Ontario Ministry of the Environment and Climate Change - Record of Site Condition # 216034 Record of Site Condition Under Part XV.1 of the Environment Protection Act Summary Record of Site Condition Number Date Filed to Environmental Site Registry Certification Date Current Property Use Intended Property Use Certificate of Property Use Number Applicable Site Condition Standards** Property Municipal Address 216034 2015/04/23 2014/04/23 Commercial Residential No CPU Full Depth Generic Site Conditions Standard, with Potable Ground Water, Medium and Fine Textured Soil, for Residential property use 17645 YONGE STREET, NEWMARKET, ON, L3Y 5H6 Notice to Readers Concerning Due Diligence This record of site condition has been filed in the Environmental Site Registry to which the public has access and which contains a notice advising users of the Environmental Site Registry who have dealings with any property to consider conducting their own due diligence with respect to the environmental condition of the property, in addition to reviewing information in the Environmental Site Registry. Contents of this Record of Site Condition This record of site condition consists (RSC) of this document which is available to be printed directly from the Environmental Site Registry as well as all supporting documentation indicated in this RSC to have been submitted in electronic format to the Ministry of the Environment and Climate Change. Filed Record of Site Condition # 216034 on 2015/04/23 1 of 18 PART 1: PROPERTY OWNERSHIP, PROPERTY INFORMATION AND OWNER'S CERTIFICATIONS Information about the owner who is submitting or authorizing the submission of the RSC Owner Name DWIGHT SLESSOR HOLDINGS LIMITED Authorized Person ROBERT FORREST Mailing Address 590 ALDEN ROAD, MARKHAM ONTARIO, CANADA Postal Code L3R 8N2 Phone (905) 752-6776 Fax (905) 752-6781 Email Address bob@bobfor.com Filed Record of Site Condition # 216034 on 2015/04/23 2 of 18 RSC Property Location Information Municipal Address(es) 17645 YONGE STREET, NEWMARKET, ON L3Y 5H6 Municipality Newmarket Legal Description See Attached Lawyer’s Letter Assessment Roll Number(s) 1948040172230000000 Property Identifier Number(s) 03578-0942 (LT) RSC Property Geographical References Coordinate System UTM Datum NAD 83 Zone 17 Easting 621,763.00 Northing 4,879,475.00 RSC Property Use Information The following types of property uses are defined by the Regulation: Agricultural or other use, Commercial use, Community use, Industrial use, Institutional use, Parkland use, and Residential use. Current Property Use Commercial Intended Property Use Residential Certificate of Property Use has been issued under section 168.6 of the EPA No Filed Record of Site Condition # 216034 on 2015/04/23 3 of 18 Please See the Signed Statements of Property Owner, or Agent, or Receiver at the End of this RSC The rest of this page has been left intentionally blank Filed Record of Site Condition # 216034 on 2015/04/23 4 of 18 PART 2: LIST OF REPORTS, SUMMARY OF SITE CONDITIONS AND QUALIFIED PERSON’S STATEMENTS AND CERTIFICATIONS Qualified Person's Information Name RUSS PAGULAYAN Type of Licence Under Professional Engineers Act Licence Licence Number 90524018 QP Employer Name TERRAPROBE INC. Mailing Address 11 INDELL LANE, BRAMPTON ONTARIO, L6T 3Y3 CANADA Phone (905) 796-2650 Fax (905) 796-2250 Email Address rpagulayan@terraprobe.ca Municipal Information Local or Single-Tier Municipality Newmarket Upper-Tier Municipality York Ministry of the Environment and Climate Change District Office District Office York-Durham District Office District Office Address 230 Westney Rd. S., 5th floor, Ajax ON L1S 7J5 Filed Record of Site Condition # 216034 on 2015/04/23 5 of 18 Phase One Environmental Site Assessment Report Document used as the phase one environmental site assessment report and updates in submitting the RSC for filing The date the last work on all of the records review, interviews and site reconnaissance components of the phase one environmental site assessment was done (refer to clause 28(1)(a) of O. Reg. 153/04) (YYYY/MM/DD) Type of Report Name of Consulting Company Report Title Date of Report (YYYY/MM/DD) Author of Report 2014/10/02 P1 ESA Phase One Environmental Site Assessment 17645 Yonge Street newmarket, Ontario 2013/09/23 Russ Pagulayan TERRAPROBE INC. P1 ESA Update Phase One Environmental Site Assessment Update 17645 Yonge Street newmarket, Ontario 2014/10/06 Russ Pagulayan TERRAPROBE INC. Reports and Other Documents Related to the Phase One Environmental Site Assessment Reports and other documents relied upon in certifying the information set out in section 10 of Schedule A or otherwise used in conducting the phase one environmental site assessment Report Title Date of Report (YYYY/MM/DD) Author of Report Name of Consulting Company N/A Filed Record of Site Condition # 216034 on 2015/04/23 6 of 18 Phase Two Environmental Site Assessment Report Document used as the phase two environmental site assessment report and updates in submitting the RSC for filing The date the last work on all of the planning of the site investigation and conducting the site investigation components of the phase two environmental site assessment was done (refer to clause 33.5(1)(a) of O. Reg. 153/04) Type of Report Report Title Date of Report (YYYY/MM/DD) Author of Report (YYYY/MM/DD) 2014/04/23 Name of Consulting Company P2 ESA Phase Two Environmental Site Assessment 17645 Yonge Street Newmarket, Ontario 2013/09/27 Russ Pagulayan TERRAPROBE INC. P2 ESA Update Phase Two Environmental Site Assessment Update 17645 Yonge Street Newmarket, Ontario 2014/11/20 Russ Pagulayan TERRAPROBE INC. Reports and Other Documents Related to the Phase Two Environmental Site Assessment Reports and other documents relied upon in making any certifications in the RSC for the purposes of Part IV of Schedule A or otherwise used in conducting the phase two environmental site assessment Report Title Date of Report (YYYY/MM/DD) . Author of Report Name of Consulting Company N/A Filed Record of Site Condition # 216034 on 2015/04/23 7 of 18 Environmental Condition Section 41 applies? No Section 43.1 applies? No Site Condition Information Certification date (YYYY/MM/DD) 2014/04/23 Total area of RSC property (in hectares) 1.69500 Number of any previously filed RSC that applies to any part of the RSC property Number of any previously filed Transition Notice that applies to any part of the RSC property Soil Texture Medium and Fine Assessment/Restoration Approach Full Depth Generic Site investigation includes the investigation, sampling and analysis of ground water? Yes Is there soil present that is sufficient to investigate, sample and analyze soil on, in or under the property in accordance with s. 6, Schedule E of O.Reg. 153/04? Yes Site investigation includes the investigation, sampling and analysis of soil on, in or under the property which is used in the RSC? Yes Name of the laboratory used to analyze any samples collected of soil, ground water or sediment MAXXAM ANALYTICS Ground water condition (potable, non-potable) Potable Applicable Site Condition Standard TABLE 2 Filed Record of Site Condition # 216034 on 2015/04/23 8 of 18 Table 1 – Maximum Contaminant Concentrations Compared to Applicable Site Condition Standards Measured Concentration for Contaminants in Soil Contaminant Name 1 Barium 2 Beryllium 3 Boron (total) 4 Cadmium 5 Maximum Concentration Applicable Site Condition Standard Unit of Measure 390 µg/g 5 µg/g 120 µg/g 0.5 1.2 µg/g Chromium Total 15 160 µg/g 6 Cobalt 5.8 22 µg/g 7 Copper 14 180 µg/g 8 Lead 7 120 µg/g 9 Molybdenum 0.5 6.9 µg/g 10 Nickel 19 130 µg/g 11 Silver < 0.2 25 µg/g 12 Thallium < 0.4 1 µg/g 13 Uranium 0.5 23 µg/g 14 Vanadium 26 86 µg/g 15 Zinc 29 340 µg/g 16 Antimony 0.8 7.5 µg/g 17 Arsenic 3 18 µg/g 18 Selenium 0.5 2.4 µg/g 19 Boron (Hot Water Soluble)* < 0.48 1.5 µg/g 20 Chromium VI < 0.2 10 µg/g 21 Cyanide (CN-) < 0.04 0.051 µg/g 22 Electrical Conductivity 23 Mercury 24 Sodium Adsorption Ratio 25 Benzene < 0.02 0.17 µg/g 26 Ethylbenzene < 0.05 1.6 µg/g 27 Toluene < 0.05 6 µg/g 28 Xylene Mixture < 0.05 25 µg/g 29 Bromodichloromethane < 0.05 1.9 µg/g 30 Bromoform < 0.05 0.26 µg/g 31 Dibromochloromethane < 0.05 2.9 µg/g 32 Petroleum Hydrocarbons F1**** < 5 65 µg/g 33 Petroleum Hydrocarbons F2 < 10 150 µg/g 34 Petroleum Hydrocarbons F3 < 50 1300 µg/g 35 Petroleum Hydrocarbons F4 < 50 5600 µg/g 63 < 0.5 7 < < < < 0.608 0.7 mS/cm 0.1 1.8 µg/g 4.2 5 ...Continued on next page Filed Record of Site Condition # 216034 on 2015/04/23 9 of 18 Table 1 – Maximum Contaminant Concentrations Compared to Applicable Site Condition Standards Measured Concentration for Contaminants in Soil Continued from previous page.... Contaminant Name Maximum Concentration 36 Acetone < 0.5 37 Bromomethane < 38 Carbon Tetrachloride 39 Applicable Site Condition Standard Unit of Measure 28 µg/g 0.05 0.05 µg/g < 0.05 0.12 µg/g Chlorobenzene < 0.05 2.7 µg/g 40 Chloroform < 0.04 0.18 µg/g 41 Dichlorobenzene, 1,2- < 0.05 1.7 µg/g 42 Dichlorobenzene, 1,3- < 0.05 6 µg/g 43 Dichlorobenzene, 1,4- < 0.05 0.097 µg/g 44 Dichlorodifluoromethane < 0.05 25 µg/g 45 Dichloroethane, 1,1- < 0.02 0.6 µg/g 46 Dichloroethane, 1,2- < 0.03 0.05 µg/g 47 Dichloroethylene, 1,1- < 0.05 0.05 µg/g 48 Dichloroethylene, 1,2-cis- < 0.02 2.5 µg/g 49 Dichloroethylene, 1,2-trans- < 0.05 0.75 µg/g 50 Dichloropropane, 1,2- < 0.03 0.085 µg/g 51 Dichloropropene,1,3- < 0.05 0.081 µg/g 52 Ethylene dibromide < 0.04 0.05 µg/g 53 Hexane (n) < 0.05 34 µg/g 54 Methyl Ethyl Ketone < 0.5 44 µg/g 55 Methyl Isobutyl Ketone < 0.5 4.3 µg/g 56 Methyl tert-Butyl Ether (MTBE) < 0.05 1.4 µg/g 57 Methylene Chloride < 0.05 0.96 µg/g 58 Styrene < 0.05 2.2 µg/g 59 Tetrachloroethane, 1,1,1,2- < 0.04 0.05 µg/g 60 Tetrachloroethane, 1,1,2,2- < 0.05 0.05 µg/g 61 Tetrachloroethylene < 0.04 2.3 µg/g 62 Trichloroethane, 1,1,1- < 0.05 3.4 µg/g 63 Trichloroethane, 1,1,2- < 0.04 0.05 µg/g 64 Trichloroethylene < 0.03 0.52 µg/g 65 Trichlorofluoromethane < 0.05 5.8 µg/g 66 Vinyl Chloride < 0.02 0.022 µg/g Filed Record of Site Condition # 216034 on 2015/04/23 10 of 18 Table 1 – Maximum Contaminant Concentrations Compared to Applicable Site Condition Standards (Continued) Ground Water Contaminant Name Maximum Concentration Applicable Site Condition Standard Unit of Measure 1 Petroleum Hydrocarbons F1**** < 25 750 µg/L 2 Petroleum Hydrocarbons F2 < 100 150 µg/L 3 Petroleum Hydrocarbons F3 < 200 500 µg/L 4 Petroleum Hydrocarbons F4 < 200 500 µg/L 5 Acetone < 10 2700 µg/L 6 Bromomethane < 0.5 0.89 µg/L 7 Carbon Tetrachloride < 0.2 5 µg/L 8 Chlorobenzene < 0.2 30 µg/L 9 Chloroform < 0.2 22 µg/L 10 Dichlorobenzene, 1,2- < 0.5 3 µg/L 11 Dichlorobenzene, 1,3- < 0.5 59 µg/L 12 Dichlorobenzene, 1,4- < 0.5 1 µg/L 13 Dichlorodifluoromethane < 1 590 µg/L 14 Dichloroethane, 1,1- < 0.2 5 µg/L 15 Dichloroethane, 1,2- < 0.5 5 µg/L 16 Dichloroethylene, 1,1- < 0.2 14 µg/L 17 Dichloroethylene, 1,2-cis- < 0.5 17 µg/L 18 Dichloroethylene, 1,2-trans- < 0.5 17 µg/L 19 Dichloropropane, 1,2- < 0.2 5 µg/L 20 Dichloropropene,1,3- < 0.5 0.5 µg/L 21 Ethylene dibromide < 0.2 0.2 µg/L 22 Hexane (n) < 1 520 µg/L 23 Methyl Ethyl Ketone < 10 1800 µg/L 24 Methyl Isobutyl Ketone < 5 640 µg/L 25 Methyl tert-Butyl Ether (MTBE) < 0.5 15 µg/L 26 Methylene Chloride < 2 50 µg/L 27 Styrene < 0.5 5.4 µg/L 28 Tetrachloroethane, 1,1,1,2- < 0.5 1.1 µg/L 29 Tetrachloroethane, 1,1,2,2- < 0.5 1 µg/L 30 Tetrachloroethylene < 0.2 17 µg/L 31 Trichloroethane, 1,1,1- < 0.2 200 µg/L 32 Trichloroethane, 1,1,2- < 0.5 5 µg/L 33 Trichloroethylene 0.32 5 µg/L 34 Trichlorofluoromethane < 0.5 150 µg/L 35 Vinyl Chloride < 0.2 1.7 µg/L ...Continued on next page Filed Record of Site Condition # 216034 on 2015/04/23 11 of 18 Table 1 – Maximum Contaminant Concentrations