Ontario Ministry of the Environment - Record of Site Condition #

Transcription

1 Ontario Ministry of the Environment - Record of Site Condition # 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 2014/08/28 Certification Date 2013/12/27 Current Property Use Residential Intended Property Use Residential Certificate of Property Use Number No CPU Applicable Site Condition Standards** Full Depth Generic Site Conditions Standard, with Potable Ground Water, Coarse Textured Soil, for Residential property use Property Municipal Address 95 MORNING CALM DRIVE, CAMBRIDGE, ON, N1R 8H7, 350 DUNDAS STREET SOUTH, CAMBRIDGE, ON, N1R 5S2, 360 DUNDAS STEET SOUTH, CAMBRIDGE, ON, N1R 5S2 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. Filed Record of Site Condition # on 2014/08/28 1 of 19

2 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 Authorized Person Mailing Address Postal Code FREURE BLAIR CROSSING LIMITED DAVID FREURE 501 KRUG STREET, SUITE 201, KITCHENER ONTARIO, CANADA N2B 1L3 Phone (519) Fax (519) Address Filed Record of Site Condition # on 2014/08/28 2 of 19

3 RSC Property Location Information Municipal Address(es) Municipality Legal Description Assessment Roll Number(s) 350 DUNDAS STREET SOUTH, CAMBRIDGE, ON N1R 5S2 360 DUNDAS STEET SOUTH, CAMBRIDGE, ON N1R 5S2 95 MORNING CALM DRIVE, CAMBRIDGE, ON N1R 8H7 Cambridge See Attached Lawyer s Letter Property Identifier Number(s) (LT) (LT) (LT) RSC Property Geographical References Coordinate System UTM Datum NAD 83 Zone 17 Easting 557, Northing 4,800, 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 Intended Property Use Certificate of Property Use has been issued under section of the EPA Residential Residential No Filed Record of Site Condition # on 2014/08/28 3 of 19

4 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 # on 2014/08/28 4 of 19

5 PART 2: LIST OF REPORTS, SUMMARY OF SITE CONDITIONS AND QUALIFIED PERSON S STATEMENTS AND CERTIFICATIONS Qualified Person's Information Name Type of Licence Under Professional Engineers Act MICHAEL L DUCHENE Licence Licence Number QP Employer Name Mailing Address BLUMETRIC ENVIRONMENTAL INC. 171 VICTORIA STREET NORTH, KITCHENER ONTARIO, N2H 5C5 CANADA Phone (519) Fax (519) Address mduchene@wesa.ca Municipal Information Local or Single-Tier Municipality Upper-Tier Municipality Cambridge Waterloo Ministry of the Environment District Office District Office District Office Address Guelph District Office 1 Stone Road W., Guelph ON N1G 4Y2 Filed Record of Site Condition # on 2014/08/28 5 of 19

6 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) 2014/08/21 Type of Report Report Title Date of Report (YYYY/MM/DD) Author of Report Name of Consulting Company P1 ESA Phase One Environmental Site Asessment, 350 Dundas Street South, Cambridge, ON 2014/08/21 Michael Duchene, Melanie Bombini, Melonie MacLaughlin BLUMETRIC ENVIRONMENTAL 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 Phase I Environmental Site Assessment, Freure Homes, 350 Dundas Street South, Cambridge, ON (Draft) Date of Report (YYYY/MM/DD) Author of Report Name of Consulting Company 2011/04/09 Tanya Shanoff Stantec Consulting Ltd. Filed Record of Site Condition # on 2014/08/28 6 of 19

7 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) (YYYY/MM/DD) 2013/12/27 Type of Report Report Title Date of Report (YYYY/MM/DD) Author of Report Name of Consulting Company P2 ESA Phase Two Environmental Site Assessment, 350 Dundas Street South, Cambridge, ON 2014/08/21 Michael Duchene, Melonie Bombini, Melanie MacLaughlin BLUMETRIC ENVIRONMENTAL 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 # on 2014/08/28 7 of 19

8 Environmental Condition Section 41 applies? Section 43.1 applies? No No Site Condition Information Certification date (YYYY/MM/DD) 2013/12/27 Total area of RSC property (in hectares) 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 Assessment/Restoration Approach Site investigation includes the investigation, sampling and analysis of ground water? 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? Site investigation includes the investigation, sampling and analysis of soil on, in or under the property which is used in the RSC? Name of the laboratory used to analyze any samples collected of soil, ground water or sediment Ground water condition (potable, non-potable) Coarse Full Depth Generic Yes Yes Yes MAXXAM ANALYTICS Potable Applicable Site Condition Standard TABLE 2 Filed Record of Site Condition # on 2014/08/28 8 of 19

