PRE-DEMOLITION HAZARDOUS BUILDING MATERIALS SURVEY

Transcription

1 PRE-DEMOLITION HAZARDOUS BUILDING MATERIALS SURVEY Residential Property 670 Reid Street Peterborough, Ontario K9H 3R9 Presented to: The City of Peterborough 500 George Street North Peterborough, Ontario K9H 3R9 September 2013 OHE Project No.: Submitted by: Occupational Hygiene & Environment 311 Matheson Blvd. East Mississauga, Ontario L4Z 1X8 Head Office: 311 Matheson Blvd. East, Mississauga, ON, L4Z 1X8 Tel: Fax: Toll Free: OHE 4 EOH Member of the 2E Group. Offices in Peterborough, Ottawa, British Columbia, Alberta, Quebec

2 TABLE OF CONTENTS 1.0 INTRODUCTION AND REGULATORY REQUIREMENTS INTRODUCTION AND SCOPE REGULATORY REQUIREMENTS Lead Silica PCBs METHODOLOGY SURVEY METHODOLOGY METHODOLOGY FOR ASBESTOS BULK SAMPLE ANALYSIS METHODOLOGY FOR LEAD ANALYSIS METHODOLOGY FOR THE INVESTIGATION OF PCB-CONTAINING EQUIPMENT RESULTS FINDINGS ACMS Sprayed Fireproofing Material Applied Texturized Material Mechanical Systems Insulation Suspended Ceiling Tiles Plaster Materials Asbestos Cement Products Vinyl Sheet Flooring / Vinyl Floor Tiles Drywall Joint Compound Roofing Materials Other ACMs LEAD MERCURY SILICA ISOCYANATES VINYL CHLORIDE BENZENE ACRYLONITRILE COKE OVEN EMISSIONS ARSENIC ETHYLENE OXIDE PCBS DISCUSSION ACMS LEAD MERCURY SILICA RECOMMENDATIONS GENERAL STATEMENT OF LIMITATIONS APPENDIX A: Drawings APPENDIX B: Results of Sampling and Testing for: Asbestos Lead APPENDIX C: APPENDIX D: APPENDIX E: Background Information on Designated Substances Laboratory Analysis Reports Site Photographs

3 EXECUTIVE SUMMARY OHE Project No.: (OHE) was retained by the City of Peterborough, to conduct a pre-demolition hazardous building materials survey in the property located at 670 Reid Street, Peterborough, Ontario (herein referred to as the Subject Location ). The fieldwork was carried out on August 20, 2013 by Ms. Reah Hosein, Project Consultant, of OHE. The survey consisted of a review of existing environmental reports (where available), visual inspection for the presence of hazardous building materials including Designated Substances, Polychlorinated Biphenyls (PCBs) and testing and sampling of materials suspected to contain hazardous building materials, particularly asbestos, lead and PCBs. A summary of the hazardous building materials identified during the survey is presented below: Asbestos Asbestos-containing mechanical systems insulation in the form of paper insulation on ductwork was identified throughout the Subject Location. Asbestos-containing drywall joint compound was identified on the ceilings of the dining room and living room on the main floor within the Subject Location. Asbestos-containing black caulking was identified on the window frames and door frames throughout the Subject Location. Lead Lead-containing white paint was identified on the walls in the kitchen and on the walls in the patio on the main floor, on the ceilings on the second floor and on the doors, the door frames and the window frames throughout the Subject Location. Lead-containing dark-blue paint was identified on the walls in the stairwell leading to the basement within the Subject Location. Lead-containing light-yellow paint was identified on the floor and on the walls in bedroom #3 on the second floor within the Subject Location. Lead-containing green paint was identified on the door in bedroom #1 and on the walls in bedroom #3 on the second floor within the Subject Location. Lead-containing purple paint was identified on the walls in bedroom #2 on the second floor within the Subject Location. Lead-containing blue paint was identified on the walls in the bathroom on the second floor within the Subject Location. Lead-containing grey paint was identified on the walls in the patio on the main floor within the Subject Location. Lead-containing black paint was identified on the walls in the patio on the main floor and on the exterior rain leader covering within the Subject Location. Lead may be present in wiring connectors and electric cable sheathing; and Page i

4 EXECUTIVE SUMMARY OHE Project No.: Lead may be present in solder joints on copper piping. Mercury Mercury was identified in a thermostat in the hallway on the main floor within the Subject Location. Mercury is present as a vapour in fluorescent light bulbs; and, Mercury may be present as a component in electrical equipment, such as silent, position dependent switches. Silica Silica is presumed to be present in materials such as fillers for paints and mastic and in bricks, ceramics, masonry, concrete and mortar. PCBs Fluorescent light fixtures were not observed at the Subject Location. Hazardous building materials may be present in areas not accessible for view and identification. In situations where the hazardous building materials extend into a non-accessible area, the materials were assumed to also be present in those areas and have been reported as such. Contractors and maintenance personnel should be warned of the possibility of undisclosed hazardous building materials when breaking into enclosed areas or concealed wires inside the conduits. All hazardous building materials discovered in these areas should be treated as a hazardous building material until proven otherwise as per all applicable regulation and guidelines. OHE s recommendations, based on the findings of the survey, are as follows: Provide a copy of this report to contractors bidding on or performing work at the Subject Location. Remove all asbestos-containing materials that are likely to be disturbed during planned demolition. Removal of the asbestos-containing mechanical systems insulation in the form of paper insulation on ductwork will require removal operation procedures as specified in Ontario Regulation 278/05 (Type 2 or Type 2 Glovebag Operations); Removal of the asbestos-containing drywall joint compound will require removal operation procedures as specified in Ontario Regulation 278/05 (Type 2 Operation); Page ii

5 EXECUTIVE SUMMARY OHE Project No.: Removal of the asbestos-containing caulking will require removal operation procedures as specified in Ontario Regulation 278/05 (Type 1 Operation); Remove all lead-containing materials that are likely to be disturbed during planned demolition. Removal and disposal of identified lead-containing materials shall be carried out in accordance with the following requirements: o Guideline: Lead on Construction Projects (issued by Ontario Ministry of Labour); o Ontario Regulation 490/09 Designated Substances (O. Reg. 490/09); and o Ontario Regulation 213/9 Construction Projects (O. Reg. 213/91). Removal and disposal of mercury-containing equipments shall be carried out to minimize spills in accordance with applicable guidelines and regulations. Renovations and/or demolition operations that are likely to generate silica-containing dust shall be carried out in accordance with the following requirements: o Guideline: Silica on Construction Projects (issued by Ontario Ministry of Labour); o O. Reg. 490/09; and o O. Reg. 213/91. Hazardous material waste shall be transported and disposed of in accordance with all applicable guidelines and regulations. Should suspect hazardous building materials be discovered during any demolition or renovation work in the Subject Location, the contractor shall stop all work and immediately notify personnel from both the City of Peterborough and. This executive summary provides a brief overview of the survey findings. It is not intended to substitute for the complete survey report, nor does it discuss specific issues documented in the report. The executive summary should not be used as a substitute to reading the complete report. Page iii

