ministry of Labour “Guideline for Lead on Construction
Projects” be followed when working with potential lead hazards.
The Time-Weighted Average Exposure Limits (TWAEL) of a worker to lead is to be maintained at the
lowest practical level and not exceed an eight hour average concentration of 0.05 mg/m³ of air for non
tetraethyl lead and 0.10 mg/m³ of air in the case of tetraethyl lead.
11
Agincourt Road Public School – 1250 Agincourt Rd., Ottawa, ON
Designated Substance Survey
May 2012
Mercury
If mercury (Hg) is removed or relocated, work must be completed in accordance with Ontario Regulation
490/09. Recycling of fluorescent light tubes should be performed by a contractor. If removed,
fluorescent tubes must be recycled.
The TWAEL of a worker to mercury is to be maintained at the lowest practical level and not exceed an
eight hour average concentration of 0.025 mg/m³ of air for all forms of mercury except alkyl compounds
which is 0.01 mg/m³ of air. If work on mercury containing materials is likely to produce mercury dust or
fumes, for example during welding, torch cutting, grinding, sanding or sandblasting, then proper
precautions should be followed.
Ozone Depleting Substances
Non-base building units (i.e., refrigerators, and A/C units) should be relocated or reused rather than
destroyed. If the units will not be relocated then a licensed technician should evacuate the refrigerants.
Polychlorinated Biphenyls
Prior to any renovation or demolition, all ballasts should be compared to the information outlined in the
1991 Environment Canada publication “Identification of Lamp Ballasts Containing PCBs”, and
removed/disposed of accordingly.
Silica
Silica occurs naturally as crystalline material in concrete and cement. Crystalline silica is significantly
more toxic than amorphous silica. Therefore for health reasons, only crystalline varieties are regulated
under Ontario Regulation 490/09 as one of the designated substances. Silica dust can be generated
through such processes such as blasting, grinding, crushing or sandblasting silica-containing material.
Silica is often found contained within concrete walls, stairs and ramps. Therefore, appropriate
respiratory protection and ventilation must be utilized during construction and demolition. As best
industry practice CM3 recommends that the ministry of Labour “Guideline for Silica on Construction
Projects” is followed when dealing with potential silica hazards.
12
APPENDIX A
Drawings
Designated Substance Survey Report
Agincourt Road Public School
1250 Agincourt Road, Ottawa ON
APPENDIX B
Analytical Results
Designated Substance Survey Report
Agincourt Road Public School
1250 Agincourt Road, Ottawa ON
PLM Summary Report
Steve Moody Micro Services, LLC
NVLAP Lab No. 102056
2051 Valley View Lane
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Project # :
Agincourt Road PS - OCDSB
RCP-1070
Sample Date : 04/2012
Report Date : 05/14/2012
Identification :
Asbestos, Bulk Sample Analysis
Test Method :
Polarized Light Microscopy / Dispersion Staining (PLM/DS)
EPA Method 600 / R-93 / 116
Page 1 of 8
On 5/11/2012, one hundred fifteen (115) bulk material samples were submitted by Richard Pope of CM3 Environmental Inc. - Ottawa, ON for asbestos
analysis by PLM/DS. The PLM Detail Report is attached; additional information may be found therein. The results are summarized below:
Sample Number
Client Sample Description / Location
Asbestos Content
CTM-01-A
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1958
None Detected - Brown Mastic
CTM-01-B
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1958
None Detected - Brown Mastic
CTM-01-C
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1958
None Detected - Brown Mastic
CTM-02-A
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1959
2% Chrysotile - Brown Mastic
CTM-02-B
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1959
Not Analyzed - Positive Stop
CTM-02-C
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1959
Not Analyzed - Positive Stop
CTM-03-A
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1962
None Detected - Brown Mastic
CTM-03-B
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1962
None Detected - Brown Mastic
CTM-03-C
Ceiling Tile Mastic (Brown), 1st Floor, Hallway, 1962
None Detected - Brown Mastic
CT-01-A
1' x 1' Ceiling Tile (Random Holes Pattern), 1st Floor,
Hallway, 1959
None Detected - Acoustic Tile
CT-01-B
1' x 1' Ceiling Tile (Random Holes Pattern), 1st Floor,
Hallway, 1959
None Detected - Acoustic Tile
CT-01-C
1' x 1' Ceiling Tile (Random Holes Pattern), 2nd Floor,
Hallway, 1959
None Detected - Acoustic Tile
CT-02-A
1' x 1' Ceiling Tile (Random Holes Pattern), 1st Floor,
Hallway, 1962
None Detected - Acoustic Tile
CT-02-B
1' x 1' Ceiling Tile (Random Holes Pattern), 1st Floor,
Hallway, 1962
None Detected - Acoustic Tile
CT-02-C
1' x 1' Ceiling Tile (Random Holes Pattern), 1st Floor,
Hallway, 1962
None Detected - Acoustic Tile
CT-03-A
1' x 1' Ceiling Tile (Evenly Spaced Holes Pattern), Room
111, 1958
None Detected - Acoustic Tile
CT-03-B
1' x 1' Ceiling Tile (Evenly Spaced Holes Pattern), Room
106, 1958
None Detected - Acoustic Tile
PLM Summary Report
Steve Moody Micro Services, LLC
NVLAP Lab No. 102056
2051 Valley View Lane
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Project # :
Agincourt Road PS - OCDSB
RCP-1070
Sample Date : 04/2012
Report Date : 05/14/2012
Identification :
Asbestos, Bulk Sample Analysis
Test Method :
Polarized Light Microscopy / Dispersion Staining (PLM/DS)
EPA Method 600 / R-93 / 116
Page 2 of 8
On 5/11/2012, one hundred fifteen (115) bulk material samples were submitted by Richard Pope of CM3 Environmental Inc. - Ottawa, ON for asbestos
analysis by PLM/DS. The PLM Detail Report is attached; additional information may be found therein. The results are summarized below:
Sample Number
Client Sample Description / Location
Asbestos Content
CT-03-C
1' x 1' Ceiling Tile (Evenly Spaced Holes Pattern), Room
202, 1959
None Detected - Acoustic Tile
CT-04-A
2' x 4' Ceiling Tile (Thick Parallel Fissures, Pinholes, and
Red Backing), 1st Floor, Hallway, 1958
None Detected - Acoustic Tile
CT-04-B
2' x 4' Ceiling Tile (Thick Parallel Fissures, Pinholes, and
Red Backing), 1st Floor, Hallway, 1959
None Detected - Acoustic Tile
CT-04-C
2' x 4' Ceiling Tile (Thick Parallel Fissures, Pinholes, and
Red Backing), 1st Floor, Hallway, 1962
None Detected - Acoustic Tile
CT-05-A
2' x 4' Ceiling Tile (Pinholes), Library, 1973
None Detected - Acoustic Tile
CT-05-B
2' x 4' Ceiling Tile (Pinholes), Library, 1973
None Detected - Acoustic Tile
CT-05-C
2' x 4' Ceiling Tile (Pinholes), Library, 1973
None Detected - Acoustic Tile
CT-06-A
2' x 4' Ceiling Tile (Texture with Pinholes Pattern),
Library, 1973
None Detected - Acoustic Tile
CT-06-B
2' x 4' Ceiling Tile (Texture with Pinholes Pattern),
Library, 1973
None Detected - Acoustic Tile
CT-06-C
2' x 4' Ceiling Tile (Texture with Pinholes Pattern),