9 Table 1 Maximum Contaminant Concentrations Compared to Applicable Site Condition Standards Measured Concentration for Contaminants in Soil Contaminant Name Maximum Concentration Applicable Site Condition Standard Unit of Measure 1 Acenaphthene µg/g 2 Acenaphthylene µg/g 3 Anthracene µg/g 4 Benz[a]anthracene µg/g 5 Benzo[a]pyrene µg/g 6 Benzo[b]fluoranthene µg/g 7 Benzo[ghi]perylene µg/g 8 Benzo[k]fluoranthene µg/g 9 Chrysene µg/g 10 Dibenz[a h]anthracene µg/g 11 Fluoranthene µg/g 12 Fluorene µg/g 13 Indeno[1 2 3-cd]pyrene µg/g 14 Methlynaphthalene, 2-(1-) *** µg/g 15 Naphthalene µg/g 16 Phenanthrene µg/g 17 Pyrene µg/g 18 Petroleum Hydrocarbons F2 < µg/g 19 Petroleum Hydrocarbons F µg/g 20 Petroleum Hydrocarbons F µg/g 21 Antimony µg/g 22 Arsenic µg/g 23 Barium µg/g 24 Beryllium µg/g 25 Boron (total) µg/g 26 Cadmium µg/g 27 Chromium Total µg/g 28 Cobalt µg/g 29 Copper µg/g 30 Lead µg/g 31 Molybdenum µg/g 32 Nickel µg/g 33 Selenium < µg/g 34 Silver < µg/g 35 Thallium µg/g 36 Uranium µg/g 37 Vanadium µg/g 38 Zinc µg/g 39 Mercury µg/g Filed Record of Site Condition # on 2014/08/28 9 of 19

10 39 Mercury µg/g 40 Sodium Adsorption Ratio Chromium VI < µg/g 42 Electrical Conductivity ms/cm 43 Cyanide (CN-) < µg/g 44 Boron (Hot Water Soluble)* µg/g 45 Benzene < µg/g 46 Toluene < µg/g 47 Ethylbenzene < µg/g 48 Xylene Mixture < µg/g 49 Petroleum Hydrocarbons F1**** < µg/g 50 Acetone µg/g 51 Bromodichloromethane < µg/g 52 Bromoform < µg/g 53 Bromomethane < µg/g 54 Carbon Tetrachloride < µg/g 55 Chlorobenzene < µg/g 56 Chloroform < µg/g 57 Dibromochloromethane < µg/g 58 Dichlorobenzene, 1,2- < µg/g 59 Dichlorobenzene, 1,3- < µg/g 60 Dichlorobenzene, 1,4- < µg/g 61 Dichlorodifluoromethane < µg/g 62 Dichloroethane, 1,1- < µg/g 63 Dichloroethane, 1,2- < µg/g 64 Dichloroethylene, 1,1- < µg/g 65 Dichloroethylene, 1,2-cis- < µg/g 66 Dichloroethylene, 1,2-trans- < µg/g 67 Dichloropropane, 1,2- < µg/g 68 Dichloropropene,1,3- < µg/g 69 Ethylene dibromide < µg/g 70 Hexane (n) µg/g 71 Methyl Ethyl Ketone < µg/g 72 Methyl Isobutyl Ketone < µg/g 73 Methyl tert-butyl Ether (MTBE) < µg/g 74 Methylene Chloride < µg/g 75 Styrene < µg/g 76 Tetrachloroethane, 1,1,1,2- < µg/g 77 Tetrachloroethane, 1,1,2,2- < µg/g 78 Tetrachloroethylene < µg/g 79 Trichloroethane, 1,1,1- < µg/g 80 Trichloroethane, 1,1,2- < µg/g 81 Trichloroethylene < µg/g 82 Trichlorofluoromethane < µg/g Filed Record of Site Condition # on 2014/08/28 10 of 19

11 81 Trichloroethylene < µg/g 82 Trichlorofluoromethane < µg/g 83 Vinyl Chloride < µg/g Filed Record of Site Condition # on 2014/08/28 11 of 19