6 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September INTRODUCTION AND REGULATORY REQUIREMENTS 1.1 Introduction and Scope (OHE) was retained by the City of Peterborough, to conduct a pre-demolition hazardous building materials survey in the residential property located at 670 Reid Street, Peterborough, Ontario (herein referred to as the Subject Location ). In accordance with Section 30 of the Ontario Occupational Health and Safety Act, Designated Substances and other potentially hazardous building materials must be identified prior to construction or demolition that may disturb such materials. The Designated Substances include: Asbestos Lead Mercury Silica Isocyanates Vinyl Chloride Benzene Acrylonitrile Coke Oven Emissions Arsenic Ethylene Oxide In addition to Designated Substances, the scope of this survey also involved the visual assessment and sampling, where applicable, for Polychlorinated Biphenyls (PCBs), which are subject to Ontario Ministry of Environment Regulations. 1.2 Regulatory Requirements Designated Substances A Designated Substances report is completed to fulfil the Owner's requirements under Section 30 of the Ontario Occupational Health and Safety Act. A copy of the report must be provided to the general contractor who in turn must submit the report to all subcontractors prior to the commencement of any demolition, construction or renovation work. There are no specific Ministry of Labour regulations for control of the other Designated Substances on construction projects. However, the Ministry of Labour actively enforces the general duty clause of the Health and Safety Act which protects workers and provides guidance on exposure monitoring, permissible exposure levels, medical monitoring, etc. for all Designated Substances in an industrial setting. Page 1

7 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September Asbestos Ontario Regulation 278/05 applies to buildings with regards to maintenance, renovations or demolition work where Asbestos-Containing Materials (ACMs) are or may be disturbed. The major requirements of the asbestos management program for the building owner include: Preparation and maintenance of a record of the location of ACMs in the building; Notification of the building's tenants of the location of such material; Establishment of a training program for those employees of the owner who may work in close proximity to and disturb the material; Periodic inspection of the material to determine its condition; Remedial action on material that has deteriorated following the precautions and procedures prescribed by the regulation as Type 1, Type 2 and Type 3; and Removal of asbestos-containing materials to the extent practicable prior to demolition of a building or part thereof. The regulation prescribes work to be conducted according to three procedure types. The procedure to be followed depends on the type of material and the regulation provides instruction on how the work must be performed. Three regulations govern the control, handling, transport and disposal of asbestos in Ontario: Ontario Regulation 278/05 Asbestos on Construction Projects and in Buildings and Repair Operations made under the Occupational Health and Safety Act (O. Reg. 278/05); Ontario Regulation 347/90 General - Waste Management (as amended) made under the Environmental Protection Act (O. Reg. 347/90); and Lead The regulations respecting the Handling and Offering for Transport and Transporting of Dangerous Goods. Guideline: Lead on Construction Projects (issued by Ontario Ministry of Labour) has been prepared to raise the awareness of employers and workers to the hazards posed by lead in construction and the measures and procedures that should be taken to control those hazards. Page 2

8 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September 2013 The document provides information on the following: Health effects associated with lead exposure; Methods for controlling the lead hazard; Classification of work; and, Measure and procedures for working with lead. The guideline classifies operations involving lead-containing materials into three groups, Type 1, Type 2 and Type 3 operations. The procedure to be followed depends on the anticipated airborne concentration of lead generated during the operation, which is dependent on the type of work performed. The guideline also provides instruction on how the work must be performed Silica Guideline: Silica on Construction Projects (issued by Ontario Ministry of Labour) has been prepared to raise the awareness of employers and workers to the hazards posed by silica in construction and the measures and procedures that should be taken to control those hazards. The document provides information on the following: Health effects associated with silica exposure; Methods for controlling the silica hazard; Classification of work; and, Measure and procedures for working with silica. The guideline classifies operations involving silica-containing materials into three groups, Type 1, Type 2 and Type 3 operations. The procedure to be followed depends on the anticipated airborne concentration of silica generated during the operation, which is dependent on the type of work performed. The guideline also provides instruction on how the work must be performed PCBs Ontario Regulation 362/90 Waste Management-PCBs made under the Environmental Protection Act (O. Reg. 362/90) controls the waste management and transfer of PCBs. Page 3

9 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September METHODOLOGY 2.1 Survey Methodology The fieldwork was conducted by Ms. Reah Hosein, Project Consultant, of OHE on August 20, Identification of materials suspected of containing hazardous substances was performed by the surveyor who, through her knowledge (from published literature and past experience), was able to identify the potential presence of such materials in buildings. The fieldwork consisted of surveying all accessible areas in order to obtain an overall representation of the hazardous materials present. OHE followed the protocols outlined in O. Reg. 278/05 for collecting and analyzing bulk samples of materials suspected to contain asbestos. Visual assessment of the material was the primary method of identification with occasional physical contact for the purpose of collecting bulk samples or examining for underlying layers. Representative bulk samples were collected of materials suspected of containing asbestos. The tools used by the investigator to collect the bulk samples were cleaned after each sample was collected to avoid cross contamination. Samples were placed in plastic sealable containers, marked with a unique sample number and transported to an independent accredited laboratory for analysis. 2.2 Methodology for Asbestos Bulk Sample Analysis Bulk samples of suspect ACMs were analysed in accordance with a US EPA method for the determination of asbestos content in bulk materials, EPA Method 600/R-93/116. The EPA Method requires that the samples be analyzed using the Polarized Light Microscopy (PLM) technique. Percentage of asbestos in the sample is measured as perceived by the analyst in comparison to standard area projections and is greatly influenced by the analyst experience. The methods are useful for the qualitative identification of asbestos (type) and the semi-quantitative (% estimates) determination of asbestos content in bulk samples. The asbestos bulk samples were analysed by EMSL Analytical Inc. (EMSL), an independent and NVLAP accredited laboratory. 2.3 Methodology for Lead Analysis Testing for lead in paint was carried out using an X-ray Fluorescence (XRF) Spectrum Analyser. Painted surfaces contain concentrations of various elements which the XRF can detect using lowlevel radioactivity. The XRF unit is positioned against the exposed painted surface and the radiation from the XRF is directed at the painted surface. The radiation is absorbed by the painted surface Page 4