Library, 1973
None Detected - Acoustic Tile
CT-07-A
2' x 4' Ceiling Tile (Perpendicular Fissures with Pinholes
Pattern), Library, 1973
None Detected - Acoustic Tile
CT-07-B
2' x 4' Ceiling Tile (Perpendicular Fissures with Pinholes
Pattern), Library, 1973
None Detected - Acoustic Tile
CT-07-C
2' x 4' Ceiling Tile (Perpendicular Fissures with Pinholes
Pattern), Library, 1973
None Detected - Acoustic Tile
PI-01-A
Aircell, Domestic Water Pipe, Room 128, under Stairs,
1958
50% Chrysotile - Thermal Insulation
PI-02-A
Anti-Sweat Wrap, Rain Water Leader, Small Gym Entrance None Detected - Paper Wrap
PI-02-B
Anti-Sweat Wrap, Rain Water Leader, Small Gym Entrance None Detected - Paper Wrap
PLM Summary Report
Steve Moody Micro Services, LLC
NVLAP Lab No. 102056
2051 Valley View Lane
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Project # :
Agincourt Road PS - OCDSB
RCP-1070
Sample Date : 04/2012
Report Date : 05/14/2012
Identification :
Asbestos, Bulk Sample Analysis
Test Method :
Polarized Light Microscopy / Dispersion Staining (PLM/DS)
EPA Method 600 / R-93 / 116
Page 3 of 8
On 5/11/2012, one hundred fifteen (115) bulk material samples were submitted by Richard Pope of CM3 Environmental Inc. - Ottawa, ON for asbestos
analysis by PLM/DS. The PLM Detail Report is attached; additional information may be found therein. The results are summarized below:
Sample Number
Client Sample Description / Location
Asbestos Content
PI-02-C
Anti-Sweat Wrap, Rain Water Leader, Small Gym Entrance None Detected - Paper Wrap
P-01-A
Plaster Finish, Gymnasium Kitchen, 1958
None Detected - Bottom Plaster
None Detected - Top Plaster
P-01-B
Plaster Finish, Gymnasium Entrance, 1958
None Detected - Bottom Plaster
None Detected - Top Plaster
P-01-C
Plaster Finish, Stage, 1958
None Detected - Bottom Plaster
None Detected - Top Plaster
P-01-D
Plaster Finish, Stage, 1958
None Detected - Bottom Plaster
None Detected - Top Plaster
P-01-E
Plaster Finish, Room 128, under Stairs, 1958
None Detected - Bottom Plaster
None Detected - Top Plaster
P-01-F
Plaster Finish, Room 211, 1958
None Detected - Bottom Plaster
None Detected - Top Plaster
P-01-G
Plaster Finish, 1st Floor, Hallway, 1958
None Detected - Bottom Plaster
None Detected - Top Plaster
P-02-A
Plaster Finish, Ceiling, Boiler Room, 1958
None Detected - Plaster
P-02-B
Plaster Finish, Ceiling, Boiler Room, 1958
None Detected - Plaster
P-02-C
Plaster Finish, Ceiling, Boiler Room, 1958
None Detected - Plaster
P-02-D
Plaster Finish, Ceiling, Boiler Room, 1958
None Detected - Plaster
P-02-E
Plaster Finish, Ceiling, Boiler Room, 1958
None Detected - Plaster
P-03-A
Plaster Finish, 1st Floor, Hallway, 1959
None Detected - Plaster
P-03-B
Plaster Finish, Room 201, 1959
None Detected - Bottom Plaster
None Detected - Top Plaster
P-03-C
Plaster Finish, Room 202, 1959
None Detected - Bottom Plaster
None Detected - Top Plaster
PLM Summary Report
Steve Moody Micro Services, LLC
NVLAP Lab No. 102056
2051 Valley View Lane
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Project # :
Agincourt Road PS - OCDSB
RCP-1070
Sample Date : 04/2012
Report Date : 05/14/2012
Identification :
Asbestos, Bulk Sample Analysis
Test Method :
Polarized Light Microscopy / Dispersion Staining (PLM/DS)
EPA Method 600 / R-93 / 116
Page 4 of 8
On 5/11/2012, one hundred fifteen (115) bulk material samples were submitted by Richard Pope of CM3 Environmental Inc. - Ottawa, ON for asbestos
analysis by PLM/DS. The PLM Detail Report is attached; additional information may be found therein. The results are summarized below:
Sample Number
Client Sample Description / Location
Asbestos Content
P-03-D
Plaster Finish, Boys' Washroom, 1959
None Detected - Bottom Plaster
None Detected - Top Plaster
P-03-E
Plaster Finish, 1st Floor, Hallway, 1959
None Detected - Bottom Plaster
None Detected - Top Plaster
P-03-F
Plaster Finish, 1st Floor, Hallway, 1959
None Detected - Bottom Plaster
None Detected - Top Plaster
P-03-G
Plaster Finish, 1st Floor, Hallway, 1959
None Detected - Bottom Plaster
None Detected - Top Plaster
P-04-A
Plaster Finish, Room 156, 1962
None Detected - Bottom Plaster
None Detected - Top Plaster
P-04-B
Plaster Finish, Room 151, 1962
None Detected - Bottom Plaster
None Detected - Top Plaster
P-04-C
Plaster Finish, Room 153, 1962
None Detected - Bottom Plaster
None Detected - Top Plaster
P-04-D
Plaster Finish, Room 154, 1962
None Detected - Bottom Plaster
None Detected - Top Plaster
P-04-E
Plaster Finish, Room 162, 1962
None Detected - Bottom Plaster
None Detected - Top Plaster
P-04-F
Plaster Finish, 1st Floor, Hallway, 1962
None Detected - Bottom Plaster
None Detected - Top Plaster
P-04-G
Plaster Finish, 1st Floor, Hallway, 1962
None Detected - Bottom Plaster
None Detected - Top Plaster
DJC-01-A
Drywall Joint Compound, Library, 1973
2% Chrysotile - Joint Compound
DJC-01-B
Drywall Joint Compound, Library, 1973
Not Analyzed - Positive Stop
DJC-01-C
Drywall Joint Compound, Library, 1973
Not Analyzed - Positive Stop
DJC-01-D
Drywall Joint Compound, Library, 1973
Not Analyzed - Positive Stop
DJC-01-E
Drywall Joint Compound, Library, 1973
Not Analyzed - Positive Stop
PLM Summary Report
Steve Moody Micro Services, LLC
NVLAP Lab No. 102056
2051 Valley View Lane
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Project # :
Agincourt Road PS - OCDSB
RCP-1070
Sample Date : 04/2012
Report Date : 05/14/2012
Identification :
Asbestos, Bulk Sample Analysis
Test Method :
Polarized Light Microscopy / Dispersion Staining (PLM/DS)
EPA Method 600 / R-93 / 116
Page 5 of 8
On 5/11/2012, one hundred fifteen (115) bulk material samples were submitted by Richard Pope of CM3 Environmental Inc. - Ottawa, ON for asbestos
analysis by PLM/DS. The PLM Detail Report is attached; additional information may be found therein. The results are summarized below:
Sample Number
Client Sample Description / Location
Asbestos Content
DJC-02-A
Drywall Joint Compound, Room 120, 1958
None Detected - Joint Compound
DJC-02-B
Drywall Joint Compound, Room 120, 1958
None Detected - Joint Compound
DJC-02-C
Drywall Joint Compound, Room 120, 1958
None Detected - Joint Compound
VFT-01-A
12" x 12" Vinyl Tile (Gold Brown), Room 111, 1958
5% Chrysotile - Floor Tile
None Detected - Black Mastic
VFT-01-B
12" x 12" Vinyl Tile (Gold Brown), Room 111, 1958
Not Analyzed - Positive Stop
VFT-01-C
12" x 12" Vinyl Tile (Gold Brown), Room 111, 1958
Not Analyzed - Positive Stop
VFT-02-A
9" x 9" Vinyl Tile (Brown with White Streaks), Room 109,
1958
VFT-02-B
9" x 9" Vinyl Tile (Brown with White Streaks), Room 162,
1962
Not Analyzed - Positive Stop
VFT-02-C
9" x 9" Vinyl Tile (Brown with White Streaks), Room 164,
1962
Not Analyzed - Positive Stop
VFT-03-A
12" x 12" Vinyl Tile (Beige Swirls), Room 108, 1958
None Detected - Floor Tile
Insufficient Mastic
VFT-03-B
12" x 12" Vinyl Tile (Beige Swirls), Room 108, 1958
None Detected - Floor Tile
Insufficient Mastic
VFT-03-C