Compared to Applicable Site Condition Standards (Continued) Ground Water Continued from previous page.... Contaminant Name Maximum Concentration Applicable Site Condition Standard Unit of Measure 36 Bromodichloromethane < 0.5 16 µg/L 37 Bromoform < 1 25 µg/L 38 Dibromochloromethane < 0.5 25 µg/L Filed Record of Site Condition # 216034 on 2015/04/23 12 of 18 Remedial Action and Mitigation Remediated Soils Estimated quantities of the soil, if any, originating at and remaining on the RSC property that have been remediated, at a location either on or off the property, to reduce the concentration of contaminants in the soil. Indicate the remediation process or processes used and the estimated amount of soil remediated by each identified process. Soil Remediation Process Excavation Estimated Quantity of Soil (in-ground volume in m³) 0.0 Description of Remediation Description of any action taken to reduce the concentration of contaminants (including soil removals) on, in or under the RSC property. Impacted soils were excavated and disposed of at a soil receiver with a proper CofA for the treatment of soil Soil or Sediment Removed and Not Returned Estimated quantities of soil or sediment, if any, removed from and not returned to the RSC property. Estimated Quantity of Soil (in-ground volume in m³) 2,206.0 Estimated Quantity of Sediment (in-ground volume in m³) 0.0 Soil Brought to the Property Estimated quantity of the soil, if any, being brought from another property to and deposited at the RSC property, not including any soil that may have originated at but been remediated off the RSC property and that is identified in section 28 of Schedule A. Estimated Quantity of Soil Brought to the Property (in-ground volume in m³) Filed Record of Site Condition # 216034 on 2015/04/23 0.0 13 of 18 Ground Water Control or Treatment Measures Ground water control or treatment measures that were required for the RSC property prior to the certification date for the purpose of submitting the RSC for filing. Excavation of ground water as part of the soil excavation Ground water control or treatment measures that are required for the RSC property after the certification date. None Estimated volume of ground water, if any, removed from and not returned to the RSC property. Estimated Volume of Ground Water (in litres) 500,000.0 Filed Record of Site Condition # 216034 on 2015/04/23 14 of 18 Other Activities Including Risk Management Measures Constructed works that prior to the certification date for the purpose of submitting the RSC for filing, were required to control or otherwise mitigate the release or movement of known existing contaminants at the RSC property. Constructed works that after the certification date, are required to control or otherwise mitigate the release or movement of known existing contaminants at the RSC property. Monitoring or Maintenance Soil Management Measures Soil monitoring requirements or any requirements for care, maintenance or replacement or any monitoring or control works for known existing contaminants, if any, on the RSC property, after the certification date. Ground Water Management Measures Ground water monitoring requirements or requirements for care, maintenance or replacement of any monitoring or control works or known existing contaminants, if any, on the RSC property, after the certification date. Remediated or Removed Soil, Sediment or Ground Water From Near Property Boundary Has any soil, sediment or ground water at the RSC property that is or was located within 3 metres of the RSC property boundary been remediated or removed for the purpose of remediation? Filed Record of Site Condition # 216034 on 2015/04/23 Yes 15 of 18 Qualified Person’s Statements and Certifications As the qualified person, I certify that: A phase one environmental site assessment of the RSC property, which includes the evaluation of the information gathered from a records review, site reconnaissance, interviews, a report and any updates required, has been conducted in accordance with the regulation by or under the supervision of a qualified person as required by the regulation. A phase two environmental site assessment of the RSC property, which includes the evaluation of the information gathered from planning and conducting a site investigation, a report, and any updates required, has been conducted in accordance with the regulation by or under the supervision of a qualified person as required by the regulation. The information represents the site conditions at the sampling points at the time of sampling only and the conditions between and beyond the sampling points may vary. As of 2014/04/23, in my opinion, based on the phase one environmental site assessment and the phase two environmental site assessment, and any confirmatory sampling, there is no evidence of any contaminants in the soil, ground water or sediment on, in or under the RSC property that would interfere with the type of property use to which the RSC property will be put, as specified in the RSC. Ground water sampling has been conducted in accordance with the regulation by or under the supervision of a qualified person as required by the regulation. As of 2014/04/23, in my opinion, based on the phase one and phase two environmental site assessments and any confirmatory sampling, the RSC property meets the applicable full depth generic site condition standards prescribed by section 36 of the regulation for all contaminants prescribed by the regulation in relation to the type of property use for which this RSC is filed, except for those contaminants (if any) specified in this RSC at Table 2, Maximum Contaminant Concentrations Compared to Standards Specified in a Risk Assessment. As of 2014/04/23, the maximum known concentration of each contaminant in soil, sediment and ground water at the RSC property for which sampling and analysis has been performed is specified in this RSC at Table 1, Maximum Contaminant Concentrations Compared to Applicable Site Condition Standards. I am a qualified person and have the qualifications required by section 5 of the regulation. I have in place an insurance policy that satisfies the requirements of section 7 of the regulation. I acknowledge that the RSC will be submitted for filing in the Environmental Site Registry, that records of site condition that are filed in the Registry are available for examination by the public and that the Registry contains a notice advising users of the Registry who have dealings with any property to consider conducting their own due diligence with respect to the environmental condition of the property, in addition to reviewing information in the Registry. The opinions expressed in this RSC are engineering or scientific opinions made in accordance with generally accepted principles and practices as recognized by members of the environmental engineering or science profession or discipline practising at the same time and in the same or similar location. I do not hold and have not held and my employer TERRAPROBE INC. does not hold and has not held a direct or indirect interest in the RSC property or any property which includes the RSC property and was the subject of a phase one or two environmental site assessment or risk assessment upon which this record of site condition is based To the best of my knowledge, the certifications and statements in this part of the RSC are true as of 2014/04/23. By signing this RSC, I make no express or implied warranties or guarantees. By checking the boxes above, and entering my membership/licence number in this submission, I, RUSS PAGULAYAN, a qualified person as defined in section 5 of O. Reg. 153/04 am, on 2014/12/05: a) signing this record of site condition submission as a qualified person; and b) making all certifications required as a qualified person for this record of site condition. I Agree Filed Record of Site Condition # 216034 on 2015/04/23 16 of 18 Additional Documentation Provided by Property Owner or Agent The following documents have been submitted to the Ministry of the Environment and Climate Change as part of the record of site condition Certificate of Status or equivalent for the owner Lawyer’s letter consisting of a legal description of the property Copy of any deed(s), transfer(s) or other document(s) by which the RSC property was acquired A Current plan of Survey Area(s) of Potential Environmental Concern Table of Current and Past Uses of the Phase One Property Phase 2 Conceptual Site Model Owner or agent certification statements 5.1.52 Filed Record of Site Condition # 216034 on 2015/04/23 17 of 18 Filed Record of Site Condition # 216034 on 2015/04/23 18 of 18 Request ID: 017115199 Demande n° : Transaction ID: 56174919 Transaction n° : Category ID: CT Catégorie : Province of Ontario Province de l'Ontario Ministry of Government Services Ministère des Services gouvernementaux Date Report Produced: 2014/12/05 Document produit le : Time Report Produced: 13:30:51 Imprimé à : CERTIFICATE OF STATUS ATTESTATION DU STATUT JURIDIQUE This is to certify that according to the records of the Ministry of Government Services DW IGHT D'après les dossiers du Ministère des Services gouvernementaux, nous attestons que la société S L ES S O R H O L D I N GS L I M I T ED Ontario Corporation Number Numéro matricule de la société (Ontario) 0 0 1 5 0 7 7 7 5 is a corporation incorporated, amalgamated or continued under the laws of the Province of Ontario. est une société constituée, prorogée ou née d'une fusion aux termes des lois de la Province de l'Ontario. The corporation came into existence on La société a été fondée le J A NUA RY 0 1 J A N V I ER, 2 0 0 2 and has not been dissolved. et n'est pas dissoute. Dated Fait le D EC EM BER 0 5 D ÉC EM BRE, 2 0 1 4 Director Directeur The issuance of this certifcate in electronic form is authorized by the Ministry of Government Services. La délivrance du présent certificat sous forme électronique est autorisée par le Ministère des Services gouvernementaux. PHASE ONE PROPERTY PHASE TWO PROPERTY RSC PROPERTY TABLE OF AREAS OF POTENTIAL ENVIRONMENTAL CONCERN (Refer to clause 16(2)(a), Schedule D, O.Reg.153/04) Area of Potential Environmental Concern1 Location of Area of Potential Environmental Concern on Phase One Property Potentially Contaminating Activity2 Location of PCA (on-site or off-site) Contaminants of Potential Concern3 Media Potentially Impacted (Ground water, soil and/or sediment) APEC 1 Central property at location of the former dealership building #52 Storage, maintenance, fuelling and repair of equipment, vehicles , and material used to maintain transportation systems On-Site VOCs and PHC Soil and Water Ground APEC 2 Central property at location of the former dealership building #39 Paints Manufacturing, Processing and Bulk Storage On-Site VOCs Soil and Water Ground APEC 3 South western quadrant of the property (former retail fuel outlet location) #28 Gasoline and Associated Products Storage in Fixed Tank On-Site BTEX and PHC Soil and Water Ground APEC 4 South Central area of the property (location of underground storage tank) #28 Gasoline and Associated Products in Fixed Tank On-Site BTEX and PHC Soil and Water Ground APEC 5 South East portion of property in the area of the oil/water separator #28 Gasoline and associated Products in Fixed Tank On-Site PHC and VOCs Soil and Water Ground APEC 6 Entire property. #30 Importation of Fill Material of Unknown Quality On-Site Metals and ORPs (boron, cyanide, hexavalent chromium, mercury, pH) Soil Area of Potential Environmental Concern1 Location of Area of Potential Environmental Concern on Phase One Property Potentially Contaminating Activity2 Location of PCA (on-site or off-site) Contaminants of Potential Concern3 Media Potentially Impacted (Ground water, soil and/or sediment) APEC 7 Potential impact coming to the northern property line #37 Operation of Dry Cleaning Equipment (where chemicals are used) off-site VOCs Ground Water APEC 8 Potential impact coming to the southern property line #52 Storage, maintenance, fuelling and repair of equipment, vehicles , and material used to maintain transportation systems off-site VOCs, BTEX and PHC Ground Water APEC 9 Potential impact coming to the southern property #28 Gasoline and Associated Products Storage in Fixed Tank off-site BTEX and PHC Ground Water Notes: 1 - Area of Potential Environmental Concern means the area on, in or under a phase one property where one or more contaminants are potentially present, as determined through the phase one environmental site assessment, including through, (a) identification of past or present uses on, in or under the phase one property, and (b) identification of potentially contaminating activity. 