12 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 Benzene < µg/l 2 Toluene µg/l 3 Ethylbenzene < µg/l 4 Xylene Mixture < µg/l 5 Petroleum Hydrocarbons F1**** < µg/l 6 Petroleum Hydrocarbons F2 < µg/l 7 Petroleum Hydrocarbons F3 < µg/l 8 Petroleum Hydrocarbons F4 < µg/l 9 Chromium VI < 5 25 µg/l 10 Mercury < µg/l 11 Antimony < µg/l 12 Arsenic < 1 25 µg/l 13 Barium µg/l 14 Beryllium < µg/l 15 Boron (total) µg/l 16 Cadmium < µg/l 17 Chromium Total < 5 50 µg/l 18 Cobalt < µg/l 19 Copper µg/l 20 Lead µg/l 21 Molybdenum µg/l 22 Nickel µg/l 23 Selenium < 2 10 µg/l 24 Silver < µg/l 25 Sodium 10, µg/l 26 Thallium < µg/l 27 Uranium µg/l 28 Vanadium µg/l 29 Zinc µg/l 30 Acenaphthene < µg/l 31 Acenaphthylene < µg/l 32 Anthracene < µg/l 33 Benz[a]anthracene < µg/l 34 Benzo[a]pyrene < µg/l 35 Benzo[b]fluoranthene < µg/l 36 Benzo[ghi]perylene < µg/l 37 Benzo[k]fluoranthene < µg/l 38 Chrysene < µg/l 39 Dibenz[a h]anthracene < µg/l Filed Record of Site Condition # on 2014/08/28 12 of 19

13 39 Dibenz[a h]anthracene < µg/l 40 Fluoranthene < µg/l 41 Fluorene < µg/l 42 Indeno[1 2 3-cd]pyrene < µg/l 43 Methlynaphthalene, 2-(1-) *** < µg/l 44 Naphthalene < µg/l 45 Phenanthrene < µg/l 46 Pyrene < µg/l 47 Acetone < µg/l 48 Bromodichloromethane < µg/l 49 Bromoform < µg/l 50 Bromomethane < µg/l 51 Carbon Tetrachloride < µg/l 52 Chlorobenzene < µg/l 53 Chloroform < µg/l 54 Dibromochloromethane < µg/l 55 Dichlorobenzene, 1,2- < µg/l 56 Dichlorobenzene, 1,3- < µg/l 57 Dichlorobenzene, 1,4- < µg/l 58 Dichlorodifluoromethane < µg/l 59 Dichloroethane, 1,1- < µg/l 60 Dichloroethane, 1,2- < µg/l 61 Dichloroethylene, 1,1- < µg/l 62 Dichloroethylene, 1,2-cis- < µg/l 63 Dichloroethylene, 1,2-trans- < µg/l 64 Dichloropropane, 1,2- < µg/l 65 Dichloropropene,1,3- < µg/l 66 Ethylene dibromide < µg/l 67 Hexane (n) < µg/l 68 Methylene Chloride < µg/l 69 Methyl Isobutyl Ketone < µg/l 70 Methyl Ethyl Ketone < µg/l 71 Methyl tert-butyl Ether (MTBE) < µg/l 72 Styrene < µg/l 73 Tetrachloroethane, 1,1,1,2- < µg/l 74 Tetrachloroethane, 1,1,2,2- < µg/l 75 Tetrachloroethylene < µg/l 76 Trichloroethane, 1,1,1- < µg/l 77 Trichloroethane, 1,1,2- < µg/l 78 Trichloroethylene < µg/l 79 Vinyl Chloride < µg/l 80 Trichlorofluoromethane < µg/l Filed Record of Site Condition # on 2014/08/28 13 of 19

14 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 Estimated Quantity of Soil (in-ground volume in m³) None Description of Remediation Description of any action taken to reduce the concentration of contaminants (including soil removals) on, in or under the RSC property. Soil excavated and removed from site. A total of 14, tonnes was disposed of off site. 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) 6,780.0 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) 0.0 Filed Record of Site Condition # on 2014/08/28 14 of 19

15 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. None 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) 0.0 Filed Record of Site Condition # on 2014/08/28 15 of 19

16 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. None 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. None 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. None 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. None 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? Yes Filed Record of Site Condition # on 2014/08/28 16 of 19

17 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 2013/12/27, 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 2013/12/27, 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 2013/12/27, 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 BLUMETRIC ENVIRONMENTAL 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 2013/12/27. 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, MICHAEL L DUCHENE, a qualified person as defined in section 5 of O. Reg. 153/04 am, on 2014/08/25: 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 # on 2014/08/28 17 of 19

18 Additional Documentation Provided by Property Owner or Agent The following documents have been submitted to the Ministry of the Environment 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 v Filed Record of Site Condition # on 2014/08/28 18 of 19