10 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September 2013 and emits energy back to the analyzer as fluorescence. The level of fluorescence will be distinctive to a particular element present in the paint. Lead emissions are measured by the analyzer, and then converted into an electrical signal. The analyzer uses this electric signal to calculate and display the lead concentration in the paint surface. The low levels of radiation provide for accurate readings with the precision of ±0.05 mg/cm 2 when measuring lead concentrations. The XRF is equipped with a depth index that indicates where the lead is located within the paint layers. The detection limit of the instrument varies with depth and ranges from mg/cm 2 to 0.05 mg/cm 2. The analyzer used by OHE performs an automatic self-calibration/quality control check when the unit is switched on. 2.4 Methodology for the Investigation of PCB-Containing Equipment The investigation for PCBs usually includes a random examination of fluorescent lamp ballasts present in the building. Information collected from the labels of inspected light ballasts was cross referenced with the Environment Canada publication entitled "Identification of Lamp Ballasts Containing PCBs" (Revised August 1991). The investigation was restricted to the equipment observed and excludes PCB-containing components that may be concealed. Due to safety precautions, only the exterior of electrical equipment was inspected. If the equipment labels did not provide enough information on the contents with respect to the subject substances, the findings were noted and recommendations regarding the next course of action were provided. 3.0 RESULTS The results of the survey for asbestos and lead are presented in Appendix B. The results are presented in the form of summary tables for each of the materials. Bulk sample locations for suspect ACMs are shown on Drawings 1.1 to 1.3 presented in Appendix A. XRF spot testing locations for lead in paint are shown on Drawings 2.1 to 2.3 presented in Appendix A. Asbestos-containing friable materials are shown on Drawings 3.1 to 3.3 in Appendix A. Asbestos-containing non-friable materials are shown on Drawings 4.1and 4.2 in Appendix A. The laboratory analysis reports are presented in Appendix D. Selected site photographs are presented in Appendix E. Page 5

11 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September FINDINGS 4.1 ACMs Sprayed Fireproofing Material Sprayed fireproofing material was not observed within the Subject Location Applied Texturized Material Applied texturized material was not observed within the Subject Location Mechanical Systems Insulation Mechanical Systems Insulation (MSI) in the form of paper insulation on ductwork was observed on the ductwork throughout the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of MSI was collected as part of the survey. OHE sample A, was found to contain 70% Chrysotile asbestos. The remaining samples in the sample set were not analyzed as per O. Reg. 278/05. MSI in the form of pipe insulation was observed on a pipe in the basement at the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of MSI was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed Suspended Ceiling Tiles Suspended Ceiling Tiles (SCTs) were observed throughout the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of SCTs was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed Plaster Materials Plaster was observed throughout the Subject Location. Three (3) sample sets, consisting of seventeen (17) samples (OHE Samples A to G, A to G and A to C), of plaster were collected as part of the survey. Asbestos was not detected in the seventeen (17) samples collected and analyzed. Page 6

12 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September Asbestos Cement Products Parging cement was observed within the Subject Location. Two (2) sample sets, consisting of six (6) samples (OHE Samples A to C and A to C), of parging cement were collected as part of the survey. Asbestos was not detected in the six (6) samples collected and analyzed Vinyl Sheet Flooring / Vinyl Floor Tiles Vinyl Floor Tiles Vinyl Floor Tiles were not observed within the Subject Location. Vinyl Sheet Flooring Vinyl sheet flooring (VSF) was observed throughout the Subject Location. Five (5) sample sets, consisting of fifteen (15) samples (OHE Samples A to C, A to C, A to C, A to C and A to C), of VSF were collected as part of the survey. Asbestos was not detected in the fifteen (15) samples collected and analyzed Drywall Joint Compound Drywall Joint Compound (DJC) was observed within the Subject Location. Four (4) sample sets, consisting of twelve (12) samples (OHE Samples A to C, A to C, A to C and A to C), of DJC were collected as part of the survey. OHE sample A, was found to contain 3% Chrysotile asbestos. The remaining samples in the sample set were not analyzed as per O. Reg. 278/ Roofing Materials Roof Shingles Roof shingles were observed within the Subject Location. Two (2) sample sets, consisting of six (6) samples (OHE Samples A to C and A to C), of roof shingles were collected as part of the survey. Asbestos was not detected in the six (6) samples collected and analyzed. Page 7

13 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September Other ACMs Loose Attic Insulation Loose attic insulation was observed within the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of loose attic insulation was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed. Black Mastic Black mastic was observed below the wood flooring within the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of black mastic was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed. Yellow Mastic Yellow mastic was observed below the ceramic tiles within the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of yellow mastic was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed. Floor Levelling Compound Floor levelling compound was observed below the wood flooring within the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of floor levelling compound was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed. Wood Fibre Insulation Wood fibre insulation was observed in the ceilings within the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of wood fibre insulation was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed. Black Caulking Black caulking was observed in the Subject Location. Two (2) sample sets, consisting of six (6) samples (OHE Samples A to C and A to C), of black caulking Page 8

14 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September 2013 were collected as part of the survey. OHE sample A, was found to contain 8% Chrysotile asbestos. The remaining samples in the sample set were not analyzed as per O. Reg. 278/05 White Caulking White caulking was observed within the Subject Location.. One (1) sample set, consisting of three (3) samples (OHE Samples A to C) of white caulking was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed. Cream Caulking Cream caulking was observed within the Subject Location. One (1) sample set, consisting of three (3) samples (OHE Samples A to C), of cream caulking was collected as part of the survey. Asbestos was not detected in the three (3) samples collected and analyzed. 4.2 Lead Lead-containing white paint was identified on the walls in the kitchen and on the walls in the patio on the main floor, on the ceilings on the second floor and on the doors, the door frames and the window frames throughout the Subject Location. Lead-containing dark-blue paint was identified on the walls in the stairwell leading to the basement within the Subject Location. Lead-containing light-yellow paint was identified on the floor and on the walls in bedroom #3 on the second floor within the Subject Location. Lead-containing green paint was identified on the door in bedroom #1 and on the walls in bedroom #3 on the second floor within the Subject Location. Lead-containing purple paint was identified on the walls in bedroom #2 on the second floor within the Subject Location. Lead-containing blue paint was identified on the walls in the bathroom on the second floor within the Subject Location. Lead-containing grey paint was identified on the walls in the patio on the main floor within the Subject Location. Page 9