12" x 12" Vinyl Tile (Beige Swirls), Room 108, 1958
None Detected - Floor Tile
Insufficient Mastic
VFT-04-A
9" x 9" Vinyl Tile (Grey), Room 103, 1958
5% Chrysotile - Floor Tile
5% Chrysotile - Black Mastic
VFT-04-B
9" x 9" Vinyl Tile (Grey), Room 103, 1958
Not Analyzed - Positive Stop
VFT-04-C
9" x 9" Vinyl Tile (Grey), Room 103, 1958
Not Analyzed - Positive Stop
VFT-05-A
9" x 9" Vinyl Tile (White with Black Streaks), Room 126,
1958
5% Chrysotile - Floor Tile
None Detected - Black Mastic
3% Chrysotile - Floor Tile
None Detected - Black Mastic
PLM Summary Report
Steve Moody Micro Services, LLC
NVLAP Lab No. 102056
2051 Valley View Lane
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Project # :
Agincourt Road PS - OCDSB
RCP-1070
Sample Date : 04/2012
Report Date : 05/14/2012
Identification :
Asbestos, Bulk Sample Analysis
Test Method :
Polarized Light Microscopy / Dispersion Staining (PLM/DS)
EPA Method 600 / R-93 / 116
Page 6 of 8
On 5/11/2012, one hundred fifteen (115) bulk material samples were submitted by Richard Pope of CM3 Environmental Inc. - Ottawa, ON for asbestos
analysis by PLM/DS. The PLM Detail Report is attached; additional information may be found therein. The results are summarized below:
Sample Number
Client Sample Description / Location
Asbestos Content
VFT-05-B
9" x 9" Vinyl Tile (White with Black Streaks), Room 126,
1958
Not Analyzed - Positive Stop
VFT-05-C
9" x 9" Vinyl Tile (White with Black Streaks), Room 130,
1958
Not Analyzed - Positive Stop
VFT-06-A
9" x 9" Vinyl Tile (Grey with Black Streaks), Room 166,
1962
VFT-06-B
9" x 9" Vinyl Tile (Grey with Black Streaks), Room 166,
1962
Not Analyzed - Positive Stop
VFT-06-C
9" x 9" Vinyl Tile (Grey with Black Streaks), Room 151,
1962
Not Analyzed - Positive Stop
VFT-07-A
12" x 12" Vinyl Tile (Beige Speckled), Room 224, 1958
None Detected - Floor Tile
No Mastic
VFT-07-B
12" x 12" Vinyl Tile (Beige Speckled), Room 224, 1958
None Detected - Floor Tile
No Mastic
VFT-07-C
12" x 12" Vinyl Tile (Beige Speckled), Room 224, 1958
None Detected - Floor Tile
No Mastic
VFT-08-A
12" x 12" Vinyl Tile (White with Black Flecks), Room
211, 1958
None Detected - Floor Tile
No Mastic
VFT-08-B
12" x 12" Vinyl Tile (White with Black Flecks), Room
211, 1958
None Detected - Floor Tile
No Mastic
VFT-08-C
12" x 12" Vinyl Tile (White with Black Flecks), Room
211, 1958
None Detected - Floor Tile
No Mastic
VFT-09-A
12" x 12" Vinyl Tile (Grey with Black Streaks), Room
222, 1958
5% Chrysotile - Floor Tile
None Detected - Black Mastic
VFT-09-B
12" x 12" Vinyl Tile (Grey with Black Streaks), Room
222, 1958
Not Analyzed - Positive Stop
VFT-09-C
12" x 12" Vinyl Tile (Grey with Black Streaks), Room
222, 1958
Not Analyzed - Positive Stop
5% Chrysotile - Floor Tile
5% Chrysotile - Black Mastic
PLM Summary Report
Steve Moody Micro Services, LLC
NVLAP Lab No. 102056
2051 Valley View Lane
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Project # :
Agincourt Road PS - OCDSB
RCP-1070
Sample Date : 04/2012
Report Date : 05/14/2012
Identification :
Asbestos, Bulk Sample Analysis
Test Method :
Polarized Light Microscopy / Dispersion Staining (PLM/DS)
EPA Method 600 / R-93 / 116
Page 7 of 8
On 5/11/2012, one hundred fifteen (115) bulk material samples were submitted by Richard Pope of CM3 Environmental Inc. - Ottawa, ON for asbestos
analysis by PLM/DS. The PLM Detail Report is attached; additional information may be found therein. The results are summarized below:
Sample Number
Client Sample Description / Location
Asbestos Content
VFT-10-A
9" x 9" Vinyl Tile (Dark Grey with White Streaks), Room
207, 1958
VFT-10-B
9" x 9" Vinyl Tile (Dark Grey with White Streaks), Room
209, 1958
Not Analyzed - Positive Stop
VFT-10-C
9" x 9" Vinyl Tile (Dark Grey with White Streaks), Room
209, 1958
Not Analyzed - Positive Stop
VFT-11-A
12" x 12" Vinyl Tile (Blueish Speckled), Room 101,
Library, 1959
None Detected - Floor Tile
Insufficient Mastic
VFT-11-B
12" x 12" Vinyl Tile (Blueish Speckled), Room 101,
Library, 1959
None Detected - Floor Tile
Insufficient Mastic
VFT-11-C
12" x 12" Vinyl Tile (Blueish Speckled), Room 101,
Library, 1959
None Detected - Floor Tile
Insufficient Mastic
VFT-12-A
9" x 9" Vinyl Tile (Grey with White Streaks), Room 202,
1959
5% Chrysotile - Floor Tile
5% Chrysotile - Black Mastic
VFT-12-B
9" x 9" Vinyl Tile (Grey with White Streaks), Room 210,
1958
Not Analyzed - Positive Stop
VFT-12-C
9" x 9" Vinyl Tile (Grey with White Streaks), Room 203,
1959
Not Analyzed - Positive Stop
CB-01-A
Cove Base and Mastic, Room 111, 1958
None Detected - Cove Base
None Detected - Brown Mastic
None Detected - Clear Mastic
CB-01-B
Cove Base and Mastic, Room 111, 1958
None Detected - Cove Base
None Detected - Brown Mastic
None Detected - Clear Mastic
CB-01-C
Cove Base and Mastic, Room 111, 1958
None Detected - Cove Base
None Detected - Brown Mastic
None Detected - Clear Mastic
12" x 12" Vinyl Tile (Beige Speckled), Gym Equipment
Storage, 1989
None Detected - Floor Tile
None Detected - Black Mastic
VFT-13-A
5% Chrysotile - Floor Tile
None Detected - Black Mastic
PLM Summary Report
Steve Moody Micro Services, LLC
NVLAP Lab No. 102056
2051 Valley View Lane
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Project # :
Agincourt Road PS - OCDSB
RCP-1070
Sample Date : 04/2012
Report Date : 05/14/2012
Identification :
Asbestos, Bulk Sample Analysis
Test Method :
Polarized Light Microscopy / Dispersion Staining (PLM/DS)
EPA Method 600 / R-93 / 116
Page 8 of 8
On 5/11/2012, one hundred fifteen (115) bulk material samples were submitted by Richard Pope of CM3 Environmental Inc. - Ottawa, ON for asbestos
analysis by PLM/DS. The PLM Detail Report is attached; additional information may be found therein. The results are summarized below:
Sample Number
Client Sample Description / Location
Asbestos Content
VFT-13-B
12" x 12" Vinyl Tile (Beige Speckled), Gym Equipment
Storage, 1989
None Detected - Floor Tile
None Detected - Black Mastic
VFT-13-C
12" x 12" Vinyl Tile (Beige Speckled), Gym Equipment
Storage, 1989
None Detected - Floor Tile
None Detected - Black Mastic
DJC-03-A
Drywall Joint Compound, Change Rooms, 1989
None Detected - Joint Compound
DJC-03-B
Drywall Joint Compound, Change Rooms, 1989
None Detected - Joint Compound
DJC-03-C
Drywall Joint Compound, Change Rooms, 1989
None Detected - Joint Compound
DJC-03-D
Drywall Joint Compound, Change Rooms, 1989
None Detected - Joint Compound
DJC-03-E
Drywall Joint Compound, Change Rooms, 1989
None Detected - Joint Compound
These samples were analyzed by layers. Quantification, unless otherwise noted, is performed by calibrated visual
estimate. Results may not be reproduced except in full. This test report relates only to the samples tested. These
test results do not imply endorsement by NVLAP or any agency of the U.S. Government. Accredited by the
National Voluntary Laboratory Accreditation Program for Bulk Asbestos Fiber Analysis under Lab Code 102056.