2 - Potentially Contaminating Activity means a use or activity set out in Column A of Table 2 of Schedule D that is occurring or has occurred in a phase one study area 3 - when completing this column, identify all contaminants of potential concern using the Method Groups as identified in the Protocol for in the Assessment of Properties under Part XV.1 of the Environmental Protection Act, March 9, 2004, amended as of July 1, 2011, as specified below: ABNs, PCBs, Metals, Electrical Conductivity, SAR, CPs, s, As, Sb, Se, Cr (VI), 1,4-Dioxane, THMs, Na, Hg, Dioxins/Furans, PCDDs/PCDFs VOCs, B-HWS, Methyl Mercury, Ocs, BTEX, Cl-, high pH, PHCs, Ca, Mg, CN-, low pH 4 - when submitting a record of site condition for filing, a copy of this table must be attached TABLE OF CURRENT AND PAST USES OF THE PHASE ONE PROPERTY (Refer to clause 16(2)(b), Schedule D, O. Reg. 153/04) Year Name of Owner Description of Property Use Commercial Use 1947 Commercial Enterprise selling automobiles and gasoline Slessor Motors (Newmarket) Limited Commercial Enterprise selling automobiles and gasoline Dwight Slessor Commercial Enterprise selling automobiles John Espey and Helen Espey Agricultural Use (Pig Farm) 1940 Frances Elizabeth Miller Agricultural Use Agricultural Use 1938 Agricultural Use Agricultural Use 1907 Norman D. Rogers and Agnes I. Rogers Norman D. Rogers Agricultural Use Agricultural Use 1896 Obadiah Rogers Agricultural Use Agricultural Use 1889 Cyrus Rogers Agricultural Use Agricultural Use 1864 Levi Rogers Agricultural Use Agricultural Use 1807 Asa Rogers Agricultural Use Agricultural Use 1805 Timoth Rogers Agricultural Use Agricultural Use 1804 Nehemiah Hide Agricultural Use Agricultural Use 2001 1979 1961 Dwight Slessor Holdings Limited Property Use Commercial Use Commercial Use Agricultural Use Other Observations from Aerial Photographs, Fire Insurance Plans, Etc. Interview with owner regarding the development of the property, and air photos. Interview with owner regarding the development of the property, and air photos. Interview with owner regarding the development of the property. Eariest Air Photo (1946) shows no land development, and interview with owner. Eariest Air Photo (1946) shows no land development Eariest Air Photo (1946) shows no land development Eariest Air Photo (1946) shows no land development Eariest Air Photo (1946) shows no land development Eariest Air Photo (1946) shows no land development Eariest Air Photo (1946) shows no land development Eariest Air Photo (1946) shows no land development Eariest Air Photo (1946) shows no land development Eariest Air Photo (1946) shows no land development Notes: 1 - for each owner, specify one of the following types of property use (as defined in O.Reg. 153/04) that applies: Agriculture or other use Commercial use Community use Industrial use Institutional use Parkland use Residential use 2 - when submitting a record of site condition for filing, a copy of this table must be attached **Cette publication hautement spécialisée n’est disponible qu’en anglais en vertu du règlement 671/92, qui en exempte l’application de la Loi sur les services en français. Pour obtenir de l’aide en francais, veuillez communiquer avec le ministère de l’Environnement au 1-800-461-6290 Terraprobe Consulting Geotechnical & Environmental Engineering Construction Materials Inspection & Testing PHASE TWO CONCEPTUAL SITE MODEL 17645 YONGE STREET NEWMARKET, ONTARIO File No 11-10-5203 Dated November 20, 2014 Revised March 6, 2015 ©Terraprobe Inc. Terraprobe Inc. Greater Toronto Hamilton – Niagara Central Ontario Northern Ontario 11 Indell Lane Brampton, Ontario L6T 3Y3 (905) 796-2650 Fax: 796-2250 903 Barton Street, Unit 22 Stoney Creek, Ontario L8E 5P5 (905) 643-7560 Fax: 643-7559 220 Bayview Drive, Unit 25 Barrie, Ontario L4N 4Y8 (705) 739-8355 Fax: 739-8369 1012 Kelly Lake Rd., Unit 1 Sudbury, Ontario P3E 5P4 (705) 670-0460 Fax: 670-0558 www.terraprobe.ca Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 TABLE OF CONTENTS SECTION PAGE 1.0 INTRODUCTION ........................................................................................................................... 1 1.1 Property Description ........................................................................................................... 1 1.2 Summary of Pervious Investigations and Remediation Work ............................................ 2 2.0 INFORMATION FROM THE PHASE ONE ENVIRONMENTAL SITE ASSESSMENT .......... 6 2.1 Areas Where Potentially Contaminating Activity has occurred ......................................... 6 2.2 Areas of Potential Environmental Concern ........................................................................ 7 2.3 Subsurface Structures and Utilities ..................................................................................... 9 3.0 PHYSICAL SETTING OF THE PHASE TWO PROPERTY ...................................................... 10 3.1 Site Stratigraphy ............................................................................................................... 10 3.2 Approximate Depth to Water Table.................................................................................. 11 3.3 Site Hydrogeological Characteristics ................................................................................ 12 3.4 Approximate Depth to Bedrock ........................................................................................ 13 3.5 Section 41 or 43.1 ............................................................................................................. 13 3.6 Soils Placed On, In or Under the Phase Two Property ..................................................... 13 3.7 Proposed Buildings ........................................................................................................... 13 4.0 CONTAMINATION IN OR UNDER THE PHASE TWO PROPERTY ..................................... 14 4.1 Applicable Site Condition Standard.................................................................................. 14 4.2 Media Investigated............................................................................................................ 14 4.3 Sampling Rationale ........................................................................................................... 14 4.4 Contaminants Associated with Each Area ........................................................................ 15 4.5 Medium in Which Contaminant are Associated ............................................................... 17 4.6 Information Known about Each Contaminated Area........................................................ 17 4.7 Distribution of Contaminant ............................................................................................. 18 4.8 Reasons for Discharge of Contaminant ............................................................................ 18 4.9 Migration of Contaminant................................................................................................. 19 4.10 Climatic or Meteorological Influences on Migration ....................................................... 19 4.11 Soil Vapour Intrusion into Buildings ................................................................................ 19 4.12 Relevant Construction Features of Buildings ................................................................... 19 4.13 Building HVAC ................................................................................................................ 19 4.14 Subsurface Structures and Utilities ................................................................................... 19 5.0 POTENTIAL EXPOSURE PATHWAYS AND RECEPTORS.................................................... 20 5.1 Description of All Components ........................................................................................ 20 5.2 Receptor Human Health.................................................................................................... 21 5.3 Receptor Terrestrial Environment..................................................................................... 22 5.4 Receptor Aquatic Environment......................................................................................... 22 5.5 Summary of Potential Receptor Risks .............................................................................. 22 Terraprobe Page No ii Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 FIGURES Figure 1 – Site Location Plan Figure 2 – Areas of Potential Environmental Concern Figure 3 – Survey Plan Figure 4 – Borehole Location Plan Figure 5 – Soil Exceedances Figure 6 – Ground Water Exceedances Figure 7 – Excavation Areas Figure 8 – Location of Confirmatory Samples - Impact Area 1 Figure 9 – Location of Confirmatory Samples - Impact Area 2 Figure 10 – Location of Confirmatory Samples - Impact Area 3 Figure 11 – Cross Section A-A’ - Impact Area 1 Figure 12 – Cross Section B-B’ - Impact Area 2 Figure 13 – Cross Section C-C’ - Impact Area 3 Figure 14 – Post Remediation Ground Water - APEC 1, 2, 5 Figure 15 – Pathways and Receptors Figure 16 – Post Remediation Ground Water Cross Section A-A’ - APEC 1, 2, 5 APPENDICES Appendix A – Plan of Survey/Lawyers Letter Appendix B – Grain Size Analysis Terraprobe Page No iii Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario 1.0 Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 INTRODUCTION The following document presents the Phase Two Conceptual Site Model for the Phase Two Property (Property) which consists of: a) Pin 03578-0942 LT Interest/Estate Fee Simple Part of Lot 96, Concession 1, East of Yonge Street, Geographic Township of Est Gwillimbury, Town of Newmarket, being Part 1 on Plan of Survey by Krcmar Surveyors Ltd. dated November 14, 2012, (part of PIN 03578-0942 (LT). Address: 17645 Yonge Street, Newmarket, Ontario Assessment Roll Number: 19 48 040 172 23000 0000 The Plan of survey is located in the Appendix A, as well as the letter from W. Roy Gordon Professional Corporation Lawyer confirms the above information. 