19 Filed Record of Site Condition # on 2014/08/28 19 of 19

20 Request ID: Province of Ontario Date Report Produced: 2014/08/08 Demande n : Province de l'ontario Document produit le : Transaction ID: Ministry of Government Services Time Report Produced: 09:29:06 Transaction n : Ministère des Services gouvernementaux Imprimé à : Category ID: CT Catégorie : CERTIFICATE OF STATUS ATTESTATION DU STATUT JURIDIQUE This is to certify that according to the records of the Ministry of Government Services D'après les dossiers du Ministère des Services gouvernementaux, nous attestons que la société F R E U R E B L A I R C R O S S I N G L I M I T E D Ontario Corporation Number Numéro matricule de la société (Ontario) is a corporation incorporated, amalgamated or continued under the laws of the Province of Ontario. The corporation came into existence on est une société constituée, prorogée ou née d'une fusion aux termes des lois de la Province de l'ontario. La société a été fondée le N O V E M B E R 1 6 N O V E M B R E, and has not been dissolved. et n'est pas dissoute. Dated Fait le A U G U S T 0 8 A O Û T, 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.

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23 LRO # 58 Transfer Registered as WR on at 14:53 The applicant(s) hereby applies to the Land Registrar. yyyy mm dd Page 1 of 3 Properties PIN LT Interest/Estate Fee Simple Description PT LT 5 CON 10 NORTH DUMFRIES PTS 1 & 4, 67R2634; S/T WS662858; CAMBRIDGE Address 350 DUNDAS ST S CAMBRIDGE Consideration Consideration Transferor(s) The transferor(s) hereby transfers the land to the transferee(s). Name HOLLINGS, BONNIE LYNN Address for Service 360 Dundas Street South, R. R. 1 Cambridge, ON N1R 5S2 I am at least 18 years of age. The property is not ordinarily occupied by me and my spouse, who is not separated from me, as our family residence. This document is not authorized under Power of Attorney by this party. Transferee(s) Capacity Share Name Address for Service FREURE BLAIR CROSSING LIMITED 501 Krug Street Suite 201 Kitchener, Ontario N2B 1L3 STATEMENT OF THE TRANSFEROR (S): The transferor(s) verifies that to the best of the transferor s knowledge and belief, this transfer does not contravene the Planning Act. STATEMENT OF THE SOLICITOR FOR THE TRANSFEROR (S): I have explained the effect of the Planning Act to the transferor(s) and I have made inquiries of the transferor(s) to determine that this transfer does not contravene that Act and based on the information supplied by the transferor(s), to the best of my knowledge and belief, this transfer does not contravene that Act. I am an Ontario solicitor in good standing. STATEMENT OF THE SOLICITOR FOR THE TRANSFEREE (S): I have investigated the title to this land and to abutting land where relevant and I am satisfied that the title records reveal no contravention as set out in the Planning Act, and to the best of my knowledge and belief this transfer does not contravene the Planning Act. I act independently of the solicitor for the transferor(s) and I am an Ontario solicitor in good standing. Signed By William Kurt Schwarz Water St. N. Cambridge N1R 7L6 acting for Transferor(s) Signed Tel Fax I am the solicitor for the transferor(s) and I am not one and the same as the solicitor for the transferee(s). I have the authority to sign and register the document on behalf of the Transferor(s). Andrew Douglas Robertson Graham 30 Duke Street West, Suite 1017 Kitchener N2H 3W5 Tel Fax acting for Transferee(s) I am the solicitor for the transferee(s) and I am not one and the same as the solicitor for the transferor(s). I have the authority to sign and register the document on behalf of the Transferee(s). Signed Submitted By ANDREW D. R. GRAHAM, BARRISTER & SOLICITOR 30 Duke Street West, Suite 1017 Kitchener N2H 3W Tel

24 LRO # 58 Transfer Registered as WR on at 14:53 The applicant(s) hereby applies to the Land Registrar. yyyy mm dd Page 2 of 3 Submitted By Fax Fees/Taxes/Payment Statutory Registration Fee $60.00 Provincial Land Transfer Tax Total Paid File Number Transferor Client File Number :