Analyst(s): Heather Deines, Jose Ortiz
Lab Manager : Bruce Crabb
Lab Director : Steve Moody
Approved Signatory :
Approved Signatory :
Thank you for choosing Steve Moody Micro Services
Steve Moody Micro Services, LLC
2051 Valley View Lane
NVLAP Lab No. 102056
PLM Detail Report
TDSHS License No. 30-0084
Supplement to PLM Summary Report
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 1 of 9
Sample Number
Layer
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
CTM-01-A
Brown Mastic (Brown)
100%
Glue Binders
100%
05/11
HD
CTM-01-B
Brown Mastic (Brown)
100%
Glue Binders
100%
05/11
HD
CTM-01-C
Brown Mastic (Brown)
100%
Glue Binders
100%
05/11
HD
CTM-02-A
Brown Mastic (Brown)
100%
Chrysotile
2%
05/11
HD
CTM-02-A
Brown Mastic (Brown)
100%
Glue Binders
98%
05/11
HD
CTM-02-B
Not Analyzed - Positive Stop
100%
05/11
HD
CTM-02-C
Not Analyzed - Positive Stop
100%
05/11
HD
CTM-03-A
Brown Mastic (Brown)
100%
Glue Binders
100%
05/11
HD
CTM-03-B
Brown Mastic (Brown)
100%
Glue Binders
100%
05/11
HD
CTM-03-C
Brown Mastic (Brown)
100%
Glue Binders
100%
05/11
HD
CT-01-A
Acoustic Tile (Off-White)
100%
Mineral Wool Fibers
95%
05/11
HD
CT-01-A
Acoustic Tile (Off-White)
100%
Binders / Fillers
5%
05/11
HD
CT-01-B
Acoustic Tile (Off-White)
100%
Mineral Wool Fibers
95%
05/11
HD
CT-01-B
Acoustic Tile (Off-White)
100%
Binders / Fillers
5%
05/11
HD
CT-01-C
Acoustic Tile (Off-White)
100%
Mineral Wool Fibers
95%
05/11
HD
CT-01-C
Acoustic Tile (Off-White)
100%
Binders / Fillers
5%
05/11
HD
CT-02-A
Acoustic Tile (Off-White)
100%
Mineral Wool Fibers
95%
05/11
HD
CT-02-A
Acoustic Tile (Off-White)
100%
Binders / Fillers
5%
05/11
HD
CT-02-B
Acoustic Tile (Off-White)
100%
Mineral Wool Fibers
95%
05/11
HD
CT-02-B
Acoustic Tile (Off-White)
100%
Binders / Fillers
5%
05/11
HD
CT-02-C
Acoustic Tile (Off-White)
100%
Mineral Wool Fibers
95%
05/11
HD
CT-02-C
Acoustic Tile (Off-White)
100%
Binders / Fillers
5%
05/11
HD
CT-03-A
Acoustic Tile (Tan)
100%
Wood Fibers
100%
05/11
HD
CT-03-B
Acoustic Tile (Tan)
100%
Wood Fibers
100%
05/11
HD
CT-03-C
Acoustic Tile (Tan)
100%
Wood Fibers
100%
05/11
HD
CT-04-A
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-04-A
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-04-A
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
Steve Moody Micro Services, LLC
2051 Valley View Lane
NVLAP Lab No. 102056
PLM Detail Report
TDSHS License No. 30-0084
Supplement to PLM Summary Report
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 2 of 9
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-04-B
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-04-B
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-04-C
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-04-C
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
28%
05/11
HD
CT-04-C
Acoustic Tile (Light Grey)
100%
Wollastonite
2%
05/11
HD
CT-04-C
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-05-A
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-05-A
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-05-A
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-05-B
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-05-B
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-05-B
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-05-C
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-05-C
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-05-C
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-06-A
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-06-A
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-06-A
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-06-B
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-06-B
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-06-B
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-06-C
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-06-C
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-06-C
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-07-A
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-07-A
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-07-A
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
Sample Number
Layer
CT-04-B
Steve Moody Micro Services, LLC
2051 Valley View Lane
NVLAP Lab No. 102056
PLM Detail Report
TDSHS License No. 30-0084
Supplement to PLM Summary Report
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 3 of 9
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-07-B
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-07-B
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
CT-07-C
Acoustic Tile (Light Grey)
100%
Cellulose Fibers
50%
05/11
HD
CT-07-C
Acoustic Tile (Light Grey)
100%
Mineral Wool Fibers
30%
05/11
HD
CT-07-C
Acoustic Tile (Light Grey)
100%
Perlite
20%
05/11
HD
PI-01-A
Thermal Insulation (Light Grey)
100%
Chrysotile
50%
05/11
HD
PI-01-A
Thermal Insulation (Light Grey)
100%
Cellulose Fibers
40%
05/11
HD
PI-01-A
Thermal Insulation (Light Grey)
100%
Binders / Fillers
10%
05/11
HD
PI-02-A
Paper Wrap (Tan)
100%
Cellulose Fibers
100%
05/11
HD
PI-02-B
Paper Wrap (Tan)
100%
Cellulose Fibers
100%
05/11
HD
PI-02-C
Paper Wrap (Tan)
100%
Cellulose Fibers
100%
05/11
HD
P-01-A
Bottom Plaster (Grey)
10%
Aggregate
65%
05/11
HD
P-01-A
Bottom Plaster (Grey)
10%
Calcite / Binders
35%
05/11
HD
P-01-A
Top Plaster (White)
90%
Calcite / Binders
100%
05/11
HD
P-01-B
Bottom Plaster (Grey)
85%
Aggregate
65%
05/11
HD
P-01-B
Bottom Plaster (Grey)
85%
Calcite / Binders
35%
05/11
HD
P-01-B
Top Plaster (White)
15%
Calcite / Binders
100%
05/11
HD
P-01-C
Bottom Plaster (Grey)
55%
Aggregate
65%
05/11
HD
P-01-C
Bottom Plaster (Grey)
55%
Calcite / Binders
35%
05/11
HD
P-01-C
Top Plaster (White)
45%
Calcite / Binders
100%
05/11
HD
P-01-D
Bottom Plaster (Grey)
80%
Aggregate
65%
05/11
HD
P-01-D
Bottom Plaster (Grey)
80%
Calcite / Binders
35%
05/11
HD
P-01-D
Top Plaster (White)
20%
Calcite / Binders
100%
05/11
HD
P-01-E
Bottom Plaster (Grey)
65%
Aggregate
65%
05/14
HD
P-01-E
Bottom Plaster (Grey)
65%
Calcite / Binders
35%
05/14
HD
P-01-E
Top Plaster (White)
35%
Calcite / Binders
100%
05/14
HD
Sample Number
Layer
CT-07-B
Steve Moody Micro Services, LLC
2051 Valley View Lane
PLM Detail Report
Supplement to PLM Summary Report
NVLAP Lab No. 102056
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 4 of 9
Sample Number
Layer
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
P-01-F
Bottom Plaster (Grey)
65%