1.1 Property Description The Property is located at 17645 Yonge Street on the east side of Yonge Street, approximately 250 m north of the intersection of Yonge Street and Davis Drive in Newmarket, Ontario Figure 1. The Property is irregular in shape with frontage along the east side of Yonge Street (Figure 3). The Property has an area of about 1.6950 hectares. The property is located in an area of mixed development/property use that includes commercial (retail and professional office), and residential developments east of George Street. The Property information is as follows: Legal Description Part of Lot 96, Concession 1, East of Yonge Street, Geographic Township of Est Gwillimbury, Town of Newmarket, being Part 1 on Plan of Survey by Krcmar Surveyors Ltd. dated November 14, 2012, (part of PIN 03578-0942 (LT). PIN(s) Pin 03578-0942 LT Interest/Estate Fee Simple Assessment Roll Number 19 48 040 172 23000 0000 Municipal Address 17645 Yonge Street, Newmarket, Ontario Zoning Zoned UC-P-119 (Provincial Urban Centre Zone) – Residential Land use Area 1.6950 ha . Terraprobe Page No 1 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario 1.2 Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Summary of Pervious Investigations and Remediation Work Previous investigations for the Property, which were provided to Terraprobe, are summarized below: Report Title Phase I and II Environmental Assessment – Slessor Motors, 17645 Yonge Street North, Newmarket, Ontario Report Date September, 2001 File No. 01-16 Prepared By Alpha Environmental Services Inc. Prepared For Dwight Slessor Holdings Ltd. • The subject property consisted of a single storey commercial/industrial building that was originally constructed in 1962 and was renovated in 1999. The building was heated by natural gas. A showroom was present at the west side of the building and the rear or east side of the building was comprised of a garage with a body and paint shop and full service bays. A gasoline service bar was present at the front (west) side of the property with six underground gasoline storage tanks, two associated pump islands, and a kiosk. New cars are stored on the paved area at the north side of the property. • The building was occupied by Slessor Motors and was used as a car dealership and vehicle service garage with a gasoline service bar operated by Cango at the southwest side of the property fronting onto Yonge Street. • Six underground storage tanks associated with the gasoline service bar were present at the southwest side of the property. • A spill was reported to have occurred in approximately 1988 due to overfilling a tank, and a clean-up was undertaken whereby a considerable amount of contaminated soil was removed from the site up to 4 m below grade. Monitoring wells were installed at the time; however, all the wells were found to be destroyed or compromised at the time of the Alpha Environmental inspection. • Two aboveground storage tanks (approximately 900 L) for new oil with no secondary containment were observed, one at the north interior side of the building and one at the south interior side of the building. • One double-walled aboveground storage tank (approximately 13,600 L) containing waste oil was present at the south exterior side of the building. • A new oil/water interceptor had been installed in approximately May of 2000, and is cleaned out annually by Safety Kleen. • Slessor Motors had been assigned Ontario Waste Generator Number ON2030800 for waste oil, solvents, and waste anti-freeze that are removed by Safety Kleen as needed. Terraprobe Page No 2 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 • Slessor Motors has been assigned Certificate of Approval 8-3484-93-006 for air emissions from the down-draft oven in the paint shop. • Silty clay fill and silty clay were present in the boreholes to the maximum drilled depth of 5.18 m. • Ground water was encountered in the six drilled boreholes at depths ranging from 1.68 m to 2.10 m below grade. • Relative groundwater elevation measurements indicated that the ground water flow direction is toward the southwest. • Concentrations of benzene and ethylbenzene above the specified Table A guideline limit in the MOE’s Guideline for Use at Contaminated Sites in Ontario were found in the soil samples from four of the boreholes, located south of the retail fuel outlet kiosk and to the south of the USTs, along the southern property boundary. The concentration of toluene in one soil sample from a borehole to the south of the kiosk exceeded the Table A guideline limit. • Several of the ground water samples submitted for laboratory analysis exceeded the Table A guideline limits for benzene, toluene, ethylbenzene and xylene. Report Title Phase II Environmental Site Assessment – 17645 Yonge Street, Newmarket, Ontario Report Date February 28, 2002 File No. 01180 Prepared By Barenco Inc. Prepared For Cango Inc. • The intent of the work was to remove impacted soil identified in the Alpha Environmental report and to ensure that activities that had taken place on the subject property were not a source of adverse environmental effects to adjacent properties. • The report details removal of impacted soil from an area south of the UST nest. Four test pits were excavated and one worst-case soil sample was submitted from each test pit for laboratory analysis of benzene, toluene, ethylbenzene and xylenes (BTEX), and total petroleum hydrocarbons (TPH) in the gas/diesel and heavy oils ranges. Temporary subsurface monitors were installed in two of the test pits and one water sample from each temporary monitor was submitted for analysis of BTEX and TPH in the gas/diesel range. Ground water samples were also submitted from four of the monitoring wells previously installed by Alpha Environmental. The analytical results were compared to the applicable MOE standards in effect at that time as defined in the Ontario Ministry of Environment’s Guideline for Use at Contaminated Sites in Terraprobe Page No 3 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Ontario (February 1997). The results were compared to the generic Table A standards for industrial/commercial land use (medium and fine textured soil). • • The results of the investigation were as follows: o All four “worst-case” soil samples submitted from the test pits excavated along the property boundary met the applicable Table A criteria for BTEX and TPH. o Ground water samples taken from the temporary monitors along the southern property boundary exceeded the Table A guideline for benzene. o One ground water sample collected from the monitoring well to the south of the pump island exceeded the Table A guideline for both benzene and ethylbenzene. Barenco concluded in their report that “minor exceedances of petroleum parameters in soil and ground water samples collected from the subject property are not indicative of any significant environmental issues. Rather, the exceedances are indicative of the present of an operating gas bar on the property.” The report also states that “[u]nder the Management Protocol that supports [the Technical Standards and Safety Act], GA1/99, remediation of a gas bar is only required if there is off-site migration of petroleum-related contaminants or if there are unacceptable safety conditions for continued operation… there are no unacceptable safety conditions that would arise under continued operation of the gas bar. No liquid product was observed in any of the ground water samples and the native silty clay surrounding the petroleum handling equipment will prevent migration of petroleum off-site. Hence, it appears that activities that are taking place on the subject property are not a source of environmental impairment on adjacent properties. Accordingly, further clean up activities in the vicinity of the operating gas bar, including soil removal, are neither recommended nor warranted at this time.” • Based on the results of the investigation, ground water along the property boundary exceeded the applicable Standards. There was therefore a high probability that petroleum-related contaminants were migrating off-site. Report Title Environmental Inspection of UST and Pump Island Excavation – Slessor Motors, 17645 Yonge Street, Newmarket, Ontario Report Date September 18, 2009 File No. W2466 Prepared By Winchurch Environmental Inc. Prepared For Cannington Construction Ltd. • The investigation by Winchurch was conducted after the removal of the pump island, piping and USTs associated with the former Cango retail gas bar on the property by Terraprobe Page No 4 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Cannington Construction Limited on September 4, 2009. The scope of the work was as follows: • To ascertain the presence and/or extent of any environmental impact in the vicinity of the former USTs, pump islands and piping, • To submit representative “worst-case” assessment soil samples for laboratory analysis, and • To compare the analytical results from the soil samples to applicable site condition standards to confirm/refute regulatory compliance. Ground water was not sampled or tested as part of the investigation. • Winchurch submitted twelve (12) soil samples from the walls and base of the pump island and UST excavations for chemical analysis. Samples were selected for submission based on headspace vapour readings. • The regulatory Standards to which soil results were compared as part of this report are those contained within Table 5 of the Ontario Regulation 153/04 reference document Soil, Ground Water and Sediment Standards for Use Under Part XV.1 of the Environmental Protection Act, for industrial/commercial/community use and a medium/fine-textured soil and non-potable ground water condition. These were not the appropriate Standards for the property. The Town of Newmarket derives its drinking water from ground water sources, which means that the ground water should be in a potable condition and the appropriate Standards were those contained in Table 2, not those in Table 5. The report concludes that “[a]n examination of the analytical results indicates that the concentrations of BTEX/PHC measured in the soil samples obtained from the excavation are in compliance with the applicable Table 5 site condition standards for the chemical parameters analyzed.” • Upon comparison of the analytical results with the appropriate Table 2 Standards, several of the soil samples exceeded the Standards for parameters including fraction 1 petroleum hydrocarbons (F1 PHCs), F2 PHCs, benzene, and ethylbenzene. • The report did not recommend further environmental work. Terraprobe Page No 5 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario 2.0 Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 INFORMATION FROM THE PHASE ONE ENVIRONMENTAL SITE ASSESSMENT 2.1 Areas Where Potentially Contaminating Activity has occurred The Phase One Environmental Site Assessment identified the following Potentially Contaminating Activities (PCAs) on the Property and within the Study Area. The locations of the PCAs are illustrated in Figure 3. Location of PCA PCA Potential APEC Justification (Yes/No) Central property at location of the former dealership building #52 Storage, maintenance, fuelling and repair of equipment, vehicles , and material used to maintain transportation systems Yes PCA has potential to cause an APEC on the Property Central property at location of the former dealership building #39 Paints Manufacturing, Processing and Bulk Storage Yes PCA has potential to cause an APEC on the Property in the area of the former garage. South western quadrant of the property (former retail fuel outlet location) #28 Gasoline and Associated Products Storage in Fixed Tank Yes PCA has potential to cause an APEC on the property in the area of the former garage. South Central area of the property (location of underground storage tank) #28 Gasoline and Associated Products Storage in Fixed Tank Yes PCA has the potential to cause an APEC on the property in the area of the former tanks. South East portion of property in the area of the oil/water separator #28 Gasoline and Associated Yes PCA has the potential to cause an APEC on Entire property #30 Importation of Fill Material of Unknown Quality Yes PCA has potential to cause an APEC on the Property. Excavations were identified in this area. 17725 Yonge Street #37 Operation of Dry Cleaning Equipment (where chemicals are used) Yes PCA has the potential to cause an APEC on the property