15 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September 2013 Lead-containing black paint was identified on the walls in the patio on the main floor and on the exterior rain leader covering within the Subject Location. Lead may be present in wiring connectors and electric cable sheathing; and Lead may be present in solder joints on copper piping. Lead is often present in ceramic building products such as floor or wall tiles. No special handling or disposal procedures are required for this material. Workers performing demolition or alterations to these tiles should be informed of the potential for lead to be present. 4.3 Mercury Mercury was identified in a thermostat in the hallway on the main floor within the Subject Location. Mercury is present as a vapour in fluorescent light bulbs and may be present as a component in electrical equipment, such as silent, position dependent switches. 4.4 Silica Silica is presumed to be present in materials such as fillers for paints and mastic and in brick, concrete and mortar. 4.5 Isocyanates The material was not identified during the site visit and is not expected to be found. 4.6 Vinyl Chloride The material was not identified during the site visit and is not expected to be found. 4.7 Benzene The material was not identified during the site visit and is not expected to be found 4.8 Acrylonitrile The material was not identified during the site visit and is not expected to be found. Page 10

16 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September Coke Oven Emissions The material was not identified during the site visit and is not expected to be found Arsenic The material was not identified during the site visit and is not expected to be found Ethylene Oxide The material was not identified during the site visit and is not expected to be found PCBs Fluorescent light fixtures were not observed at the Subject Location. 5.0 DISCUSSION 5.1 ACMs Prior to disturbance of ACMs, the materials should be removed using the appropriate type of asbestos removal operation, as per O. Reg. 278/ Lead Prior to disturbance of lead-containing materials, the material should be removed using the appropriate type of removal operation as specified in the applicable guidelines and regulations. 5.3 Mercury Prior to disturbance of mercury-containing materials, the material should be removed using the appropriate type of removal operation as specified in the applicable guidelines and regulations. Simple personal hygiene practices will be sufficient to protect workers from possible mercury exposure. 5.4 Silica Silica-containing materials should be handled using the appropriate type of operation as specified in the applicable guidelines and regulations. No adverse effects from exposure to silica are likely to Page 11

17 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September 2013 occur unless silica in the material is reduced to a respirable size and the airborne concentrations exceed the 8-hour time-weighted average. Hazardous building materials may be present in areas not accessible for view and identification. In situations where the hazardous building materials extend into a nonaccessible area, the materials were assumed to also be present in those areas and have been reported as such. Contractors and maintenance personnel should be warned of the possibility of undisclosed hazardous building materials when breaking into enclosed areas or concealed wires inside the conduits. All hazardous building materials discovered in these areas should be treated as a hazardous building material until proven otherwise as per all applicable regulation and guidelines. 6.0 RECOMMENDATIONS OHE s recommendations, based on the findings of the survey, are as follows: Provide a copy of this report to contractors bidding on or performing work at the Subject Location. Remove all ACMs that are likely to be disturbed during planned demolition. Removal of the asbestos-containing MSI in the form of paper insulation on ductwork will require removal operation procedures as specified in Ontario Regulation 278/05 (Type 2 or Type 2 Glovebag Operations); Removal of the asbestos-containing DJC will require removal operation procedures as specified in Ontario Regulation 278/05 (Type 2 Operation); Removal of the asbestos-containing caulking will require removal operation procedures as specified in Ontario Regulation 278/05 (Type 1 Operation); Remove all lead-containing materials that are likely to be disturbed during planned demolition. Removal and disposal of identified lead-containing materials shall be carried out in accordance with the following requirements: o Guideline: Lead on Construction Projects (issued by Ontario Ministry of Labour); o Ontario Regulation 490/09 Designated Substances (O. Reg. 490/09); and o Ontario Regulation 213/9 Construction Projects (O. Reg. 213/91). Page 12

18 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September 2013 Removal and disposal of mercury-containing equipments shall be carried out to minimize spills in accordance with applicable guidelines and regulations. Renovations and/or demolition operations that are likely to generate silica-containing dust shall be carried out in accordance with the following requirements: o Guideline: Silica on Construction Projects (issued by Ontario Ministry of Labour); o O. Reg. 490/09; and o O. Reg. 213/91. Hazardous material waste shall be transported and disposed of in accordance with all applicable guidelines and regulations. Should suspect hazardous building materials be discovered during any demolition or renovation work in the Subject Location, the contractor shall stop all work and immediately notify personnel from both the City of Peterborough and OHE Consultants. Page 13

19 Pre-Demolition Hazardous Building Materials Survey Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 September GENERAL STATEMENT OF LIMITATIONS The information and opinions rendered in this report are for use exclusively by the City of Peterborough. OHE reserves the right to review and comment on any interpretation of the data or conclusions derived by the City of Peterborough. No other representation, either expressed or implied, is included in this report. The survey did not consider current or past use of the property or occupant articles within the building (i.e. furniture, stock items, etc.), nor does it report on possible contaminants in the soil and groundwater of the site, vessels, drums, underground storage tanks, etc. The survey consisted of accessible areas only; samples were not collected if accessibility was restricted. The field observations and analysis are considered sufficient in detail and scope to form a reasonable basis for the findings presented in this report. OHE warrants that the findings and conclusions contained herein have been made in accordance with generally accepted evaluation methods in the industry and applicable regulations at the time of the performance of the survey. It is possible, due to the nature of building construction, that conditions may exist which could not be reasonably identified within the scope of the sampling or which were not apparent during the site investigation. OHE believes that the information collected during the sampling period concerning the property is reliable. No other warranties are implied or expressed. Dated September 2013 Occupational Hygiene & Environment Prepared by: Reah Hosein, M.Sc. Project Consultant Reviewed by: Farid (Fred) Atrash, M.H.Sc., ROH, CIH Director / Senior Consultant Reviewed by: Kelly Fernandes, M.Sc., EP, CIH Senior Technical Reviewer/Occupational Hygienist Page 14

20 APPENDIX A DRAWINGS

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32 APPENDIX B RESULTS OF SAMPLING AND TESTING FOR: Asbestos Lead