Aggregate
65%
05/14
HD
P-01-F
Bottom Plaster (Grey)
65%
Calcite / Binders
35%
05/14
HD
P-01-F
Top Plaster (White)
35%
Calcite / Binders
100%
05/14
HD
P-01-G
Bottom Plaster (Grey)
90%
Aggregate
65%
05/14
HD
P-01-G
Bottom Plaster (Grey)
90%
Calcite / Binders
35%
05/14
HD
P-01-G
Top Plaster (White)
10%
Calcite / Binders
100%
05/14
HD
P-02-A
Plaster (Grey)
100%
Cellulose Fibers
<1%
05/14
HD
P-02-A
Plaster (Grey)
100%
Vermiculite
65%
05/14
HD
P-02-A
Plaster (Grey)
100%
Calcite / Binders
35%
05/14
HD
P-02-B
Plaster (Grey)
100%
Cellulose Fibers
<1%
05/14
HD
P-02-B
Plaster (Grey)
100%
Vermiculite
65%
05/14
HD
P-02-B
Plaster (Grey)
100%
Calcite / Binders
35%
05/14
HD
P-02-C
Plaster (Grey)
100%
Cellulose Fibers
<1%
05/14
HD
P-02-C
Plaster (Grey)
100%
Vermiculite
65%
05/14
HD
P-02-C
Plaster (Grey)
100%
Calcite / Binders
35%
05/14
HD
P-02-D
Plaster (Grey)
100%
Cellulose Fibers
<1%
05/14
HD
P-02-D
Plaster (Grey)
100%
Vermiculite
65%
05/14
HD
P-02-D
Plaster (Grey)
100%
Calcite / Binders
35%
05/14
HD
P-02-E
Plaster (Grey)
100%
Cellulose Fibers
<1%
05/14
HD
P-02-E
Plaster (Grey)
100%
Vermiculite
65%
05/14
HD
P-02-E
Plaster (Grey)
100%
Calcite / Binders
35%
05/14
HD
P-03-A
Plaster (Grey)
100%
Aggregate
65%
05/14
HD
P-03-A
Plaster (Grey)
100%
Calcite / Binders
35%
05/14
HD
P-03-B
Bottom Plaster (Grey)
80%
Cellulose Fibers
<1%
05/14
HD
P-03-B
Bottom Plaster (Grey)
80%
Vermiculite
65%
05/14
HD
P-03-B
Bottom Plaster (Grey)
80%
Calcite / Binders
35%
05/14
HD
P-03-B
Top Plaster (White)
20%
Calcite / Binders
100%
05/14
HD
Steve Moody Micro Services, LLC
2051 Valley View Lane
PLM Detail Report
Supplement to PLM Summary Report
NVLAP Lab No. 102056
TDSHS License No. 30-0084
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 5 of 9
Sample Number
Layer
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
P-03-C
Bottom Plaster (Grey)
80%
Cellulose Fibers
<1%
05/14
HD
P-03-C
Bottom Plaster (Grey)
80%
Vermiculite
65%
05/14
HD
P-03-C
Bottom Plaster (Grey)
80%
Calcite / Binders
35%
05/14
HD
P-03-C
Top Plaster (White)
20%
Calcite / Binders
100%
05/14
HD
P-03-D
Bottom Plaster (Grey)
15%
Aggregate
65%
05/14
HD
P-03-D
Bottom Plaster (Grey)
15%
Calcite / Binders
35%
05/14
HD
P-03-D
Top Plaster (White)
85%
Calcite / Binders
100%
05/14
HD
P-03-E
Bottom Plaster (Grey)
75%
Aggregate
65%
05/14
HD
P-03-E
Bottom Plaster (Grey)
75%
Calcite / Binders
35%
05/14
HD
P-03-E
Top Plaster (White)
25%
Calcite / Binders
100%
05/14
HD
P-03-F
Bottom Plaster (Grey)
50%
Aggregate
65%
05/14
HD
P-03-F
Bottom Plaster (Grey)
50%
Calcite / Binders
35%
05/14
HD
P-03-F
Top Plaster (White)
50%
Calcite / Binders
100%
05/14
HD
P-03-G
Bottom Plaster (Grey)
85%
Aggregate
65%
05/14
HD
P-03-G
Bottom Plaster (Grey)
85%
Calcite / Binders
35%
05/14
HD
P-03-G
Top Plaster (White)
15%
Calcite / Binders
100%
05/14
HD
P-04-A
Bottom Plaster (Grey)
10%
Aggregate
65%
05/14
HD
P-04-A
Bottom Plaster (Grey)
10%
Calcite / Binders
35%
05/14
HD
P-04-A
Top Plaster (White)
90%
Calcite / Binders
100%
05/14
HD
P-04-B
Bottom Plaster (Grey)
85%
Aggregate
65%
05/14
HD
P-04-B
Bottom Plaster (Grey)
85%
Calcite / Binders
35%
05/14
HD
P-04-B
Top Plaster (White)
15%
Calcite / Binders
100%
05/14
HD
P-04-C
Bottom Plaster (Grey)
85%
Aggregate
65%
05/14
HD
P-04-C
Bottom Plaster (Grey)
85%
Calcite / Binders
35%
05/14
HD
P-04-C
Top Plaster (White)
15%
Calcite / Binders
100%
05/14
HD
P-04-D
Bottom Plaster (Grey)
90%
Aggregate
65%
05/14
HD
P-04-D
Bottom Plaster (Grey)
90%
Calcite / Binders
35%
05/14
HD
P-04-D
Top Plaster (White)
10%
Calcite / Binders
100%
05/14
HD
Steve Moody Micro Services, LLC
2051 Valley View Lane
NVLAP Lab No. 102056
PLM Detail Report
TDSHS License No. 30-0084
Supplement to PLM Summary Report
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 6 of 9
Sample Number
Layer
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
P-04-E
Bottom Plaster (Grey)
90%
Aggregate
65%
05/14
HD
P-04-E
Bottom Plaster (Grey)
90%
Calcite / Binders
35%
05/14
HD
P-04-E
Top Plaster (White)
10%
Calcite / Binders
100%
05/14
HD
P-04-F
Bottom Plaster (Grey)
90%
Aggregate
65%
05/14
HD
P-04-F
Bottom Plaster (Grey)
90%
Calcite / Binders
35%
05/14
HD
P-04-F
Top Plaster (White)
10%
Calcite / Binders
100%
05/14
HD
P-04-G
Bottom Plaster (Grey)
90%
Aggregate
65%
05/14
HD
P-04-G
Bottom Plaster (Grey)
90%
Calcite / Binders
35%
05/14
HD
P-04-G
Top Plaster (White)
10%
Calcite / Binders
100%
05/14
HD
DJC-01-A
Joint Compound (White)
100%
Chrysotile
2%
05/11
JO
DJC-01-A
Joint Compound (White)
100%
Calcite / Talc / Binders
98%
05/11
JO
DJC-01-B
Not Analyzed - Positive Stop
100%
05/11
JO
DJC-01-C
Not Analyzed - Positive Stop
100%
05/11
JO
DJC-01-D
Not Analyzed - Positive Stop
100%
05/11
JO
DJC-01-E
Not Analyzed - Positive Stop
100%
05/11
JO
DJC-02-A
Joint Compound (White)
100%
Calcite / Talc / Binders
100%
05/11
JO
DJC-02-B
Joint Compound (White)
100%
Calcite / Talc / Binders
100%
05/11
JO
DJC-02-C
Joint Compound (White)
100%
Calcite / Talc / Binders
100%
05/11
JO
VFT-01-A
Floor Tile (Brown)
95%
Chrysotile
5%
05/11
JO
VFT-01-A
Floor Tile (Brown)
95%
Calcite / Vinyl Binders
95%
05/11
JO
VFT-01-A
Black Mastic (Black)
5%
Tar Binders
100%
05/11
JO
VFT-01-B
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-01-C
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-02-A
Floor Tile (Brown)
95%
Chrysotile
5%
05/11
JO
VFT-02-A
Floor Tile (Brown)
95%
Calcite / Vinyl Binders
95%
05/11
JO
VFT-02-A
Black Mastic (Black)
5%
Tar Binders
100%
05/11
JO
VFT-02-B
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-02-C
Not Analyzed - Positive Stop
100%
05/11
JO
Steve Moody Micro Services, LLC
2051 Valley View Lane
NVLAP Lab No. 102056
PLM Detail Report
TDSHS License No. 30-0084
Supplement to PLM Summary Report
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 7 of 9
Sample Number
Layer
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
100%
100%
VFT-03-A
Floor Tile (Beige)
05/11
JO
VFT-03-A
Insufficient Mastic
05/11
JO
VFT-03-B
Floor Tile (Beige)
05/11
JO
VFT-03-B
Insufficient Mastic
05/11
JO
VFT-03-C
Floor Tile (Beige)
05/11
JO
VFT-03-C
Insufficient Mastic
05/11
JO
VFT-04-A
Floor Tile (Grey)
97%
Chrysotile
5%
05/11
JO
VFT-04-A
Floor Tile (Grey)
97%
Calcite / Vinyl Binders
95%
05/11
JO
VFT-04-A
Black Mastic (Black)
3%
Chrysotile
5%
05/11
JO
VFT-04-A
Black Mastic (Black)
3%
Tar Binders
95%
05/11
JO
VFT-04-B
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-04-C
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-05-A