Directly adjacent to the north property line. Products Storage in Fixed Tank the property in the area of the former tanks. #28 Gasoline and Associated Products Storage in Fixed Tank Terraprobe Page No 6 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Location of PCA Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 PCA Potential APEC Justification (Yes/No) Adjacent to the southwest portion of the property 2.2 #52 Storage, maintenance, fuelling and repair of equipment, vehicles , and material used to maintain transportation systems Yes The garage bays at the neighboring property are close enough for the PCA to be a potential APEC on the property. Areas of Potential Environmental Concern The following areas of potential environmental concern (APEC) resulting from the potentially contaminating activities were identified by the Phase One ESA. The location of the APECs are shown on the attached Figure 3 Area of Potential Environmental Concern1 Location of Area of Potential Environmental Concern on Phase One Property Potentially Contaminating Activity2 Location of PCA (on-site or off-site) Contaminants of Potential Concern3 Media Potentially Impacted (Ground water, soil and/or sediment) APEC 1 Central property at location of the former dealership building #52 Storage, maintenance, fuelling and repair of equipment, vehicles , and material used to maintain transportation systems On-Site VOCs and PHC Soil and Water Ground APEC 2 Central property at location of the former dealership building #39 Paints Manufacturing, Processing and Bulk Storage On-Site VOCs Soil and Water Ground APEC 3 South western quadrant of the property (former retail fuel outlet location) #28 Gasoline and Associated Products Storage in Fixed Tank On-Site BTEX and PHC Soil and Water Ground APEC 4 South Central area of the property (location of underground storage tank) #28 Gasoline and Associated Products in Fixed Tank On-Site BTEX and PHC Soil and Water Ground Terraprobe Page No 7 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Location of Area of Potential Environmental Concern on Phase One Property Potentially Contaminating Activity2 APEC 5 South East portion of property in the area of the oil/water separator APEC 6 Area of Potential Environmental Concern1 Media Potentially Impacted (Ground water, soil and/or sediment) Location of PCA (on-site or off-site) Contaminants of Potential Concern3 #28 Gasoline and associated Products in Fixed Tank On-Site PHC and VOCs Soil and Water Entire property. #30 Importation of Fill Material of Unknown Quality On-Site Metals and ORPs (boron, cyanide, hexavalent chromium, mercury, pH) Soil APEC 7 Potential impact coming to the northern property line #37 Operation of Dry Cleaning Equipment (where chemicals are used) off-site VOCs Ground Water APEC 8 Potential impact coming to the southern property line #52 Storage, maintenance, fuelling and repair of equipment, vehicles , and material used to maintain transportation systems off-site VOCs, BTEX and PHC Ground Water APEC 9 Potential impact coming to the southern property #28 Gasoline and Associated Products Storage in Fixed Tank off-site BTEX and PHC Ground Water Ground Notes: 1 - Area of Potential Environmental Concern means the area on, in or under a phase one property where one or more contaminants are potentially present, as determined through the phase one environmental site assessment, including through, (a) identification of past or present uses on, in or under the phase one property, and (b) identification of potentially contaminating activity. 2 - Potentially Contaminating Activity means a use or activity set out in Column A of Table 2 of Schedule D that is occurring or has occurred in a phase one study area 3 - when completing this column, identify all contaminants of potential concern using the Method Groups as identified in the Protocol for in the Assessment of Properties under Part XV.1 of the Environmental Protection Act, March 9, 2004, amended as of July 1, 2011, as specified below: ABNs, PCBs, Metals, Electrical Conductivity, SAR, CPs, s, As, Sb, Se, Cr (VI), 1,4-Dioxane, THMs, Na, Hg, Dioxins/Furans, PCDDs/PCDFs VOCs, B-HWS, Methyl Mercury, Ocs, BTEX, Cl-, high pH, PHCs, Ca, Mg, CN-, low pH 4 - when submitting a record of site condition for filing, a copy of this table must be attached Terraprobe Page No 8 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario 2.3 Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Subsurface Structures and Utilities Underground utilities are present on the Property. During the removal of impacted soils, impacts along the utilities were assed and not encountered. Based upon this, it is possible that any potentially contaminated ground water could migrate horizontally along the utilities onto or off the Property. The Property is covered with a hard surface cap. As such, the hard cap will limit infiltration of storm water from the ground surface. Downward migration of contaminates would be limited. Terraprobe Page No 9 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 3.0 PHYSICAL SETTING OF THE PHASE TWO PROPERTY 3.1 Site Stratigraphy Earth Fill There is a pavement structure consisting of an asphaltic concrete layer that ranged in thickness from 110 to 185 mm overlying an aggregate layer ranging in thickness from 390 to 415 mm. Underlying the surficial pavement structure earth fill was encountered that consists of silt with trace to some clay, trace sand to some sand and trace gravel. The earth fill, where encountered, extends to 1.5 to 4.6 metres below existing grade (Elev. 262.3 to 258.7 metres). The earth fill is generally characterized as being brown, dark brown or brownish grey and moist to wet. Standard Penetration Test results (“N” Values) measured in the earth fill ranged from 2 to 15 blows per 300 mm of penetration indicating a soft to stiff consistency, or a very loose to compact relative density. Upper and Lower Silt Layers Two distinct silt layers were encountered within the boreholes advanced on site, and consist of silt with some clay and trace to no sand. The “upper” silt layer was encountered in near surface, and the “lower” silt layer was encountered in all boreholes between the two glacial till layers (as described in the subsequent section). The silt layers were encountered at the following depths and elevations, and with the following properties: • The upper silt layer was encountered at 0.5 to 2.7 metres below existing grade (Elev. 263.0 to 259.8 metres) and extends to 3.5 to 4.6 metres below existing grade (Elev. 259.2 to 258.6 metres). The upper silt layer is generally characterized as brown and wet. Standard Penetration Test results (“N” Values) measured in the upper silt layer ranged from 4 to 15 blows per 300 mm of penetration, indicating a firm to stiff consistency. Insitu shear vane tests conducted yielded in-situ undrained shear strengths of 96 to greater than 100 kPa. • The lower silt layer was encountered at 10.7 to 12.2 metres below existing grade (Elev. 252.7 to 250.3 metres) and extends to 13.7 to 15.2 metres below existing grade (Elev. 249.8 to 248.6 metres). The lower silt layer is generally characterized as grey and wet. Standard Penetration Test results (“N” Values) measured in the lower silt layer ranged from 7 to 37 blows per 300 mm of penetration, indicating a loose to dense (on average, compact) relative density. Upper and Lower Glacial Till Layers Two distinct glacial till layers were encountered within the boreholes advanced on site and are comprised primarily of a matrix of silt with some clay to clayey, some sand to sandy, and trace gravel. The “upper” glacial till layer was encountered in all boreholes between the two silt layers, and the “lower” glacial till layer was encountered in all boreholes underlying the lower silt layer and extended beyond the vertical Terraprobe Page No 10 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 extent of investigation (14.2 to 17.2 metres below existing grade). The glacial till layers were encountered at the following depths and elevations, and with the following properties: • The upper glacial till layer was encountered at 3.5 to 4.6 metres below existing grade (Elev. 259.2 to 258.5 metres) and extended to 10.7 to 12.2 metres below existing grade (Elev. 252.7 to 250.3 metres). The upper glacial till layer is generally characterized as brown to grey and moist. Standard Penetration Test results (“N” Values) measured in the upper glacial till layer ranged from 11 to 52 blows per 300 mm of penetration, indicating a stiff to hard consistency. • The lower glacial till layer was encountered at 13.7 to 15.2 metres below existing grade (Elev. 249.8 to 248.6 metres) and extended to beyond the vertical extent of investigation at 14.2 to 17.2 metres below existing grade (Elev. 249.3 to 245.3 metres). The lower glacial till layer is generally characterized as grey and moist to wet. Standard Penetration Test results (“N” Values) measured in the lower glacial till layer ranged from 17 to 40 blows per 300 mm of penetration, indicating a very stiff to hard consistency, but on average is very stiff. Bedrock 3.2 Approximate Depth to Water Table Stabilized water levels were also measured within all monitoring wells installed at the site. Stabilized water levels were measured between October 21, 2010 and April 23, 2014. The ground water elevations are tabulated on the following table. The locations of the monitoring wells are shown on Figure 4. Ground Water Levels Geodetic Ground elevation (m asl) Water Elevation Oct 21/10 (m) Water Elevation July 13/11 (m) Water Elevation Mar 14/12 (m) Water Elevation Nov 28/12 (m) Water Elevation Apr 26/13 (m) Water Elevation Sept 25/13 (m) Water Elevation Feb 18/14 (m) Water Elevation April 23/14 (m) 262.84 263.29 260.44 261.29 262.07 262.38 MW 1 264.79 262.40 262.57 262.96 262.81 MW 3 264.36 261.91 262.60 263.26 262.87 263.56 MW 4-12 262.97 260.81 261.24 MW 5 264.36 262.34 MW 7 263.28 260.00 MW 8-1 263.19 258.88 261.77 MW 8-2 263.18 261.31 261.93 MW 9-1 263.76 258.70 260.59 261.28 259.90 Dry 260.85 261.34 MW 9-2 263.72 261.06 259.94 261.82 261.39 261.45 261.42 262.40 Terraprobe 262.74 262.64 262.27 262.11 Page No 11 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Geodetic Ground elevation (m asl) Water Elevation Oct 21/10 (m) Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Water Elevation July 13/11 (m) 261.62 Water Elevation Mar 14/12 (m) Water Elevation Nov 28/12 (m) Water Elevation Apr 26/13 (m) Water Elevation Sept 25/13 (m) Water Elevation Feb 18/14 (m) Water Elevation April 23/14 (m) 260.71 261.64 MW 10 263.13 261.33 MW 11 262.98 261.22 261.81 MW 19 263.35 261.62 MW 20 263.18 261.73 MW 21 263.33 261.89 262.41 MW 25 262.93 261.19 262.04 MW 27 262.86 261.93 262.59 MW 28 262.75 261.26 261.99 MW 30-1 262.97 261.09 261.82 MW 30-2 262.97 261.38 262.10 MW 31 263.37 262.60 262.89 262.86 MW 32 264.07 263.12 263.69 263.76 BH 101 263.20 262.17 261.21 BH102 263.50 262.95 262.62 BH106 263.50 262.56 261.96 MW1-14 263.32 260.80 261.60 MW2-14 263.28 260.38 261.41 MW3-14 262.95 260.35 261.35 264.00 The ground water measurements at the site during the period of the investigation indicate a static ground water level in the sandy, clayey silt/sand and silt that generally ranges from Elev. 258.88 metres to 264.00 metres. Several of the wells were decommissioned during the excavation of soils from the various APECs. 