25 LAND TRANSFER TAX STATEMENTS In the matter of the conveyance of: PT LT 5 CON 10 NORTH DUMFRIES PTS 1 & 4, 67R2634; S/T WS662858; CAMBRIDGE BY: TO: HOLLINGS, BONNIE LYNN FREURE BLAIR CROSSING LIMITED 1. DAVID FREURE I am (a) A person in trust for whom the land conveyed in the above described conveyance is being conveyed; (b) A trustee named in the above described conveyance to whom the land is being conveyed; (c) A transferee named in the above described conveyance; (d) The authorized agent or solicitor acting in this transaction for described in paragraph(s) (_) above. (e) The President, Vice President, Manager, Secretary, Director, or Treasurer authorized to act for FREURE BLAIR CROSSING LIMITED described in paragraph(s) (c) above. (f) A transferee described in paragraph() and am making these statements on my own behalf and on behalf of who is my spouse described in paragraph(_) and as such, I have personal knowledge of the facts herein deposed to. 2. I have read and considered the definition of "single family residence" set out in subsection 1(1) of the Act. The land being conveyed herein: contains at least one and not more than two single family residences. 3. The total consideration for this transaction is allocated as follows: (a) Monies paid or to be paid in cash (b) Mortgages (i) assumed (show principal and interest to be credited against purchase price) 0.00 (ii) Given Back to Vendor (c) Property transferred in exchange (detail below) 0.00 (d) Fair market value of the land(s) 0.00 (e) Liens, legacies, annuities and maintenance charges to which transfer is subject 0.00 (f) Other valuable consideration subject to land transfer tax (detail below) 0.00 (g) Value of land, building, fixtures and goodwill subject to land transfer tax (total of (a) to (f)) (h) VALUE OF ALL CHATTELS items of tangible personal property 0.00 (i) Other considerations for transaction not included in (g) or (h) above 0.00 (j) Total consideration PROPERTY Information Record A. Nature of Instrument: Transfer LRO 58 Registration No. WR Date: 2013/06/27 B. Property(s): PIN Address 350 DUNDAS ST S CAMBRIDGE C. Address for Service: 501 Krug Street Suite 201 Kitchener, Ontario N2B 1L3 D. (i) Last Conveyance(s): PIN Registration No. WR Assessment Roll No (ii) Legal Description for Property Conveyed: Same as in last conveyance? Yes No Not known E. Tax Statements Prepared By: Andrew Douglas Robertson Graham 30 Duke Street West, Suite 1017 Kitchener N2H 3W5

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35 Table of Areas of Potential Environmental Concern Area of Potential Environmental Concern 1. Imported fill of unknown origin 2. Potential heating oil UST or AST 3. Maintenance of equipment on adjacent property to the north. Location of Area of Potential Environmental Concern on Phase One Property Central portion of phase two property Rear (southwest) of residential home on eastern portion of property (fill pipe). Area along northwest property boundary south of the southern corner of the building on adjacent property to the north. Potentially Contaminating Activity 30. Importation of Fill Material of Unknown Quality 28. Gasoline and Associated Products Storage in Fixed Tanks 52. Storage, maintenance, fuelling and repair of equipment, vehicles and material used to maintain transportation Notes: PHC - petroleum hydrocarbon fractions F1 to F4, including benzene, toluene, ethylbenzene, xylenes VOC - volatile organic compounds PAH - polycyclic aromatic hydrocarbons AST - above ground storage tank UST - underground storage tank Location of PCA (on-site or off-site) On-site Contaminants of Potential Concern PHC, Metals, PAH Media Potentially Impacted (ground water, soil and/or sediment) Soil, groundwater On-site PHC, PAH Soil, groundwater Off-site PHC, PAH Soil

36 Table of Current and Past Uses of the RSC Property Year(s) Name of Owner Description of Property Use 350 and 360 Dundas Street South Property Use Other Observations from Aerial Photographs, Fire Insurance Plans, Etc William Dickson Assumed agricultural Agricultural or other use No aerial photographs available Walter Hamilton Assumed agricultural Agricultural or other use No aerial photographs available. Dickson William McMillan Assumed agricultural Agricultural or other use No aerial photographs available James McMillan Assumed agricultural Agricultural or other use No aerial photographs available John McNaughton Assumed agricultural Agricultural or other use No aerial photographs available James McMillan Assumed agricultural Agricultural or other use No aerial photographs available Henry Horton and Sarah Horton Assumed agricultural Agricultural or other use No aerial photographs available The Director of the Veterans Land Act Clemens St. Clair and Audrey St. Clair Assumed agricultural Agricultural or other use 1945 and 1955 aerial photographs show agricultural land use. Residential Residential No aerial photographs available.