33 Table B.1 Summary of Bulk Sample Analysis Results for the Presence of Asbestos by Polarized Light Microscopy (PLM) with Dispersion Staining Collected on August 20, 2013 OHE Sample Number Sample Description Sample Location Analysis Results (% and Type of Asbestos) A Plaster Ceiling, Hallway, Main Floor B Plaster C Plaster D Plaster East Wall, Living Room, Main Floor South Wall, Dining Room, Main Floor North Wall, Bedroom #1, Main Floor E Plaster Ceiling, Hallway, Second Floor F Plaster South Wall, Bedroom #3, Second Floor G Plaster Ceiling, Basement A Plaster B Plaster C Plaster D Plaster E Plaster F Plaster South Exterior Wall, Hallway, Main Floor North Exterior Wall, Living Room, Main Floor North Exterior Wall, Dining Room, Main Floor South Exterior Wall, Bedroom #1, Second Floor North Exterior Wall, Bedroom #2, Second Floor East Exterior Wall, Washroom, Second Floor G Plaster Ceiling, Basement A Paper Insulation on Ductwork B Paper Insulation on Ductwork Wall between Living Room and Hallway, Main Floor Wall between Dining Room and Kitchen, Main Floor C Paper Insulation on Ductwork Ductwork, Basement A Black Mastic B Black Mastic C Black Mastic A Plaster B Plaster Below Wooden Flooring, Hallway, Main Floor Below Wooden Flooring, Hallway, Main Floor Below Wood Flooring, Hallway, Main Floor Above Drywall Ceiling, Living Room, Main Floor Above Drywall Ceiling, Dining Room, Main Floor 70% Chrysotile Stop Positive (Not Analyzed) Stop Positive (Not Analyzed)

34 Table B.1 (Continued) OHE Sample Number Sample Description C Plaster A Drywall Joint Compound B Drywall Joint Compound C Drywall Joint Compound A B C A B C A B C Suspended Ceiling Tile, 2 x2, white, shallow fissures and small pinholes Suspended Ceiling Tile, 2 x2, white, shallow fissures and small pinholes Suspended Ceiling Tile, 2 x2, white, shallow fissures and small pinholes Vinyl Sheet Flooring, White with Cream Squares Vinyl Sheet Flooring, White with Cream Squares Vinyl Sheet Flooring, White with Cream Squares Vinyl Sheet Flooring, Brown and Cream Patterned Squares Vinyl Sheet Flooring, Brown and Cream Patterned Squares Vinyl Sheet Flooring, Brown and Cream Patterned Squares A Drywall Joint Compound B Drywall Joint Compound C Drywall Joint Compound A Levelling Compound B Levelling Compound C Levelling Compound A Wood Fibre Insulation B Wood Fibre Insulation C Wood Fibre Insulation A B Vinyl Sheet Flooring, White with Grey Large Squares and Small Black Squares Vinyl Sheet Flooring, White with Grey Large Squares and Small Black Squares Sample Location Above Drywall Ceiling, Dining Room, Main Floor South Ceiling, Living Room, Main Floor South Ceiling, Dining Room, Main Floor East Ceiling, Living Room, Main Floor Ceiling, Kitchen, Main Floor Ceiling, Kitchen, Main Floor Ceiling, Kitchen, Main Floor North Floor, Kitchen, Main Floor North Floor, Kitchen, Main Floor West Floor, Back Sun Room, Main Floor North Floor, Kitchen, Main Floor North Floor, Kitchen, Main Floor North Floor, Kitchen, Main Floor South Wall, Back Sun Room, Main Floor North Wall, Back Sun Room, Main Floor North Wall, Back Sun Room, Main Floor Below Wood Flooring, Bedroom #1, Second Floor Below Wood Flooring, Bedroom #1, Second Floor Below Wood Flooring, Bedroom #2, Second Floor Above Plaster Ceiling, Hallway, Second Floor Above Plaster Ceiling, Hallway, Second Floor Above Plaster Ceiling, Bedroom #2, Second Floor Floor, Bathroom, Second Floor Floor, Bathroom, Second Floor Analysis Results (% and Type of Asbestos) 3% Chrysotile Stop Positive (Not Analyzed) Stop Positive (Not Analyzed)

35 Table B.1 (Continued) OHE Sample Number C A B C Sample Description Vinyl Sheet Flooring, White with Grey Large Squares and Small Black Squares Vinyl Sheet Flooring, Off- White with Small Brown Squares Vinyl Sheet Flooring, Off- White with Small Brown Squares Vinyl Sheet Flooring, Off- White with Small Brown Squares A Yellow Mastic B Yellow Mastic C Yellow Mastic Sample Location Floor, Bathroom, Second Floor Floor, Bathroom, Second Floor Floor, Bathroom, Second Floor Floor, Bathroom, Second Floor Behind Ceramic Tile, North Wall, Bathroom, Second Floor Behind Ceramic Tile, North Wall, Bathroom, Second Floor Behind Ceramic Tile, North Wall, Bathroom, Second Floor Analysis Results (% and Type of Asbestos) A Loose Attic Insulation Central Ceiling. Second Floor B Loose Attic Insulation South Ceiling. Second Floor C Loose Attic Insulation North Ceiling. Second Floor A Drywall Joint Compound South Wall, Kitchen, Main Floor B Drywall Joint Compound West Wall, Kitchen, Main Floor C Drywall Joint Compound West Wall, Kitchen, Main Floor A Parging Cement South Wall, Basement B Parging Cement West Wall, Basement C Parging Cement West Wall, Basement A Pipe Insulation Pipe, Floor Basement B Pipe Insulation Pipe, Floor Basement C Pipe Insulation Pipe, Floor Basement A Drywall Joint Compound Ceiling, Basement B Drywall Joint Compound Ceiling, Basement C Drywall Joint Compound Ceiling, Basement A Vinyl Sheet Flooring, White West Floor, Basement B Vinyl Sheet Flooring, White West Floor, Basement

36 Table B.1 (Continued) OHE Sample Number Sample Description Sample Location Analysis Results (% and Type of Asbestos) C Vinyl Sheet Flooring, White West Floor, Basement A Black Caulking B Black Caulking C Black Caulking Around Window Frame, West Exterior Wall Around Window Frame, North Exterior Wall Around Window Frame, Bedroom #1, Second Floor 8% Chrysotile Stop Positive (Not Analyzed) Stop Positive (Not Analyzed) A Parging Cement Floor, Front Patio, Main Floor B Parging Cement Floor, Front Patio, Main Floor C Parging Cement Floor, Front Patio, Main Floor A White Caulking B White Caulking C White Caulking A Cream Caulking B Cream Caulking C Cream Caulking Around Window Frame, West Exterior Wall Around Window Frame, North Exterior Wall Around Window Frame, East Exterior Wall Around Window Frame, North Exterior Wall Around Window Frame, North Exterior Wall Around Window Frame, Bedroom #1, Second Floor A Roof Shingles, Black West Roof above Patio B Roof Shingles, Black West Roof above Patio C Roof Shingles, Black West Roof above Patio A B C Roof Shingles, Black and Brown Roof Shingles, Black and Brown Roof Shingles, Black and Brown A Black Caulking B Black Caulking C Black Caulking West Roof above Patio West Roof above Patio West Roof above Patio West Wall adjacent to West Roof above Patio West Wall adjacent to West Roof above Patio West Wall adjacent to West Roof above Patio