3.3 Site Hydrogeological Characteristics Single well response tests (slug tests) were conducted on some of the wells that were located on the property. The hydraulic conductivity of ranged from 10-7 m/s to 10-8 m/s, typical values for a glacial till. The ground water table is within the native glacial till. The horizontal hydraulic gradient of the ground water for the Property was determined to be approximately 0.03 m/m. There is also an upward hydraulic gradient of 0.02 m/m (between 242 masl and 256 masl). Terraprobe Page No 12 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario 3.4 Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Approximate Depth to Bedrock Bedrock was not encountered during this investigation. Based on bedrock topography mapping provided by the Ontario Geological Survey, the top of bedrock is approximately 140 masl which is 120 m below ground surface at the Phase Two Property. 3.5 Section 41 or 43.1 Section 41 of the regulation (Environmentally Sensitive Areas) does not apply to the Phase Two Property. Section 43.1 of the regulation (shallow soil property or water body) does not apply to the Property. 3.6 Soils Placed On, In or Under the Phase Two Property No soils have been imported or placed on, in or under the Phase Two Property since the Phase One ESA was completed in 2014. Soils placed on the Phase Two Property prior to the 2014 investigation were the result of historic filling of the site during original development of the Property. Depth of fill placed on the Property prior to 2012 is presented on cross-sections of the Property on Figure 5 through Figure 9, and also on the borehole logs in Appendix E. 3.7 Proposed Buildings There are currently no plans for the redevelopment. Terraprobe Page No 13 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 4.0 CONTAMINATION IN OR UNDER THE PHASE TWO PROPERTY 4.1 Applicable Site Condition Standard The applicable soil and ground water Standards for the Property were determined to be those in Table 2 of the April 15, 2011 Ontario Ministry of Environment (MOE) “Soil, Ground Water and Sediment Standards for use under part XV.1 of the Environmental Protection Act” for Residential, Parkland, and Institutional property use in a potable ground water condition for medium/fine textured soil (Table 2 RPI MFT Standards). These are considered to be the applicable Standards for the following reasons: • The proposed use for the site is for Residential Land Use. • Soil at the Property was determined to be medium/fine textured based on grain size analysis of recovered soil samples. • Bedrock is located at a depth of greater than 2 m. • The site is located in the City of Newmarket, which obtains its potable water from ground water sources. • The site is not located within 30 m of a surface water body. • The site is not located in or adjacent to a provincial park or an area of natural significance. 4.2 Media Investigated Based upon the Potentially Contaminating Activities (PCAs) identified in the Phase One ESA for the Property, it was decided that investigation was required for: • Soil • Ground water 4.3 Sampling Rationale Impact area 1, found while investigating APEC 1, 2 & 5 • Soils impact was identified based on the staining of soils in the area of an Oil/Water Separator • Ground water impacts were identified at MW19 and MW20 • The extent of the soils impacts were identified by the soils that met the applicable standards from boreholes BH7, BH8, BH10, BH 11, BH16, BH17, BH18, BH20, BH101, BH102, and BH104. • The extent of the ground water impacts was identified by the ground water that met the applicable standards from Monitoring Well MW7, MW8-1, MW8-2, MW10, MW11, MW101, MW102, MW106, MW1-14, and MW2-14. • Confirmatory soil and ground water sampling after the removal of the Oil/Water separator and the impacted soils. Terraprobe Page No 14 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Impact area 2 found while investigating APEC-3 • Soil samples from fill material from boreholes BH15 was found to exceed for Petroleum Hydrocarbons Fraction F1. • Soil samples from native soil from boreholes BH15, BH21, BH22, BH 23, and BH24 were used to delineate the extent of the soils impacts. • Ground water samples from Monitoring Well MW21, MW25 and MW101 were used to confirm that there were no ground water impacts associated with these soils impacts. • Confirmatory soil sampling after the removal of the identified soils impacts was used to confirm that the impacts were removed. Impact area 3 identified during the removal of the UST in this area. • Soil samples from the native soils at boreholes BH11, BH4-12, and BH104 were used to delineate the extent of soils impacts. • Ground water samples from Monitoring Well MW4-12, and MW3-14 confirmed the absence of ground water impacts in the area of the UST. • Confirmatory soil sampling after the removal of the underground storage tank confirmed the removal of any potentially impacted soils. Quality of soil fill on the property (APEC 6) • Soil samples from fill material from boreholes BH1, BH2, BH3, BH4, BH5, BH10, BH11, and BH15 where soil fill had been placed as cover for subsurface structures. The results of the soil samples were found to meet the appropriate standards for the COCs identified for APEC 6. Off-Site APECs 7, 8 & 9 • Ground water samples from Monitoring Well MW1, MW3, and MW32 were found to meet the applicable site condition standards. • Ground water samples from Monitoring Well MW25, MW27, MW29-1, MW29-2, and MW4-12 from the southern property boundary were found to meet the applicable site condition standards. The sampling conducted at the Property included all media present on the Property and covered the full area of the Property. The soil sampling included both the fill and the native soil strata. The locations of the boreholes are shown on the attached Figure 4. 4.4 Contaminants Associated with Each Area The Phase Two ESA used the Table 3 Community Standards for the soil and ground water as found in the “Soil, Ground Water and Sediment Standards for Use Under Part XV.1 of the Environmental Protection Act” (April 2011). Terraprobe Page No 15 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Impact Area 1 Soil (fill) • No Contaminants of Concern were noted in the soil fill. • Stained soils were observed and removed during the removal of underground structures such as oil/water separators. Soil (native) • No Contaminants of Concern were identified in the native soils. • Stained soils were observed and removed during the removal of underground structures such as oil/water separators and the associated piping that led to it. Ground Water • Petroleum Hydrocarbon Fraction F1 • Petroleum Hydrocarbon Fraction F2 • Petroleum Hydrocarbon Fraction F3 • Petroleum Hydrocarbon Fraction F4 Impact Area 2 Soil (fill) • Petroleum Hydrocarbons F1 Soil (native) • No Contaminants of Concern were noted in the native soils. Ground Water • No Contaminants of Concern were identified in the ground water Impact Area 3 Soil (fill) • No Contaminants of Concern were noted in the soil fill. • Stained soils were observed and removed during the removal of underground structures such as oil/water separators. Soil (native) Terraprobe Page No 16 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 • No Contaminants of Concern were identified in the native soils. • Stained soils were observed and removed during the removal of the underground storage tank. Ground Water • 4.5 No Contaminants of Concern were identified in the ground water. Medium in Which Contaminant are Associated Earth fill, native soils and ground water were investigated as part of the Phase Two ESA. Contaminants of Concern were identified in: Soil (fill) • Petroleum Hydrocarbon Fraction F1 • Petroleum Hydrocarbon stained soils Soil (native) • Petroleum Hydrocarbon stained soils Ground Water 4.6 • Petroleum Hydrocarbon Fraction F1 • Petroleum Hydrocarbon Fraction F2 • Petroleum Hydrocarbon Fraction F3 • Petroleum Hydrocarbon Fraction F4 Information Known about Each Contaminated Area Soil (fill) The presence of the Petroleum Hydrocarbon F1 contamination was limited in extent and likely came from a surface spill. The distribution of the stained soil fill was in the area of the underground services to the oil/water separator. Soil (native) The distribution of petroleum hydrocarbon stained soils were in the vicinity of the oil water separator and the associated piping, including the location of floor drains in the former shop floor. Ground Water Terraprobe Page No 17 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Petroleum Hydrocarbons were identified in the ground water in the vicinity of the oil/water separator and the floor drains in the former shop area. 4.7 Distribution of Contaminant Soil (fill) The distribution of the impacts in the soil fill in Impact area 2 was a spill that appeared to originate from surface to a depth of 4 metres below ground surface. Soil (native) The distribution of soils impacts in Impact area 1, extended to a depth of about 4 m below ground surface (into the native soils). Confirmatory soil samples were collected in the area of the excavation to confirm that the lateral and vertical extent of the excavations had been reached. Impact area 2 the remedial excavation extended to a depth of about 4 m below ground surface. Confirmatory soil samples were collected in the area of the excavation to confirm that the lateral and vertical extent of the excavations had been reached. The depth of excavation in Impact Area 3 was 3 m below ground surface. Confirmatory soil samples were collected in the area of the excavation to confirm that the lateral and vertical extent of the excavations had been reached. The location of the excavations to remove the soil and ground water impacts are shown on Figure 7. The location of the confirmatory samples taken in the area of each of the identified Impact Areas is shown on Figure 8, 9, and 10. The vertical extent of the excavations and the location of the former impacts are shown on Figures 11, 12, and 13 for the different identified Impact Areas. Ground Water In the area of the ground water impacts the ground water was excavated as part of the soils removed. Confirmatory ground water samples were taken in monitoring wells in the vicinity of the previously identified ground water impacts (Impact Area 1) and in the vicinity of the location of the former UST (Impact Area 2). The results of the confirmatory ground water sampling were found to meet the applicable site conditions standards are presented on Figure 14, indicating that the original ground water impacts identified had been removed. 4.8 Reasons for Discharge of Contaminant The discharge of Contaminants of Concern at the property in the soil occurred as a result of the activities at the property which included the maintenance and repair of automobiles. Terraprobe Page No 18 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario 4.9 Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Migration of Contaminant Contaminants of Concern were identified in the earth fill, native soils and ground water. Based on the direction of ground water flow ground water wells were placed down gradient of known ground water impacts and were delineated. The migration of impacts was limited by the tight glacial till soils where the impacts were identified. 4.10 Climatic or Meteorological Influences on Migration The Property was covered by a completely by a hard cap (asphalt and buildings during the time where contaminants were present). There is no erosion occurring on the Property and no significant seasonal variation in the water table. Climatic or meteorological influence appear to have had little to no influence on migration of contamination on the Property 4.11 Soil Vapour Intrusion into Buildings No volatile Contaminants of Concern have been identified on the Property in the soil and ground water during the investigation. As such there is no possibility for soil vapour intrusion of contaminants into future buildings. No buildings currently exist on the Property, therefore there is no possible of vapour intrusion. 