37 Year(s) Name of Owner Description of Property Use 350 Dundas Street South Clemens St. Clair and Audrey St. Clair June 2013 June 2013 Audrey St. Clair (till 2010), Bonnie Hollings, Brian St. Clair (till 2013) Freure Blair Crossing Limited Portion of 360 Dundas Street South July 2014 July 2014 Kenyon Hollings, Bonnie Hollings Freure Blair Crossing Limited Property Use Other Observations from Aerial Photographs, Fire Insurance Plans, Etc. Residential Residential 1993 aerial photo shows single family home on property adjacent to Dundas Street South as well as earthworks being completed on property to the south and on RSC property. 2000, 2003, 2006 and 2009 aerial photos shows property site generally as it was in Residential Residential No aerial photographs available. Residential redevelopment (townhomes) Residential No aerial photographs available. Residential Residential 1993 aerial photo shows single family home on property adjacent to Dundas Street South as well as earthworks being completed on property to the south and on 350 Dundas property. 2000, 2003, 2006 and 2009 aerial photos shows property generally as it was in Residential Residential No aerial photographs available. redevelopment (townhomes)

38 Year(s) Name of Owner Description of Property Use Property Use Other Observations from Aerial Photographs, Fire Insurance Plans, Etc. Portion of 95 Morning Calm Drive Prior to George Schultz Assumed agricultural Agricultural or other use No aerial photographs available. December 1949 December 1949 November 1979 David C. Beattie Assumed agricultural Agricultural or other use No aerial photographs available. November 1979 March 1990 August 1990 March 1993 March 1993 July 2014 July 2014 David S. Beattie, Dorothy Lee, Robert Beattie, Kenneth Beattie, Jean Morby Ontario Inc. in Trust Lusitania Villas of Cambridge Incorporated Freure Blair Crossing Limited Assumed agricultural Agricultural or other use 1945 and 1955 aerial photographs show agricultural land use. Assumed agricultural Agricultural or other use No aerial photographs available. Townhome development Residential Residential redevelopment (townhomes) Residential 1993 aerial photo shows earthworks being completed on property. 2000, 2003, 2006 and 2009 aerial photos shows property generally as it was in No aerial photographs available.

39 Phase Two Conceptual Site Model 350 Dundas Street South, Cambridge, Ontario PHASE TWO CONCEPTUAL SITE MODEL The phase two conceptual site model makes reference to the following figures: Figure 1 Phase One Conceptual Site Model Figure 2 Areas of Potential Environmental Concern Figure 3 Test Pit, Borehole and Monitoring Well Location Plan Figure 4 Cross Section A A Figure 5 Cross Section B B Figure 6 Ground Water Elevation Map Figure 7 Soil Analytical Results for Contaminants of Concern Figure 8 Limits of Excavation - Cross Section A A Figure 9 Limits of Excavation - Cross Section B B Figure 10 Confirmation Soil Sampling Figure 11 Conceptual Exposure Model The phase two conceptual site model does not include figures to show the following types of information for the following reasons: There is no figure which illustrates areas of natural significance or water bodies within 30 m of the subject property since there are no areas of natural significance or water bodies within 30 m of the subject property; There is no figure which illustrates contaminants in sediment because there is no sediment at the subject property. 1. PHYSICAL SETTING OF THE SUBJECT PROPERTY The phase two property originally consisted of one whole property and parts of two other properties. The municipal address for the larger whole property is 350 Dundas Street South, Cambridge, Ontario. The phase two property also includes portions of the properties at 95 Morning Calm Drive and 360 Dundas Street South. All three properties are collectively referred to as the phase two property. Figure 1 shows the phase two property. The property fronts on Dundas Street South and is located about 80 m southeast of the intersection of Franklin Boulevard and Dundas Street South. The 350 Dundas Street South property is approximately 1.1 ha in size, the portion of 95 Morning Calm Drive is approximately 0.1 ha in size, and the portion of 360 Dundas is approximately 0.03 ha in size, for a total area of 1.2 ha. The phase two property is located in an urban area. The property generally slopes in a southwesterly direction from a high of 293 m above sea level (asl) in the northeast corner to a low of 284 m asl in the southwest corner. There are no permanent water bodies on the property. 1