Floor Tile (Off-White)
95%
Chrysotile
3%
05/11
JO
VFT-05-A
Floor Tile (Off-White)
95%
Calcite / Vinyl Binders
97%
05/11
JO
VFT-05-A
Black Mastic (Black)
5%
Tar Binders
100%
05/11
JO
VFT-05-B
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-05-C
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-06-A
Floor Tile (Grey)
99%
Chrysotile
5%
05/11
JO
VFT-06-A
Floor Tile (Grey)
99%
Calcite / Vinyl Binders
95%
05/11
JO
VFT-06-A
Black Mastic (Black)
1%
Chrysotile
5%
05/11
JO
VFT-06-A
Black Mastic (Black)
1%
Tar Binders
95%
05/11
JO
VFT-06-B
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-06-C
Not Analyzed - Positive Stop
100%
05/11
JO
VFT-07-A
Floor Tile (Light Beige)
100%
05/14
JO
VFT-07-A
No Mastic
05/14
JO
VFT-07-B
Floor Tile (Light Beige)
05/14
JO
VFT-07-B
No Mastic
05/14
JO
VFT-07-C
Floor Tile (Light Beige)
05/14
JO
VFT-07-C
No Mastic
05/14
JO
100%
100%
100%
100%
Calcite / Vinyl Binders
Calcite / Vinyl Binders
Calcite / Vinyl Binders
Calcite / Vinyl Binders
Calcite / Vinyl Binders
Calcite / Vinyl Binders
100%
100%
100%
100%
100%
Steve Moody Micro Services, LLC
2051 Valley View Lane
NVLAP Lab No. 102056
PLM Detail Report
TDSHS License No. 30-0084
Supplement to PLM Summary Report
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 8 of 9
Sample Number
Layer
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
100%
100%
VFT-08-A
Floor Tile (Off-White)
05/14
JO
VFT-08-A
No Mastic
05/14
JO
VFT-08-B
Floor Tile (Off-White)
05/14
JO
VFT-08-B
No Mastic
05/14
JO
VFT-08-C
Floor Tile (Off-White)
05/14
JO
VFT-08-C
No Mastic
05/14
JO
VFT-09-A
Floor Tile (Grey)
95%
Chrysotile
5%
05/14
JO
VFT-09-A
Floor Tile (Grey)
95%
Calcite / Vinyl Binders
95%
05/14
JO
VFT-09-A
Black Mastic (Black)
5%
Tar Binders
100%
05/14
JO
VFT-09-B
Not Analyzed - Positive Stop
100%
05/14
JO
VFT-09-C
Not Analyzed - Positive Stop
100%
05/14
JO
VFT-10-A
Floor Tile (Grey)
99%
Chrysotile
5%
05/14
JO
VFT-10-A
Floor Tile (Grey)
99%
Calcite / Vinyl Binders
95%
05/14
JO
VFT-10-A
Black Mastic (Black)
1%
Tar Binders
100%
05/14
JO
VFT-10-B
Not Analyzed - Positive Stop
100%
05/14
JO
VFT-10-C
Not Analyzed - Positive Stop
100%
05/14
JO
VFT-11-A
Floor Tile (Blue)
100%
05/14
JO
VFT-11-A
Insufficient Mastic
05/14
JO
VFT-11-B
Floor Tile (Blue)
05/14
JO
VFT-11-B
Insufficient Mastic
05/14
JO
VFT-11-C
Floor Tile (Blue)
05/14
JO
VFT-11-C
Insufficient Mastic
05/14
JO
VFT-12-A
Floor Tile (Grey)
98%
Chrysotile
5%
05/14
JO
VFT-12-A
Floor Tile (Grey)
98%
Calcite / Vinyl Binders
95%
05/14
JO
VFT-12-A
Black Mastic (Black)
2%
Chrysotile
5%
05/14
JO
VFT-12-A
Black Mastic (Black)
2%
Tar Binders
95%
05/14
JO
VFT-12-B
Not Analyzed - Positive Stop
100%
05/14
JO
VFT-12-C
Not Analyzed - Positive Stop
100%
05/14
JO
100%
100%
100%
100%
Calcite / Vinyl Binders
Calcite / Vinyl Binders
Calcite / Vinyl Binders
Calcite / Vinyl Binders
Calcite / Vinyl Binders
Calcite / Vinyl Binders
100%
100%
100%
100%
100%
Steve Moody Micro Services, LLC
2051 Valley View Lane
NVLAP Lab No. 102056
PLM Detail Report
TDSHS License No. 30-0084
Supplement to PLM Summary Report
Farmers Branch, TX 75234 Phone: (972) 241-8460
Client :
CM3 Environmental Inc. - Ottawa, ON
Lab Job No. : 12B-05513
Project :
Agincourt Road PS - OCDSB
Report Date : 05/14/2012
Project # : RCP-1070
Page 9 of 9
Sample Number
Layer
% Of
Components
Sample
% of Analysis
Analyst
Layer
Date
CB-01-A
Cove Base (Black)
85%
Calcite / Vinyl Binders
100%
05/14
JO
CB-01-A
Brown Mastic (Brown)
5%
Glue Binders
100%
05/14
JO
CB-01-A
Clear Mastic (Clear)
10%
Glue Binders
100%
05/14
JO
CB-01-B
Cove Base (Black)
85%
Calcite / Vinyl Binders
100%
05/14
JO
CB-01-B
Brown Mastic (Brown)
5%
Glue Binders
100%
05/14
JO
CB-01-B
Clear Mastic (Clear)
10%
Glue Binders
100%
05/14
JO
CB-01-C
Cove Base (Black)
85%
Calcite / Vinyl Binders
100%
05/14
JO
CB-01-C
Brown Mastic (Brown)
5%
Glue Binders
100%
05/14
JO
CB-01-C
Clear Mastic (Clear)
10%
Glue Binders
100%
05/14
JO
VFT-13-A
Floor Tile (Beige)
100%
Calcite / Vinyl Binders
100%
05/14
JO
VFT-13-A
Black Mastic (Black)
<1%
Tar Binders
100%
05/14
JO
VFT-13-B
Floor Tile (Beige)
100%
Calcite / Vinyl Binders
100%
05/14
JO
VFT-13-B
Black Mastic (Black)
<1%
Tar Binders
100%
05/14
JO
VFT-13-C
Floor Tile (Beige)
98%
Calcite / Vinyl Binders
100%
05/14
JO
VFT-13-C
Black Mastic (Black)
2%
Tar Binders
100%
05/14
JO
DJC-03-A
Joint Compound (White)
100%
Calcite / Talc / Binders
100%
05/14
JO
DJC-03-B
Joint Compound (White)
100%
Calcite / Talc / Binders
100%
05/14
JO
DJC-03-C
Joint Compound (White)
100%
Calcite / Talc / Binders
100%
05/14
JO
DJC-03-D
Joint Compound (White)
100%
Calcite / Talc / Binders
100%
05/14
JO
DJC-03-E
Joint Compound (White)
100%
Calcite / Talc / Binders
100%
05/14
JO
Certificate of Analysis
CM3 Environmental Inc.
120 Robertson Road, Suite 208
Ottawa, ON K2H 5Z1
Attn: Richard Pope
Client PO:
Project: RCP-1070
Custody: 91897
Phone: (613) 820-4343
Fax: (613) 820-7695
Report Date: 15-May-2012
Order Date: 11-May-2012
Order #: 1219267
This Certificate of Analysis contains analytical data applicable to the following samples as submitted:
Paracel ID
Client ID
1219267-01
1219267-02
1219267-03
1219267-04
1219267-05
1219267-06
1219267-07
1219267-08
1219267-09
1219267-10
1219267-11
P-01 Yellow Paint, Wall Rm 103
P-02 Blue Paint, Wall, Copier Rm
P-03 Yellow Paint, Wall, Rm 120
P-04 Blue Paint, Door, Stairwell
P-05 Yellow Paint, Wall, Corridor (1962)
P-06 Beige Paint, Wall, Boiler Rm
P-07 Beige Paint, Wall, Rm 211
P-08 Beige Paint, Wall, Gym Equip. Rm
P-09 Yellow Paint, Wall, Rm 128
P-10 Baby Blue Paint, Wall, Rm 210
P-11 Beige Paint, Door, Gym (1989)
Approved By:
Mark Foto, M.Sc. For Dale Robertson, BSc
Laboratory Director
Any use of these results implies your agreement that our total liabilty in connection with this work, however arising shall be limited to the amount paid by you
for this work, and that our employees or agents shall not under circumstances be liable to you in connection with this work
Page 1 of 7
Order #: 1219267
Report Date: 15-May-2012
Order Date:11-May-2012
Certificate of Analysis
Client: CM3 Environmental Inc.
Client PO:
Project Description: RCP-1070
Analysis Summary Table
Analysis
Mercury
Metals
Method Reference/Description
EPA 7471A - CVAA, digestion
EPA 6020 - Digestion, ICP-MS
Extraction Date Analysis Date
14-May-12
14-May-12
14-May-12
14-May-12
Page 2 of 7
Order #: 1219267
Report Date: 15-May-2012
Order Date:11-May-2012
Certificate of Analysis
Client: CM3 Environmental Inc.