4.12 Relevant Construction Features of Buildings No buildings were present on the Property. 4.13 Building HVAC No HVAC systems were present and no volatile Contaminants of Concern have been identified on the Property. Therefore, it is not possible building HVAC to affect the distribution and transport of Contaminants of Concern. 4.14 Subsurface Structures and Utilities Underground utilities are present on the Property. Based upon this, it is possible that any potentially contaminated ground water could migrate horizontally along the utilities onto or off the Property. However in the area where the soils impacts were identified, they were removed. There is no further source of impact on the Property. Terraprobe Page No 19 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 5.0 POTENTIAL EXPOSURE PATHWAYS AND RECEPTORS 5.1 Description of All Components Following is the list of all risk based components of the potential exposure pathways and receptors. These components are used in this section as well as the graphical representation of the pathways and receptors presented on Figure 15. GW1 – Ground water for drinking water purposes GW2 – Ground water for protection from movement to indoor air GW3 – Ground water for protection of aquatic life S1 – Soil for protection of a residential receptor from direct contact with surface soil S2 – Soil for protection from direct soil contact for a lower frequency and intensity exposure than residential surface soil, such as commercial or industrial scenarios S3 – Soil for direct soil contact for a low-frequency, high-intensity, human health exposure scenario without children present that is protective of a worker digging in the soil S-IA – Soil for protection of movement to indoor air and human exposure S-OA – Soil for protection of movement to outdoor air and human exposure S-Odour – Soil for protection of excessive odours S-GW1 – Soil for protection from movement to ground water for drinking water purposes S-GW3 – Soil for protection from movement to ground water and then to aquatic life Plants and Soil Organisms – Soil for protection against adverse effects to plants and soil dwelling organisms Mammals and Birds – Soil for protection against adverse effects through direct soil and food ingestion to mammals and birds Please note Figure 15 is a graphical representation of potential pathways and receptors and does not have a scale or orientation which can be related to the Phase Two Property. The sections below represent conditions prior to remediation. Terraprobe Page No 20 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario 5.2 Receptor Human Health Potential Pathway Potential Risks Sources GW1 Contamination present in groundwater GW2 Contamination present in groundwater S1 Contamination present in fill material Contamination not present in native soil S2 Contamination present in fill material Contamination not present in native soil S3 Contamination present in fill material Contamination not present in native soil S-IA Contamination present in fill material Contamination not present in native soil S-OA S-Odour Contamination present in fill material Contaminant of Concern from Phase One ESA VOC, BTEX, PHC VOC, BTEX, PHC VOC, BTEX, Metals, PHC, Potential Risks Prior to Remediation Off-site risk prior to remediation. Onsite pathway incomplete. Risk present prior to remediation. Risk present prior to remediation. boron, cyanide, hexavalent chromium, mercury, pH VOC, BTEX, Metals, PHC, boron, cyanide, hexavalent chromium, mercury, pH VOC, BTEX, Metals, PHC, Risk present prior to remediation. Risk present prior to remediation. boron, cyanide, hexavalent chromium, mercury, pH VOC, BTEX, Metals, PHC, boron, cyanide, hexavalent chromium, mercury, pH VOC, BTEX, Metals, PHC, Risk present prior to remediation. Risk present prior to remediation. Contamination not present in native soil boron, cyanide, hexavalent chromium, mercury, pH Contamination present in fill material VOC, BTEX, Metals, PHC, boron, cyanide, hexavalent chromium, mercury, pH Risk present prior to remediation. VOC, BTEX, Metals, PHC, boron, cyanide, hexavalent chromium, mercury, pH Off-site risk prior to remediation. Onsite pathway incomplete. Contamination not present in native soil S-GW1 Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Contamination present in groundwater Terraprobe Page No 21 Phase Two Environmental Site Assessment 17645 Yonge Street, Newmarket, Ontario 5.3 Nov 20, 2014. Revised Mar 6, 2015 11-10-5203 Receptor Terrestrial Environment Potential Pathway Potential Risks Sources Contaminant of Concern from Phase One ESA Potential Risks Plants and Soil Organisms Contamination present in fill material VOC, BTEX, Metals, PHC, boron, cyanide, hexavalent chromium, mercury, pH Risk present prior to remediation. Mammals and Birds Contamination present in fill material VOC, BTEX, Metals, PHC, boron, cyanide, hexavalent chromium, mercury, pH Risk present prior to remediation. 5.4 Contamination not present in native soil Contamination not present in native soil Receptor Aquatic Environment Potential Pathway Potential Risks Sources Contaminant of Concern from Phase One ESA Potential Risks GW3 Contamination present in groundwater VOC, BTEX, PHC Off-site risk prior to remediation. Onsite pathway incomplete. S-GW3 Contamination present in groundwater VOC, BTEX, PHC Off-site risk prior to remediation. Onsite pathway incomplete. 5.5 Summary of Potential Receptor Risks Contaminants of Concern were identified on the Property above the applicable full depth Generic Site Condition Standards. The contaminants in the soil and ground water were excavated and removed from the property. The remaining soil and ground water at the property were found to meet the applicable full depth Generic Site Condition Standards, based on confirmatory sampling. Terraprobe Page No 22 FIGURES TERRAPROBE INC. Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 KEY MAP SITE REFERENCE: Microsoft Streets & Trips 2010 SITE NOTES: LEGEND: PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL SITE LOCATION: 17645 YONGE STREET, NEWMARKET FIGURE TITLE: SITE LOCATION PLAN REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 1 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 KEY MAP PHASE 1 STUDY AREA SITE APEC 6 (Entire Site) ET REFERENCE: RE GE ST GEOR METRO PLAZA RIVE IS D DAV APEC 1 APEC 2 Google Earth APEC 5 NOTES: APEC Area of Potential Environmental Concern MACIVER DODGE APEC 7 SITE APEC 8 APEC 4 ET E E STR YONG APEC 9 APEC 3 LEGEND: GAS BAR PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL SITE LOCATION: 17645 YONGE STREET, NEWMARKET FIGURE TITLE: AREAS OF POTENTIAL ENVIRONMENTAL CONCERN UPPER CANADA MALL REV NO.: 0 CANADIAN TIRE FILE NO.: 11-10-5203 SCALE: As Shown 0 SCALE 50 100m DATE: September 2013 FIGURE NO.: 2 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 KEY MAP SITE REFERENCE: NOTES: LEGEND: PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL SITE LOCATION: 17645 YONGE STREET, NEWMARKET FIGURE TITLE: SURVEY PLAN REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 3 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 BH 4 MW 3 BH 2 KEY MAP MW 1 SITE MW 32 REFERENCE: BH 6 NOTES: MW 31 BH 24 MW 7 MW 101 BH 23 BH 15 MW 21 BH 22 Concrete Block Building. Slessor Motors Dealership MW 102 MW 5 BH 102 BH 16 MW 19 LEGEND: MW1-14 MW 25 Borehole (2010) BH 103 MW 8-2 Monitoring Well Location MW 20 MW2-14 MW 27 MW 8-1 Borehole (2013) BH 17 Borehole/Monitoring Well (2014) MW 106 BH 18 MW 106 MW 10 MW 4-12 BH 104 MW 11 MW3-14 MW 29-1 BH 105 PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL SITE LOCATION: MW 29-2 17645 YONGE STREET, NEWMARKET MW 9-2 MW 9-1 FIGURE TITLE: BOREHOLE LOCATION PLAN REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown 0 SCALE 5 10 15 20m DATE: November 2014 FIGURE NO.: 4 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 BH 4 MW 3 BH 2 KEY MAP MW 1 SITE MW 32 REFERENCE: BH 6 NOTES: MW 31 BH 23 BH 15 MW 21 BH 22 MW 7 MW 101 Concrete Block Bu ildin Slessor M g. otors Dealersh ip BH 24 MW 102 MW 5 BH 16 MW 19 LEGEND: MW1-14 MW 25 Borehole Location MW 8-2 Monitoring Well Location MW 20 MW2-14 MW 27 MW 8-1 BH 17 BH 18 MW 106 MW 10 MW 4-12 BH 104 Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 5,6,.dwg, SK MW 11 MW3-14 PROJECT TITLE: MW 29-1 PHASE TWO CONCEPTUAL SITE MODEL MW 29-2 SITE LOCATION: MW 9-2 MW 9-1 17645 YONGE STREET, NEWMARKET FIGURE TITLE: SOIL EXCEEDANCES REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown 0 SCALE 5 10 15 20m DATE: November 2014 FIGURE NO.: 5 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 BH 4 MW 3 BH 2 KEY MAP MW 1 SITE MW 32 REFERENCE: BH 6 NOTES: MW 31 BH 23 BH 15 MW 21 BH 22 MW 7 MW 101 Concrete Block Bu ildin Slessor M g. otors Dealersh ip BH 24 MW 102 MW 5 BH 16 MW1-14 MW 19 MW 25 LEGEND: Borehole Location MW 8-2 MW 20 Monitoring Well Location MW2-14 MW 27 MW 8-1 BH 17 BH 18 MW 106 MW 10 MW 4-12 BH 104 MW 11 MW3-14 PROJECT TITLE: MW 29-1 PHASE TWO CONCEPTUAL SITE MODEL SITE LOCATION: MW 29-2 17645 YONGE STREET, NEWMARKET MW 9-2 MW 9-1 FIGURE TITLE: GROUND WATER EXCEEDANCES REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown 0 SCALE 5 10 15 20m DATE: November 2014 FIGURE NO.: 6 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 11 Indell Lane - Brampton Ontario L6T 3Y3 (905) 796-2650 KEY MAP BH 4 MW 3 BH 2 MW 1 SITE MW 32 REFERENCE: NOTES: Forrest Group Site Block Plan Slessor Square Proposed Retirement Community 17645 Yonge Street, Newmarket Project No. 1507 Date: 09/05/12 BH 6 MW 31 Impact Area 2 BH 24 BH 23 MW 7 Remedial Excavation Area MW 101 BH 15 MW 102 MW 5 MW 21 BH 22 Remedial Excavation Area Impact Area 1 LEGEND: Site Boundary BH 16 Excavated for Soil Remediation MW 19 MW1-14 MW 25 Borehole Location MW 8-2 Monitoring Well Location MW 20 MW2-14 MW 27 MW 12 MW 8-1 BH 17 BH 18 MW 10 Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 7,8,9,10.dwg, SK MW 4-12 MW 106 PROJECT TITLE: BH 104 PHASE TWO CONCEPTUAL SITE MODEL MW 11 Impact Area 3 MW3-14 SITE LOCATION: 17645 YONGE STREET, NEWMARKET MW 29-1 MW 29-2 Remedial Excavation Area FIGURE TITLE: EXCAVATION AREAS MW 9-2 MW 9-1 REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown 0 SCALE 5 10 15 20m DATE: November 2014 FIGURE NO.: 7 SA078 1.8 m Result SA079 Standard 2.4 m Result Excav 2 N3a Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs F1 PHCs F2 PHCs F3 PHCs F4 PHCs SA080 2.4 m Result Standard Excav 2 N3b Excav2N3a SA104 3m Result Sa078 BH Sa079 Sa080 Sa077 Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs 3m Result 16 Excav2N3b MW 19 MW1-14 REFERENCE: 3m Result Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs Excav 2 Floor8 NOTES: 5m Result 2m Result Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs MW 20 Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs SA106 3m Result Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs SA102 BH 17 SA103 F1 PHCs F2 PHCs F3 PHCs F4 PHCs Excav 2 Floor13 5m Result 3m Result Standard BH 18 F1 PHCs F2 PHCs F3 PHCs F4 PHCs SA100 Excav 2 S1b F1 PHCs F2 PHCs F3 PHCs F4 PHCs 3m Result Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs MW F1F28-2 PHCs PHCs 1.5 m Result Standard 2.8 m Result Standard LEGEND: Site Boundary F3 PHCs F4 PHCs RSC Property Excav 2 E2a Borehole Location 0.5 m Result MW 8-1 F1 PHCs Standard Monitoring Well Location F2 PHCs F3 PHCs F4 PHCs Sidewall Sample Location 1.8 m Result Floor Sample Location Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs Excav2 Floor 12 MW 10 Standard SA105 SA099 Excav2S1b 1.5 m Result F1 PHCs F2 PHCs F3 PHCs F4 PHCs Excav2 2B Sa104 Sa102 Sa105 Sa101 Excav2E2a Excav 2 Floor 2 MW2-14 Sa099 Sa106 Sa103 Excav2 Floor 13 Sa100 Forrest Group Site Block