37 Table B.2 Summary of Analysis of Lead in Paint OHE Sample Number Sample Description Sample Location Contains Lead Yes/No L1 White Paint South Wall, Hallway, Main Floor No L2 Beige Paint North Wall, Hallway, Main Floor No L3 White Paint Entrance Door, Main Floor No L4 Blue Paint North Wall, Kitchen, Main Floor No L5 White Paint Door Frame, Kitchen, Main Floor L6 Purple Paint North Wall, Dining Room, Main Floor No L7 White Paint Fibre Board, North Wall, Kitchen, Main Floor L8 White Paint West Wall, Basement, Main Floor No L9 Dark-Blue Paint 0.3 North Wall, Stairwell to Basement L10 White Paint Cabinets, Kitchen, Main Floor No L11 Light-Yellow Paint Floor, Second Floor L12 Green Paint Door, Bedroom #1, Second Floor L13 White Paint Door, Washroom, Second Floor L14 White Paint L15 Purple Paint L16 Light-Yellow Paint Door Frame, Bedroom #2, Second Floor South Wall, Bedroom #2, Second Floor North Wall, Bedroom #3, Second Floor L17 Blue Paint East Wall, Bathroom, Second Floor L18 Green Paint East Wall, Bedroom #3, Second Floor L19 White Paint Ceiling, Bedroom #1, Second Floor L20 Grey Paint Floor, Patio, Main Floor L21 White Paint Pillar, Patio, Main Floor L22 White Paint Window Frame, Patio, Main Floor L23 Black Paint West Wall, Patio, Main Floor L24 White Paint L25 Black Paint Window Frame, North Exterior Wall Exterior Wood Rain Leader Covering L26 Blue Paint North Exterior Wall, Back Sun Room No

38 Note: Classification of lead results is based on the actual XRF readings. Positive results are expressed as the actual concentration of the lead in the paint. Negative results are expressed as No and are indicative of lead concentration below the limit of detection of the XRF.

39 APPENDIX C BACKGROUND INFORMATION ON DESIGNATED SUBSTANCES

40 ASBESTOS Asbestos is a naturally occurring mineral. Asbestos is divided into two mineral groups: Serpentine and Amphibole. The division between the two types of asbestos is based upon the crystalline structure. The fibers of asbestos are long and thin, easily distinguishable when compared with non-asbestos minerals. The construction industry has been using asbestos for many years because of the ability of asbestos to withstand high temperatures as well as its strength and resistance to corrosive chemicals. When asbestos-containing material is disturbed dust is released into the air that contains asbestos fibers that have the potential to be inhaled into the lungs. Depending on the size of the individual fibers inhaled, some fibers can make their way deep into the air sacs (alveoli) of the lungs. Exposure to asbestos fibers may result in scarring of the lung tissue (asbestosis), cancer of the chest cavity (mesothelioma) or other asbestos related cancers. ACRYLONITRILE Acrylonitrile is explosive, flammable and toxic, found as a colorless or yellow clear liquid. It is used to produce a variety of products including plastics, adhesives, gaskets, seals and hoses. Health effects resulting in acute exposure to acrylonitrile vary from minor symptoms such as eye irritation, itching skin, blisters, headaches, sneezing and vomiting. Chronic exposure may cause cancers of the stomach, lymph system and brain. ARSENIC The common form of arsenic is grey in color with a metallic appearance. Arsenic has been used in the manufacturing of glass to eliminate the green color resulting from the impurities of iron compounds. It was also used in the productions of poisons. Arsenic is poisonous in doses significantly larger than 65 mg (1 grain), and poisoning can arise from a single large dose or from repeated small doses. BENZENE Benzene is an aromatic organic hydrocarbon existing either as a clear liquid or a vapour. Benzene is highly flammable and volatile material and was primarily a by-product in petroleum refineries. However, it has also been commonly used to produce styrene, synthetic rubbers, plastics, resins and solvents. Serious health effects can occur from exposure to benzene, mainly as a result of inhalation of vapours and mists. Ingestion by swallowing and absorption through the skin are also possible routes of exposure. Health effects can result from ingesting food or drink contaminated with benzene. Symptoms can range from irritated eyes, red blistering skin, headaches, nausea and drowsiness. Benzene exposure can also induce blood and bone marrow toxicity. COKE OVEN EMISSIONS Coke oven emissions can be either in a condensed form as a brownish thick liquid, or uncondensed form as a vapour. Coke oven emissions are a mixture of coal tar, coal tar pitch, and creosote and contain chemicals such as benzo(a)pyrene, benzanthracene, chrysene, and phenanthrene. Page 1

41 Chronic (long-term) exposure to coke oven emissions in humans results in conjunctivitis, severe dermatitis, and lesions of the respiratory and digestive systems. Epidemiologic studies of coke oven workers have reported an increase in cancer of the lung, trachea, bronchus, kidney, prostate, and other sites. ETHYLENE OXIDE Sources of ethylene oxide emissions into the air include uncontrolled emissions or venting with other gases in industrial settings. Other sources of ethylene oxide air emissions include automobile exhaust and its release from commodity-fumigated materials. Individuals may be exposed to ethylene oxide through breathing contaminated air or from smoking tobacco or being in the proximity to someone who is smoking. Ethylene Oxide has been linked to reproductive damage, including spontaneous abortions; cytogenetic damage; neurological effects ranging from nausea and dizziness to peripheral paralysis; and tissue irritation. ISOCYANATES Isocyanates are compounds that contain a group of atoms consisting of Nitrogen (N), Carbon (C), and Oxygen (O), which make isocyanates very useful in the manufacturing industry. Isocyanates are commonly used in the production of plastics, foams, and coatings. Health effects associated with exposure to isocyanates are: decreased lung function, cold and flu-like symptoms, fever and shortness of breath. Exposure to isocyanates can be through inhalation of vapour, mist or dust, or by direct contact. LEAD For thousands of years lead has been used industrially because of its poor conductive property. Lead has been commonly used for electric storage batteries, pigments, paints, and rubber compounds. Health effects associated with lead exposure can result in damage to the kidneys, gastrointestinal system, nervous system and reproductive system. Symptoms range from vomiting, and abdominal cramps to pains in joints and muscles. MERCURY At room temperature mercury is in the form of a silver colored liquid. Mercury can exist in three forms: elemental, the pure form; organic, where mercury is bonded to a carbon molecule; or inorganic, where mercury is bonded to a molecule other than carbon. Mercury can be absorbed into the body by inhalation, ingestion or absorption through the skin. As a health hazard mercury can affect the respiratory system resulting in coughing and chest pains. Mercury poisoning can also cause kidney damage, skin irritation and may even harm the nervous system. Page 2