40 Phase Two Conceptual Site Model 350 Dundas Street South, Cambridge, Ontario There are no water bodies or areas of natural significance on the subject property or in a 30 m radius of the subject property. The nearest body of water is Moffat Creek located 180 m south of the southwest corner of the phase two property. 2. POTENTIALLY CONTAMINATING ACTIVITIES The locations of potentially contaminating activities (both on and off site) identified in the phase one ESA are illustrated in the Phase One Conceptual Site Model shown in Figure PCAS ON THE PHASE ONE, PHASE TWO AND RSC PROPERTY PCA No PCA Description Gasoline and Associated Products Storage in Fixed Tanks Importation of Fill Material of Unknown Quality PCA Location Possible fuel oil storage tank associated with heating system of former house Central portion of property PCAs as per O. Reg. 153/04, Schedule D, Table 2 Both of these PCAs were considered to be areas of potential environmental concern. 2.2 PCAS IN THE PHASE ONE STUDY AREA The following potentially contaminating activities have been identified in the phase one study area: PCA No. PCA Description PCA Location (relative to phase two property) 10. Commercial Autobody Shops Dundas Autobody, 450 Dundas Street (~ 120 m SE), Gasoline and Associated Products Storage in Fixed Tanks Operation of Dry Cleaning Equipment (where chemicals are used) Storage, maintenance, fueling and repair of equipment, vehicles and material used to maintain transportation Loblaws former retail fuel distribution, 200 Franklin Blvd (> 140 m N) Patel Cleaning, 200 Franklin Blvd (> 140 m N) E.M. Coleman Ltd., Milk Transport, 330 Dundas Street (immediately N) PCAs as per O. Reg. 153/04, Schedule D, Table 2 The properties and associated PCAs at 450 Dundas Street and 200 Franklin Blvd are not adjacent to the RSC property and the only potential for contamination on the RSC property would be groundwater flow from the properties to the RSC site. The groundwater flow direction confirmed in the Phase Two ESA confirms that these properties and associated PCAs are cross gradient and therefore there are no APECs associated with the offsite PCAs Nos. 10, 2

41 Phase Two Conceptual Site Model 350 Dundas Street South, Cambridge, Ontario 28 and 37. PCA No. 52, potential maintenance of equipment is considered to be an area of potential environmental concern. 2.3 AREAS OF POTENTIAL ENVIRONMENTAL CONCERN Areas of potential environmental concern identified at the phase two property are illustrated in Figure 2. The areas of potential environmental concern on the phase two property are as follows: APEC No. Potential Environmental Concern Area 1. Imported fill Central portion of property 2. Fuel oil storage associated with heating system for former house 3. Possible maintenance of vehicles on adjacent site to northwest of phase two property Rear (southwest) of former residential house on north eastern portion of property. Area along northwest property boundary south of the southern corner of the building on adjacent property to the north. Potentially Impacted Media Soil and ground water Soil and Ground water Soil Contaminants of Potential Concern PHC, PAHs, metals PHC, PAHs PHCs, PAHs 2.4 SUBSURFACE STRUCTURES AND UTILITIES ON PHASE TWO PROPERTY A single family residence was located on the property adjacent to Dundas Street South. This residence was demolished in October Underground utilities were limited to a water line and gas line connecting the residence to utilities on Dundas Street. Sanitary wastes were discharged to a concrete holding tank and this tank was removed in January No other subsurface structures or utilities were located on the phase two property. 2.5 STRATIGRAPHY The stratigraphy was investigated by the installation of boreholes, monitoring wells and test pits. A preliminary phase two environmental investigation included the installation of four boreholes with three of these completed as monitoring wells and the excavation of nine test pits. Additional phase two investigation involved the installation of three additional boreholes with one of these completed as a monitoring well and the excavation of 18 test pits. Five boreholes were advanced for geotechnical investigation. The locations of all boreholes, monitoring wells and test pits are shown on Figure 3. The surficial geology in this part of Cambridge largely consists of sand and gravel outwash deposits along the eastern side of the Grand River. The stratigraphy encountered during the subsurface investigation was generally consistent across the property, with an unconfined sand or sand and silt unit extending from ground surface to the maximum depth investigated 3