Client PO:
Project Description: RCP-1070
Client ID:
Sample Date:
Sample ID:
MDL/Units
P-01 Yellow Paint,
Wall Rm 103
25-Apr-12
1219267-01
Paint
P-02 Blue Paint,
Wall, Copier Rm
25-Apr-12
1219267-02
Paint
P-03 Yellow Paint,
Wall, Rm 120
25-Apr-12
1219267-03
Paint
P-04 Blue Paint,
Door, Stairwell
25-Apr-12
1219267-04
Paint
Metals
Lead
5 ug/g
1020
<5
6
4010
Mercury
2 ug/g
<2
<2
<2
<2
P-06 Beige Paint,
Wall, Boiler Rm
P-07 Beige Paint,
Wall, Rm 211
25-Apr-12
1219267-05
Paint
25-Apr-12
1219267-06
Paint
25-Apr-12
1219267-07
Paint
P-08 Beige Paint,
Wall, Gym Equip.
Rm
25-Apr-12
1219267-08
Paint
Client ID: P-05 Yellow Paint,
Wall, Corridor (1962)
Sample Date:
Sample ID:
MDL/Units
Metals
Lead
5 ug/g
1820
1170
485
1190
Mercury
2 ug/g
<2
<2
<2
<2
P-10 Baby Blue
Paint, Wall, Rm 210
25-Apr-12
1219267-10
Paint
P-11 Beige Paint,
Door, Gym (1989)
25-Apr-12
1219267-11
Paint
-
Client ID: P-09 Yellow Paint,
Wall, Rm 128
25-Apr-12
Sample Date:
1219267-09
Sample ID:
Paint
MDL/Units
Metals
Lead
5 ug/g
2010
1770
<5
-
Mercury
2 ug/g
<2
<2
<2
-
Page 3 of 7
Order #: 1219267
Report Date: 15-May-2012
Order Date:11-May-2012
Certificate of Analysis
Client: CM3 Environmental Inc.
Client PO:
Project Description: RCP-1070
Method Quality Control: Blank
Analyte
Result
Reporting
Limit
Units
ND
ND
5
2
ug/g
ug/g
Source
Result
%REC
%REC
Limit
RPD
RPD
Limit
Notes
Metals
Lead
Mercury
Page 4 of 7
Order #: 1219267
Report Date: 15-May-2012
Order Date:11-May-2012
Certificate of Analysis
Client: CM3 Environmental Inc.
Client PO:
Project Description: RCP-1070
Method Quality Control: Duplicate
Analyte
Result
Reporting
Limit
Units
Source
Result
ug/g
ug/g
33.0
ND
%REC
%REC
Limit
RPD
RPD
Limit
17.3
0.0
50
35
Notes
Metals
Lead
Mercury
27.8
2.2
5
2
Page 5 of 7
Order #: 1219267
Report Date: 15-May-2012
Order Date:11-May-2012
Certificate of Analysis
Client: CM3 Environmental Inc.
Client PO:
Project Description: RCP-1070
Method Quality Control: Spike
Analyte
Result
Reporting
Limit
Units
Source
Result
%REC
%REC
Limit
56.9
17.0
2
ug/L
ug/g
1.3
ND
111
113
70-130
70-130
RPD
RPD
Limit
Notes
Metals
Lead
Mercury
Page 6 of 7
Order #: 1219267
Report Date: 15-May-2012
Order Date:11-May-2012
Certificate of Analysis
Client: CM3 Environmental Inc.
Client PO:
Sample and QC Qualifiers Notes
Project Description: RCP-1070
None
Sample Data Revisions
None
Work Order Revisions/Comments:
None
Other Report Notes:
n/a: not applicable
MDL: Method Detection Limit
Source Result: Data used as source for matrix and duplicate samples
%REC: Percent recovery.
RPD: Relative percent difference.
Page 7 of 7
APPENDIX C
Other Designated Substances
Designated Substance Survey Report
Agincourt Road Public School
1250 Agincourt Road, Ottawa ON
The following are not typically found in most buildings and are usually exclusive to
specific industrial process:
Acrylonitrile
Acrylonitrile is used to produce polymers such as acrylonitrile-butadiene-styrene (ABS) resins.
These polymers are used in the manufacturing of a wide range of commercial products (i.e.,
automotive parts, clothing, carpets, etc.). The Time-Weighted Average Exposure Limits
(TWAEL) of a worker exposed to airborne acrylonitrile is to be maintained at the lowest practical
level and not exceed an eight hour average concentration of 4.3 mg/m³ of air (2 ppmv).
In its hardened polymer form, acrylonitrile is not expected to release emissions that would
exceed the allowable limits. Pure acrylonitrile was not identified at the subject property.
Arsenic
Arsenic can be found in paint on roofing flashings, floors, walls and on the underside of the
concrete ground floor structures in old buildings. The Time-Weighted Average Exposure Limits
(TWAEL) of a worker exposed to airborne arsenic is to be maintained at the lowest practical
level and not exceed an eight hour average concentration of 10 g/m³ of air.
Considering the age of the building, arsenic could be present in the above listed materials.
However, there is a low probability of finding arsenic-based coatings and minor amounts of this
metal did not justify that the sampling be performed in the present assessment.
Benzene
Benzene is typically found in petroleum based products such as gasoline and diesel fuels,
asphalt and other hydrocarbon based products. The Time-Weighted Average Exposure Limits
(TWAEL) of a worker exposed to airborne benzene is to be maintained at the lowest practical
level with a view to achieving an ambient air concentration lower than 3.2 mg/m³ of air (1 ppmv)
and not exceed an eight hour average concentration of 16 mg/m³ of air (5 ppmv).
Direct sources of benzene emissions were not identified at the subject property.
Coke Oven Emissions
Coke Oven Emissions result from burning of coke. The Time-Weighted Average Exposure
Limits (TWAEL) of a worker exposed to coke oven emissions are to be maintained at the lowest
practical level and not to exceed an eight hour average concentration of 0.15 mg/m³ of air.
Direct sources of coke oven emissions were not identified at the subject property.
Ethylene Oxide
Ethylene Oxide is a common by-product of fumigation or sterilization procedures. The TimeWeighted Average Exposure Limits (TWAEL) of a worker exposed to airborne ethylene oxide is
to be maintained at the lowest practical level and not exceed an eight hour average
concentration of 1.8 mg/m³ of air (1 ppmv).
Materials or processes that may release ethylene oxide to ambient air were not identified at the
subject property.
Isocyanates
Isocyanates are mainly used in the manufacture of plastics, foams and coatings. The TimeWeighted Average Exposure Limits (TWAEL) of a worker exposed is isocyanate dust is to be
maintained at the lowest practical level and not exceed an eight hour average concentration of
0.2 µmoles/m³ of air (0.005 ppmv).
Manufactured products under normal conditions do not typically pose a health risk. However,
sawing or scraping uncured polyurethane that still contains some unreacted-NCO groups will
release isocyanate dust. Uncured polyurethanes were not identified at the subject propert.
Vinyl Chloride
Vinyl Chloride is found in many applications such as PVC pipes and fittings. The Time-Weighted
Average Exposure Limits (TWAEL) of a worker exposed to vinyl chloride emission is to be
maintained at the lowest practical level and not exceed and eight hour average concentration of
5.2 mg/m³ of air (1 ppmv).
Vinyl chloride in the PVC compound is bound in a solid matrix that is unlikely to become
airborne. Vinyl chloride emissions are not likely to exceed the prescribed limits at the subject
property.
APPENDIX D
Statement of Limitations
Designated Substance Survey Report
Agincourt Road Public School
1250 Agincourt Road, Ottawa ON
This report has been prepared and the work referred to in this report has been undertaken by
CM3 Environmental Inc. for the Ottawa Carleton District School Board. It is intended for the
sole and exclusive use of the Ottawa Carleton District School Board and its authorized
agents for the purpose(s) set out in this report. Any use of, reliance on or decision made based
on this report by any person other than the Ottawa Carleton District School Board for any
purpose, or by the Ottawa Carleton District School Board for a purpose other than the
purpose(s) set out in this report, is the sole responsibility of such other person or the Ottawa
Carleton District School Board. The Ottawa Carleton District School Board and CM3
Environmental Inc. make no representation or warranty to any other person with regard to this
report and the work referred to in this report and they accept no duty of care to any other person
or any liability or responsibility whatsoever for any losses, expenses, damages, fines, penalties
or other harm that may be suffered or incurred by any other person as a result of the use of,
reliance on, any decision made or any action taken based on this report or the work referred to
in this report.
Any conclusions or recommendations made in this report reflect CM3 Environmental Inc.’s
judgment based on the following limited investigations: visual site inspection(s) on the date(s)
set out in this report; examination of public records; and interviews with individuals having
information about the site. While efforts have been made to substantiate information provided
by third parties, CM3 Environmental Inc. makes no representation or warranty as to its
completeness or accuracy.