42 SILICA Silica can be found naturally in two forms, crystalline or amorphous material. Crystalline silica is regulated due to its significant toxicity over the amorphous silica. The three most common forms of crystalline silica in the workplace are: quartz, cristobalite and tridymite. The physical properties of silica make it a valuable substance for use in a variety of different industries and processes such as an abrasive and scouring compound, fillers for paint and mastic and optical equipment. Health effects resulting from exposure to crystalline silica range from eye and skin irritation, coughing and sneezing to silicosis a progressive lung disease. VINYL CHLORIDE Vinyl chloride is required in the manufacture of polyvinyl chloride (PVC) and at room temperature is present as a colorless, flammable gas. Vinyl chloride is also known as chloroethene, chloroethylene, and ethylene monochloride, and can result from the breakdown of other substances such as trichloroethane, trichloroethylene, and tetrachloroethylene. Common exposure is a result of inhaling vinyl chloride from industrial leaks, hazardous waste sites and landfills. Symptoms of breathing vinyl chloride are sleepiness, dizziness or labored breathing. Chronic exposure can cause liver and nerve damage or cancer. Page 3

43 APPENDIX D LABORATORY ANALYSIS REPORT

44 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type A ceiling, hallway, main floor - plaster Gray B East wall, living room, main floor - plaster Gray/White C South wall, dining room, main floor - plaster Brown/Gray Fibrous 10% Cellulose 90% Non-fibrous (other) D North wall, bedroom #1, main floor - plaster Gray/White E ceiling, hallway, second floor - plaster Gray/White F South wall, bedroom #3, second floor - plaster Gray/White G ceiling, basement - plaster Gray A South exterior wall, hallway, main floor - plaster Gray Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 1

45 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type B North exterior wall, living room, main floor - plaster Gray C North exterior wall, dining room, main floor - plaster Gray D South exterior wall, bedroom #1, second floor - plaster Gray E North exterior wall, bedroom #2, second floor - plaster Gray F East exterior wall, washroom, second floor - plaster Gray G ceiling, basement - plaster Gray A wall between living room and hallway, main floor - paper insulation on ductwork Gray Fibrous 30% Non-fibrous (other) 70% Chrysotile Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 2

46 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type B wall between dining room and hallway, main floor - paper insulation on ductwork Stop Positive (Not Analyzed) C ductwork, basement - paper insulation on ductwork Stop Positive (Not Analyzed) A below wooden flooring, hallway, main floor - black mastic Black B below wooden flooring, hallway, main floor - black mastic Black C below wooden flooring, hallway, main floor - black mastic Black A above drywall ceiling, living room, main floor - plaster Gray/White B above drywall ceiling, dining room, main floor - plaster Gray Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 3

47 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type C above drywall ceiling, dining room, main floor - plaster Gray A South ceiling, living room, main floor - drywall joint compound Beige Fibrous 97% Non-fibrous (other) 3% Chrysotile B South ceiling, dining room, main floor - drywall joint compound Stop Positive (Not Analyzed) C East ceiling, living room, main floor - drywall joint compound Stop Positive (Not Analyzed) A ceiling, kitchen, main floor - suspended ceiling tile 2'x2', white shallow fissures and samll pinholes Gray Fibrous 40% 40% Cellulose Glass 20% Non-fibrous (other) B ceiling, kitchen, main floor - suspended ceiling tile 2'x2', white shallow fissures and samll pinholes Gray Fibrous 40% 40% Cellulose Glass 20% Non-fibrous (other) Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 4

48 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type C ceiling, kitchen, main floor - suspended ceiling tile 2'x2', white shallow fissures and samll pinholes Gray Fibrous 40% 40% Cellulose Glass 20% Non-fibrous (other) A North floor, kitchen, main floor - vinyl sheet flooring, white with cream squares Cream Fibrous 70% Cellulose 30% Non-fibrous (other) B North floor, kitchen, main floor - vinyl sheet flooring, white with cream squares Cream Fibrous 70% Cellulose 30% Non-fibrous (other) C West floor, back sun room, main floor - vinyl sheet flooring, white with cream squares Cream Fibrous 70% Cellulose 30% Non-fibrous (other) A North floor, kitchen, main floor - vinyl sheet flooring, brown and cream patterned squares Various Fibrous 50% Cellulose 50% Non-fibrous (other) Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 5

49 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type B North floor, kitchen, main floor - vinyl sheet flooring, brown and cream patterned squares Various Fibrous 50% Cellulose 50% Non-fibrous (other) C North floor, kitchen, main floor - vinyl sheet flooring, brown and cream patterned squares Various Fibrous 50% Cellulose 50% Non-fibrous (other) A South wall, back sun room, main floor - drywall joint compound White B North wall, back sun room, main floor - drywall joint compound White C North wall, back sun room, main floor - drywall joint compound White A below wood flooring, bedroom #1, second floor - leveling compound Gray Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 6

50 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type B below wood flooring, bedroom #1, second floor - leveling compound Gray C below wood flooring, bedroom #2, second floor - leveling compound Gray A above plaster ceiling, hallway, second floor - wood fibre insulation Brown B above plaster ceiling, hallway, second floor - wood fibre insulation Brown C above plaster ceiling, bedroom #2, second floor - wood fibre insulation Brown A floor, bathroom, second floor - vinyl sheet flooring, white with gray large squares and small black squares Cream Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 7

51 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type B floor, bathroom, second floor - vinyl sheet flooring, white with gray large squares and small black squares Cream C floor, bathroom, second floor - vinyl sheet flooring, white with gray large squares and small black squares Cream A floor, bathroom, second floor - vinyl sheet flooring, off white with small brown squares Beige Fibrous 40% Cellulose 60% Non-fibrous (other) B floor, bathroom, second floor - vinyl sheet flooring, off white with small brown squares Beige Fibrous 40% Cellulose 60% Non-fibrous (other) C floor, bathroom, second floor - vinyl sheet flooring, off white with small brown squares Beige Fibrous 40% Cellulose 60% Non-fibrous (other) Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 8