Plan Slessor Square Proposed Retirement Community 17645 Yonge Street, Newmarket Project No. 1507 Date: 09/05/12 Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs Standard SA101 5m Result SITE EXCAV 2 FLOOR 8 F1 PHCs F2 PHCs F3 PHCs F4 PHCs Excav 2 Floor2 KEY MAP Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs Excav 2 2b 11 Indell Lane - Brampton Ontario L6T 3Y3 (905) 796-2650 Remedial Excavation Area Impact Area 1 1.5 m Result Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs F1 PHCs F2 PHCs F3 PHCs F4 PHCs SA077 Terraprobe Inc. 0.5 m Result Cross Section Location PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL Excav 2 Floor12 5m Result SITE LOCATION: Standard 17645 YONGE STREET, NEWMARKET F1 PHCs F2 PHCs F3 PHCs F4 PHCs FIGURE TITLE: LOCATION OF CONFIRMATION SAMPLE IMPACT AREA 1 Standard REV NO.: 0 SCALE 5 10m 0 FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 8 SA009 Result Units Terraprobe Inc. Table 2 RPI MFT Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 11 Indell Lane - Brampton Ontario L6T 3Y3 (905) 796-2650 MW 31 Sample Type floor Benzene <0.02 0.17 Ethylbenzene <0.05 1.6 Toluene <0.08 6 Xylene (Total) <0.05 25 KEY MAP SITE F1 PHCs <5 65 F2 PHCs <10 150 F3 PHCs <50 1300 F4 PHCs <50 5600 REFERENCE: Impact Area 2 NOTES: BH 24 Sa009 BH 23 SA007 Result Units Sample Type 0.17 Ethylbenzene <0.05 1.6 Toluene <0.08 6 Xylene (Total) <0.05 25 <5 65 F1 PHCs F2 PHCs <10 150 F3 PHCs <50 1300 F4 PHCs <50 5600 SA003 Result Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 7,8,9,10.dwg, SK Units floor Benzene <0.02 0.17 Ethylbenzene <0.05 1.6 Toluene <0.08 6 Xylene (Total) <0.05 25 <5 65 F2 PHCs <10 SA008 Result Table 2 RPI MFT Units Sa008 MW 21 BH 22 Sa010 Sample Type wall LEGEND: Benzene <0.02 0.17 Ethylbenzene <0.05 1.6 Toluene <0.08 6 Xylene (Total) <0.05 25 F1 PHCs <5 65 F2 PHCs <10 150 F3 PHCs <50 1300 F4 PHCs <50 5600 Site Boundary RSC Property Borehole Location Monitoring Well Location Sidewall Sample Location Table 2 RPI MFT Sample Type F1 PHCs Sa007 Sa003 wall <0.02 MW 101 BH 15 Table 2 RPI MFT Benzene Remedial Excavation Area Forrest Group Site Block Plan Slessor Square Proposed Retirement Community 17645 Yonge Street, Newmarket Project No. 1507 Date: 09/05/12 Floor Sample Location Cross Section Location SA010 <50 1300 F4 PHCs <50 5600 Table 2 RPI MFT PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL Sample Type floor Benzene <0.02 0.17 Ethylbenzene <0.05 1.6 Toluene <0.08 6 Xylene (Total) <0.05 25 F1 PHCs <5 65 F2 PHCs <10 150 150 F3 PHCs Result Units F3 PHCs <50 1300 F4 PHCs <50 5600 SITE LOCATION: 17645 YONGE STREET, NEWMARKET FIGURE TITLE: LOCATION OF CONFIRMATION SAMPLE IMPACT AREA 2 REV NO.: 0 SCALE 5 10m 0 FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 9 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 11 Indell Lane - Brampton Ontario L6T 3Y3 (905) 796-2650 KEY MAP Floor 1 3m Result Nwall SA3 Standard 2.5 m Result Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs F1 PHCs F2 PHCs F3 PHCs F4 PHCs SITE MW 4-12 MW 106 REFERENCE: BH 104 NOTES: MW 11 Forrest Group Site Block Plan Slessor Square Proposed Retirement Community 17645 Yonge Street, Newmarket Project No. 1507 Date: 09/05/12 N Wall Sa3 Impact Area 3 Floor3 Floor1 Floor2 Floor 2 3m Result MW3-14 E Wall Sa2 Ewall SA2 Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs S Wall Sa2 Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs 1.5 m Result LEGEND: Floor 3 3m Result Standard Site Boundary F1 PHCs F2 PHCs F3 PHCs F4 PHCs Remedial Excavation Area RSC Property Borehole Location Monitoring Well Location Sidewall Sample Location Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 7,8,9,10.dwg, SK Floor Sample Location PROJECT TITLE: Swall SA2 2m Result PHASE TWO CONCEPTUAL SITE MODEL Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs SITE LOCATION: 17645 YONGE STREET, NEWMARKET FIGURE TITLE: LOCATION OF CONFIRMATION SAMPLE IMPACT AREA 3 REV NO.: 0 0 SCALE 5 10m FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 10 SA100 Silty Clay Silt Sa103 Elevation (m) BH 8 MW1-14 MW19 264 Sa100 262 Sa099 REFERENCE: Sa106 260 Silt Silty Clay Till 258 256 256 Glacial Till 5m Result Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs 254 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 NOTES: Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs Excav 2 Floor13 Standard KEY MAP Fill Impact Area1 Excavated Area Excav 2 Floor 13 258 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing SITE 260 3m Result 1.8 m Result Fill 262 SA103 SA099 F1 PHCs F2 PHCs F3 PHCs F4 PHCs BH 103/MW 106 MW2-14 BH 11/MW20 BH 18 BH 17 Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs SECTION A-A' 264 1.5 m Result 254 SA106 3m Result Silt Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs 252 252 LEGEND: Fill 250 250 Glacial Till Glacial Till Silt 248 Stabilized water level 248 Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 1,2,3,4,11,12,13.dwg, SK Sample Location 246 246 PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL 244 244 0 10 20 30 40 50 Distance Along A-A' Baseline (m) 60 70 80 SITE LOCATION: 17645 YONGE STREET, NEWMARKET FIGURE TITLE: CROSS SECTION A-A' IMPACT AREA 1 REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 11 SA009 Result Terraprobe Inc. Table 2 RPI MFT Units Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing <0.05 1.6 Toluene <0.08 6 Xylene (Total) <0.05 25 F1 PHCs <5 65 F2 PHCs <10 150 F3 PHCs <50 1300 F4 PHCs <50 5600 264 Fill Sa009 262 Silt 260 KEY MAP south SITE 266 Sa010 Fill 262 Silt 260 REFERENCE: NOTES: Glacial Till 258 Elevation (m) 264 APEC 3 Excavated Area Sa003 Silt 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 BH 25 Ethylbenzene SECTION B-B' BH 22 0.17 BH 15 MW 21 Benzene BH 24 BH 32 BH 2 266 floor <0.02 50 mm monitoring well north Sample Type 258 SA010 Result Units 256 Table 2 RPI MFT Sample Type floor Benzene <0.02 0.17 254 Ethylbenzene <0.05 1.6 Toluene <0.08 6 Xylene (Total) <0.05 25 252 F1 PHCs <5 65 F2 PHCs <10 150 F3 PHCs <50 1300 F4 PHCs <50 5600 Glacial Till Silt Silt 250 256 254 252 LEGEND: Fill 250 Glacial Till SA003 Result Units 248 Glacial Till Glacial Till Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 1,2,3,4,11,12,13.dwg, SK 246 244 242 0 10 20 30 40 50 60 Distance Along B-B' Baseline (m) 70 Table 2 RPI MFT Sample Type floor Benzene <0.02 0.17 Ethylbenzene <0.05 1.6 Toluene <0.08 6 Xylene (Total) <0.05 25 F1 PHCs <5 65 F2 PHCs <10 150 F3 PHCs <50 1300 F4 PHCs <50 5600 80 Silt 248 Stabilized water level 90 Sample Location 246 244 PROJECT TITLE: 242 SITE LOCATION: PHASE TWO CONCEPTUAL SITE MODEL 17645 YONGE STREET, NEWMARKET 100 FIGURE TITLE: CROSS SECTION B-B' IMPACT AREA 2 REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 12 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 KEY MAP SECTION C-C' Northwest Floor 1 MW 11 E Wall SA 2 APEC4 Excavated Area Fill MW3-14 BH 104 MW 4-12 264 262 Floor 3 264 Fill Fill 262 REFERENCE: Former UST 260 Silt Silt 260 NOTES: Silt Elevation (m) 258 258 Glacial Till 256 Floor 1 254 SITE Southeast 3m Result 256 Glacial Till Ewall SA2 Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs 1.5 m Result Standard F1 PHCs F2 PHCs F3 PHCs F4 PHCs 254 252 252 Floor 3 3m Result Fill Standard Silt F1 PHCs F2 PHCs F3 PHCs F4 PHCs 250 LEGEND: Silt Glacial Till 250 Silt Sample Location 248 248 Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 1,2,3,4,11,12,13.dwg, SK Glacial Till Floor Location Glacial Till 246 246 PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL 244 244 0 2 4 6 8 10 12 Distance Along C-C' Baseline (m) 14 16 18 SITE LOCATION: 20 17645 YONGE STREET, NEWMARKET FIGURE TITLE: CROSS SECTION C-C' IMPACT AREA 3 REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 13 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 BH 4 MW 3 BH 2 KEY MAP MW 1 SITE MW 32 MW101 8-May-13 25-Sep-13 Result Result REFERENCE: Standard F1 PHCs F2 PHCs F3 PHCs <1 F4 PHCs <1 MW1-14 23-Jan-14 24-Apr-14 Result Result Standard BH 6 F1 PHCs NOTES: F2 PHCs MW 31 F3 PHCs MW102 F4 PHCs 25-Apr-13 25-Sep-13 Result Result Standard F1 PHCs MW 7 BH 24 F2 PHCs MW 101 BH 23 BH 15 MW 21 Concrete Block Building. Slessor Motors Dealership BH 22 MW 102 F3 PHCs <1 F4 PHCs <1 MW 5 BH 102 Remedial Excavation Area BH 16 MW 19 LEGEND: MW1-14 MW 25 Borehole (2010) BH 103 MW 8-2 Monitoring Well Location MW 20 MW2-14 MW 8-1 Borehole (2013) BH 17 MW 27 MW8-1 MW2-14 23-Jan-14 24-Apr-14 Result Result Result Result F2 PHCs MW 10 MW 4-12 Borehole/Monitoring Well (2014) Standard F1 PHCs MW 106 F1 PHCs F2 PHCs 25-Sep-13 MW 106 BH 18 Standard 25-Apr-13 BH 104 F3 PHCs <1 F4 PHCs <1 Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 1,2,3,4,11,12,13.dwg, SK F3 PHCs MW 11 F4 PHCs MW3-14 MW 29-1 BH 105 MW3-14 24-Apr-14 Result F4 PHCs 25-Sep-13 Result Result PHASE TWO CONCEPTUAL SITE MODEL Standard F2 PHCs F2 PHCs F3 PHCs 8-May-13 F1 PHCs Standard F1 PHCs MW 29-2 PROJECT TITLE: MW106 MW 9-2 F3 PHCs <1 F4 PHCs <1 SITE LOCATION: 17645 YONGE STREET, NEWMARKET MW 9-1 FIGURE TITLE: POST REMEDIATION GROUND WATER APEC 1, 2, 5 REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown 0 SCALE 5 10 15 20m DATE: November 2014 FIGURE NO.: 14 Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 KEY MAP SITE The is a visual representation of potential pathways and receptors. This drawing is only intended to represent the components in a graphic format and does not have a specific orientation or scale which can be related to the Phase Two Property. As such this drawing does not have a scale or north arrow. Complete descriptions of the components are provided in the Conceptual Site Model. S1- Residential S2- Commercial / Industrial S3- Worker Digging REFERENCE: NOTES: Surface water not located on site. Fill Material Birds & Mammals Plants & Soil Organisms Contaminated Fill Material S-Odour S-OA S-IA Native Soil Contaminated Native Soil LEGEND: S-GW1 S-GW3 Surface Water Ground Water Table Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 1,2,3,4,11,12,13.dwg, SK Contaminated Ground Water GW3 GW1 GW3 PROJECT TITLE: Bedrock PHASE TWO CONCEPTUAL SITE MODEL SITE LOCATION: 17645 YONGE STREET, NEWMARKET FIGURE TITLE: PATHWAYS AND RECEPTORS REV NO.: 0 FILE NO.: 11-10-5203 SCALE: NTS DATE: November 2014 FIGURE NO.: 15 MW1-14 23-Jan-14 24-Apr-14 Result Result Terraprobe Inc. Consulting Geotechnical & Environmental Engineering Construction Materials, Inspection & Testing Standard F1 PHCs 10 Bram Court - Brampton Ontario L6W 3R6 (905) 796-2650 F2 PHCs F3 PHCs BH 103/MW 106 MW8-1 25-Apr-13 25-Sep-13 Result Result Standard F1 PHCs MW1-14 MW19 SITE F2 PHCs BH 8 BH 17 264 KEY MAP F4 PHCs MW2-14 BH 18 BH 11/MW20 SECTION A-A' F3 PHCs <1 F4 PHCs <1 264 Fill Silt Silty Clay Fill Impact Area1 Excavated Area 262 Sa103 Sa100 262 Sa099 REFERENCE: Sa106 260 260 Silt Excav 2 Floor 13 NOTES: MW2-14 258 23-Jan-14 24-Apr-14 Result Result Silty Clay Till Standard F1 PHCs 258 F2 PHCs F3 PHCs Elevation (m) F4 PHCs 256 MW106 8-May-13 25-Sep-13 Result Result 256 Glacial Till Standard F1 PHCs F2 PHCs 254 F3 PHCs <1 F4 PHCs <1 254 Silt 252 252 LEGEND: Fill 250 250 Glacial Till Glacial Till Silt 248 Stabilized water level 248 Z:\1-Project Files\11-Geo\2010\1-10-5200 to 5299\1-10-5203\A. Dwgs, Logs\AutoCAD\11-10-5203 Revision (Sept. 2013)\RSC Try 4 Try 5\11-10-5203 FIG 1,2,3,4,11,12,13.dwg, SK Sample Location 246 246 PROJECT TITLE: PHASE TWO CONCEPTUAL SITE MODEL 244 244 0 10 20 30 40 50 Distance Along A-A' Baseline (m) 60 70 80 SITE LOCATION: 17645 YONGE STREET, NEWMARKET FIGURE TITLE: POST REMEDIATION GROUND WATER CROSS SECTION A-A' APEC 1, 2, 5 REV NO.: 0 FILE NO.: 11-10-5203 SCALE: As Shown DATE: November 2014 FIGURE NO.: 16 APPENDIX A TERRAPROBE INC. PHASE ONE PROPERTY PHASE TWO PROPERTY RSC PROPERTY APPENDIX B TERRAPROBE INC.