This report has been prepared for specific application to this site. Unless otherwise stated, the
findings cannot be extended to previous or future site conditions; portions of the site which were
unavailable for direct investigation; subsurface locations which were not investigated directly; or
chemical parameters, materials or analysis which were not addressed. Substances other than
those addressed by the investigation described in this report may exist within the site; and
substances addressed by the investigation may exist in areas of the site not investigated or in
quantities not ascertained.
Nothing in this report is intended to constitute or provide a legal opinion. CM3 Environmental
Inc. makes no representation as to the requirements of or compliance with environmental laws,
rules, regulations or policies established by federal, provincial or local government
bodies. Revisions to the regulatory standards referred to in this report may be expected over
time. As a result, modifications to the findings, conclusions and recommendations in this report
may be necessary.
Other than by the Ottawa Carleton District School Board and its authorized agents and as
set out herein, copying or distribution of this report or use of or reliance on the information
contained herein, in whole or in part, is not permitted without the express written permission of
CM3 Environmental Inc.
APPENDIX E
Asbestos Inventory Summary Table
Designated Substance Survey Report
Agincourt Road Public School
1250 Agincourt Road, Ottawa ON
ASBESTOS INVENTORY TABLE
Asbestos Containing Material
Phase of
Construction
LOCATION
Access
Action
Condition
Analytical Results
Good Fair Poor
Comments
Friable or
Non-Friable
(F/NF)
Agincourt Road Public School - 1250 Agincourt Road, Ottawa, On
Principal's Office
A
4
Staff Room
A
4
1958
Room 128
A
2/3
Throughout
D
N/A
Mechanical Pipe Insulation (Aircell)
1959
Throughout
D
N/A
1962
Throughout
D
N/A
Principal's Office
A
4
Staff Room
A
4
Room 209
A
4
1958
Mechanical Pipe Insulation (Parging Cement)
Throughout
D
N/A
1959
Throughout
D
N/A
1962
Throughout
D
N/A
1973
Library
A
4
Ceiling Tile Mastic
1959
Room 102, 103, 201, 202, 203, 205, 208, 1st
Floor Corridor, 2nd Floor Corridor, and
Stairwell.
A
4
Drywall Joint Compound
50% Chrysotile
50% Chrysotile
50% Chrysotile
50% Chrysotile
50% Chrysotile
50% Chrysotile
Not Sampled, commonly found to
contain asbestos.
Not Sampled, commonly found to
contain asbestos.
Not Sampled, commonly found to
contain asbestos.
Not Sampled, commonly found to
contain asbestos.
Not Sampled, commonly found to
contain asbestos.
Not Sampled, commonly found to
contain asbestos.
2% Chrysotile
F
F
F
F
F
F
F
F
F
F
F
Routine surveillance of ACMs. Approximately, 15ft of aircell was observed in GOOD
condition.
Routine surveillance of ACMs. Approximately, 12ft of aircell was observed in GOOD
condition.
Repair or Remove damaged ACMs. Approximately, 12ft of aircell was observed. Pipe
insulation exposed and damaged.
Assumed to be present within concealed spaces, such as wall cavities and ceiling spaces.
Assumed to be present within concealed spaces, such as wall cavities and ceiling spaces.
Assumed to be present within concealed spaces, such as wall cavities and ceiling spaces.
Routine surveillance of ACMs. Approximately, 4 pipe fittings were observed in GOOD
condition.
Routine surveillance of ACMs. Approximately, 3 pipe fittings were observed in GOOD
condition.
Routine surveillance of ACMs. Approximately, 2 pipe fittings were observed in GOOD
condition.
Assumed to be present within concealed spaces, such as wall cavities and ceiling spaces.
Assumed to be present within concealed spaces, such as wall cavities and ceiling spaces.
Assumed to be present within concealed spaces, such as wall cavities and ceiling spaces.
F
NF
2% Chrysotile
Routine surveillance of ACMs.
Routine surveillance of ACMs.
NF
Vinyl Floor tile - 12" x 12" Gold Brown
1958
Room 111
A
4
5% Chrysotile
NF
Routine surveillance of ACMs.
Vinyl Floor Tile - 9” x 9” - Brown with White Streaks
1958
Room 109
A
4
5% Chrysotile
NF
Routine surveillance of ACMs.
Vinyl Floor Tile - 9” x 9” - Brown with White Streaks
1962
Room 157, 160, 162, and 164
A
4
5% Chrysotile
NF
Routine surveillance of ACMs.
1959
Room 103
A
4
Vinyl Floor Tile - 9” x 9” – Grey
Vinyl Floor Tile - 9” x 9” – White with Black Streaks
5% Chrysotile
3% Chrysotile
NF
Routine surveillance of ACMs. Note: Floor tile mastic was also confirmed to contain 5%
Chrysotile.
Routine surveillance of ACMs.
1958
Room 126, Room 130
A
4
1962
Room 151, Room 166
A
4
Vinyl Floor Tile - 12” x 12” – Grey with Black Streaks
1958
Room 212, 222
A
4
5% Chrysotile
NF
Routine surveillance of ACMs. Note: Floor tile mastic was also confirmed to contain 5%
Chrysotile.
Routine surveillance of ACMs.
Vinyl Floor Tile - 9” x 9” – Dark Grey with White Streaks
1958
Room 207, and 209
A
4
5% Chrysotile
NF
Routine surveillance of ACMs.
1959
Room 201, 202, 203, 205, 208, and 210
A
4
1962
East Entrance
A
4
Vinyl Floor Tile - 9” x 9” – Grey with Black Streaks
Vinyl Floor Tile - 9” x 9” – Grey with White Streaks
Exterior Plaster - Overhang
Fire Resistant Door
1958
Boiler Room
B
4
Roofing
1957/1968
Membrane/Felts/Mastic
B
4
5% Chrysotile
5% Chrysotile
Presumed ACM
Presumed ACM
Presumed ACM
NF
NF
NF
NF
F
NF
Routine surveillance of ACMs. Note: Floor tile mastic was also confirmed to contain 5%
Chrysotile.
Sample on a project specific basis. Approximately, 16ft2 of plaster was observed in
GOOD condtion.
Interior door insulation is presumed ACM. 2 suspect doors observed. Sample on a project
specific basis.
Core samples should be collected on a project specific basis.
ACTION 1 - Immediate Clean-Up of DEBRIS that is Likely to Be Disturbed
Restrict access that is likely to cause a disturbance of the ACM DEBRIS and clean up ACM DEBRIS
immediately. Utilize correct asbestos procedures. This action is required for compliance with regulatory
requirements. The surveyor should immediately notify the Asbestos Coordinator of this condition.
Access (A)
Areas of the building within reach (from floor level) of all building users, where activities of the building users may
result in disturbance of ACM not normally within reach from floor level.
ACTION 2 - ACM Removal Required for Compliance
Remove ACM for compliance with regulatory requirements. Utilize asbestos procedures appropriate to the
scope of the removal work.
Access (B)
Frequently entered maintenance areas within reach of maintenance staff, without the need for a ladder. Includes:
-areas within reach from a fixed ladder or catwalk, i.e., tops of equipment, mezzanines.
-frequently entered pipe chases, tunnels and service areas.
ACTION 3 - ACM Repair
Repair ACM found in FAIR condition, and not likely to be damaged again or disturbed by normal use of the area
or room. Upon completion of the repair work treat ACM as material in GOOD condition and implement ACTION
4. If ACM is likely to be damaged or disturbed, during normal use of the area or room, implement ACTION 2.
Access (C)
Areas of the building above 8'-0" where use of a ladder is required to reach the ACM. Only refers to ACM that is
exposed to view, from the floor or ladder, without the removal or opening of other building components such as
ceiling tiles, or service access door or hatch. Does not include infrequently accessed service areas of the building.
ACTION 4 - Routine Surveillance
Institute routine surveillance of the ACM. Trained workers or contractors must use appropriate asbestos
precautions (Type 1, Type 2 or Type 3) during disturbance of the remaining ACM.
Access (D)
Areas of the building behind inaccessible solid ceiling systems, walls or mechanical equipment, etc. where demolition
of the ceiling, wall or equipment, etc. is required to reach the ACM. Evaluation of condition and extent of ACM is
limited or impossible, depending on the surveyor's ability to visually examine materials in ACCESS D.
Agincourt Road Public School
Ottawa, Ontario
1
May 2012