52 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type A behind ceramic tile, North wall, bathroom - second floor, yellow mastic Beige B behind ceramic tile, North wall, bathroom - second floor, yellow mastic Beige C behind ceramic tile, North wall, bathroom - second floor, yellow mastic Beige A central ceiling, second floor - attic insulation Brown Fibrous 70% Cellulose 30% Non-fibrous (other) B South ceiling, second floor - attic insulation Brown Fibrous 70% Cellulose 30% Non-fibrous (other) C North ceiling, second floor - attic insulation Brown Fibrous 70% Cellulose 30% Non-fibrous (other) A South wall, kitchen, main floor - drywall joint compound White B West wall, kitchen, main floor - drywall joint compound White Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 9

53 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type C West wall, kitchen, main floor - drywall joint compound White A South wall, basement - parging cement Gray B West wall, basement - parging cement Gray C West wall, basement - parging cement Gray A pipe, floor basement - pipe insulation Brown B pipe, floor basement - pipe insulation Brown C pipe, floor basement - pipe insulation Brown A ceiling, basement - drywall joint compound White Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 10

54 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type B ceiling, basement - drywall joint compound White C ceiling, basement - drywall joint compound White A West floor, basement - vinyl sheet flooring, white White B West floor, basement - vinyl sheet flooring, white White C West floor, basement - vinyl sheet flooring, white White A around window frame, West exterior wall - black caulking Black Fibrous 92% Non-fibrous (other) 8% Chrysotile B around window frame, North exterior wall - black caulking Stop Positive (Not Analyzed) Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 11

55 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type C around window frame, bedroom #1, second floor - black caulking Stop Positive (Not Analyzed) A floor, front patio, main floor - parging cement Gray B floor, front patio, main floor - parging cement Gray C floor, front patio, main floor - parging cement Gray A around window frame, West exterior wall - white caulking White B around window frame, North exterior wall - white caulking White C around window frame, East exterior wall - white caulking White Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 12

56 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type A around window frame, North exterior wall - cream caulking Beige B around window frame, North exterior wall - cream caulking Beige C around window frame, bedroom #1, second floor - cream caulking Beige A West roof above patio - roof shingles, black Black Fibrous 30% Cellulose 70% Non-fibrous (other) B West roof above patio - roof shingles, black Black Fibrous 30% Cellulose 70% Non-fibrous (other) C West roof above patio - roof shingles, black Black Fibrous 30% Cellulose 70% Non-fibrous (other) A West roof above patio - roof shingles, black and brown Black Fibrous 30% Cellulose 70% Non-fibrous (other) Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM 13

57 EMSL Analytical, Inc. 490 Rowley Road, Depew, NY Phone/Fax: (716) / (716) buffalolab@emsl.com EMSL Order: CustomerID: CustomerPO: ProjectID: OHEI93 Attn: Fred Atrash 311 Matheson Blvd. East Mississauga, ON L4Z 1X8 Phone: (905) Fax: (905) Received: 08/28/13 10:10 AM Analysis Date: 9/4/2013 Collected: 8/20/2013 Project: Test Report: Asbestos Analysis of Bulk Materials via EPA 600/R-93/116 Method using Polarized Light Microscopy Non-Asbestos Asbestos Sample Description Appearance % Fibrous % % Type B West roof above patio - roof shingles, black and brown Black Fibrous 30% Cellulose 70% Non-fibrous (other) C West roof above patio - roof shingles, black and brown Black Fibrous 30% Cellulose 70% Non-fibrous (other) A West wall adjacent to West roof above patio - black caulking Brown B West wall adjacent to West roof above patio - black caulking Brown C West wall adjacent to West roof above patio - black caulking Brown Analyst(s) Rachel Giese (86) Rhonda McGee, Laboratory Manager or other approved signatory EMSL maintains liability limited to cost of analysis. This report relates only to the samples reported and may not be reproduced, except in full, without written approval by EMSL. EMSL bears no responsibility for sample collection activities or analytical method limitations. Interpretation and use of test results are the responsibility of the client. This report must not be used by the client to claim product certification, approval, or endorsement by NVLAP, NIST or any agency of the federal government. Non-friable organically bound materials present a problem matrix and therefore EMSL recommends gravimetric reduction prior to analysis. Samples received in good condition unless otherwise noted. Estimated accuracy, precision and uncertainty data available upon request. Unless requested by the client, building materials manufactured with multiple layers (i.e. linoleum, wallboard, etc.) are reported as a single sample. Reporting limit is 1% Samples analyzed by EMSL Analytical, Inc. Depew, NY NVLAP Lab Code , NYS ELAP Initial report from 09/04/ :37:19 Test Report PLM Printed: 9/5/2013 8:58:40 AM THIS IS THE LAST PAGE OF THE REPORT. 14

58 APPENDIX E SITE PHOTOGRAPHS

59 Site Photographs Residential Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 Photograph 1: View of the Subject Location. Photograph 2: View of the asbestos-containing drywall joint compound on gypsum wallboard identified on the ceilings of the dining room and living room on the main floor at the Subject Location.

60 Site Photographs Residential Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 Photograph 3: View of the asbestos-containing MSI in the form of paper insulation on ductwork at the Subject Location. Photograph 4: View of the asbestos-containing black caulking identified on the window frames and door frames at the Subject Location.

61 Site Photographs Residential Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 Photograph 5: View of the mercury containing thermostat in the hallway on the main floor at the Subject Location. Photograph 6: View of the lead-containing white paint on the doors, door frames and window frames throughout the Subject Location.

62 Site Photographs Residential Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 Photograph 7: View of the lead-containing white paint on the walls in the kitchen of the main floor at the Subject Location. Photograph 8: View of the lead-containing blue paint on the wall in the stairwell leading to the basement at the Subject Location.

63 Site Photographs Residential Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 Photograph 9: View of the lead-containing light-yellow paint on the floor of the second floor at the Subject Location. Photograph 10: View of the lead-containing purple paint on the walls in bedroom # 2 at the Subject Location.

64 Site Photographs Residential Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 Photograph 11: View of the lead-containing white paint on the walls and pillars in the patio at the Subject Location. Photograph 12: View of the lead-containing black paint on the exterior wood rain leader covering at the Subject Location.

65 Site Photographs Residential Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 Photograph 13: View of the lead-containing green paint on a wall in bedroom #1 on the second floor at the Subject Location. Photograph 14: View of the lead-containing grey paint on the floor of the patio on the main floor at the Subject Location.

66 Site Photographs Residential Building, 670 Reid Street, Peterborough, Ontario OHE Project No.:16906 Photograph 15: View of the lead-containing black paint on the wall of the patio on the main floor at the Subject Location.