42 Phase Two Conceptual Site Model 350 Dundas Street South, Cambridge, Ontario (15.2 m below ground surface (bgs) at MW11-2). The sand unit contained layers of sand and silt and layers of sand and gravel. A layer of fill was identified in the central portion of the property. Figures 4 and 5 are cross sections showing the stratigraphy of the subject property from the ground surface to the deepest aquifer investigated. The orientations of the cross-sections are shown in Figure HYDROGEOLOGICAL CHARACTERISTICS OF HYDROSTRATIGRAPHIC UNITS No contamination was identified in the surfical aquifer at the property; therefore only the surficial aquifer was investigated. The surficial water table is located at about 278 masl, which varies from 7 m bgs to 14 m bgs due to the topography. The sand and gravel overburden extends to a depth of about 35 m bgs based on the available literature and well records for the area. The phase two property is located in the well head protection area (WHPA) for both the Elgin Street Well Field and the Middleton Street Well Field. Both of these well fields obtain water from the bedrock aquifer. 2.7 DEPTH TO BEDROCK The dolostone of the Guelph formation is located at a depth of about 35 m below ground surface. 2.8 DEPTH TO WATER TABLE The ground water contours for April 30, 2013 are shown in Figure 6. The depth to water varied from about 7 m bgs at MW11-4 and MW1-12 to about 14 m bgs at MW11-2. MW11-4 and MW1-12 were located in the lowest areas of the property. The ground water flow direction is inferred to be towards the southwest. The horizontal gradient was approximately m/m on July 11, 2012 and approximately m/m on April 30, WITH RESPECT TO SECTION 41 OR 43.1 OF O. REG. 153 The phase two property is not considered to be environmentally sensitive as per the definitions provided in Section 41 of O.Reg.153/04. The phase two property is not part of or adjacent to an area of natural significance and the soil ph is within the permitted ranges of 5 to 11 for subsurface soils and 5 to 9 for surface soils. The property is not a shallow soil property and does not include or is within 30 m of a water body and therefore is not considered environmentally sensitive under Section 43.1 of O.Reg.153/ FILL MATERIAL Fill material was identified on the phase two property and is identified as APEC 1 and described below. 4

43 Phase Two Conceptual Site Model 350 Dundas Street South, Cambridge, Ontario 2.11 LOCATIONS OF PROPOSED BUILDINGS AND OTHER STRUCTURES The subject property will be redeveloped for residential use. Buildings (town homes) and their associated driveways and parking areas will cover a majority of the site. A total of 53 units in eight blocks are proposed. 3. CONTAMINANTS PRESENT ON PHASE TWO PROPERTY 3.1 AREAS OF POTENTIAL ENVIRONMENTAL CONCERN APEC 1 Imported Fill of Unknown Origin Fill material was identified in the central portion of the property. A total of 19 test pits and four boreholes / monitoring wells were completed in the area of the fill material to confirm the quality of the fill material and to delineate the fill material. The limits of the waste fill layer were delineated during the excavation of additional test pits by extending the test pit until the visual edge of the waste fill was encountered. Figure 7 shows the locations of the test pits and boreholes / monitoring wells completed and Figures 8 and 9 provide cross sections identifying the sample locations. Two distinct types of fill material were identified. The overlying fill material was a sand and gravel material. Based on the type of material, evidence from a 1993 aerial photograph, and anecdotal evidence it is believed this overlying fill material originated from the property immediately to the south (95 Morning Calm Drive). The fill material beneath the overlying fill material contained various waste materials (household waste, construction waste and potentially foundry sand, etc.). The waste fill material was visually identifiable in that it had a distinctive dark colouring. The limits of the waste fill layer were confirmed both visually and through analytical testing. Soil samples were analyzed for petroleum hydrocarbons (PHC), metals, polycyclic aromatic hydrocarbons (PAHs), and volatile organic compounds (VOCs). The contaminants of concern (COC) were PHC F3, metals and PAHs. All of the samples where concentrations of compounds exceeded the SCS were associated with the waste fill material. Concentrations of PAHs were found to exceed the SCS on all samples from the waste fill layer and occasionally concentrations of metals and PHC exceeded the SCS in these samples. Figure 7 shows the concentrations of COCs in soil that exceeded Table 2 SCS. It appears that either there was an existing depression on the property or excavation of the property occurred at some point in the past. Waste fill material consisting of various materials including household garbage, construction debris, fill and potentially foundry sand was placed in this depression/excavation. This material was then covered with a sand and gravel material that was likely moved from the town home development to the south of the property. There were no subsurface structures or utilities in the area of the waste fill material (APEC 1) hence there was no potential to affect contaminant transportation and transport. The COCs in soil (PHC F3, metals and PAHs) have limited mobility and leaching to groundwater is not expected. MW11-3 was installed within the area of the fill. The groundwater was sampled and 5

44 Phase Two Conceptual Site Model 350 Dundas Street South, Cambridge, Ontario analyzed for PHCs, PAHs and VOCs on three occasions with all results less than Table 2 SCS confirming leaching from the soil COCs had not occurred. Figure 11 provides a conceptual exposure model for the COCs identified in soil (PHC F3, metals and PAHs). The COCs are not volatile so the distribution mechanisms would be direct contact, particles becoming airborne, and possibly leaching to groundwater. The potential receptors would be residents, workers and visitors for human health, and mammals and birds for ecological receptors. Plants could be exposed if the root system extended to the depth of the COCs and soil organisms could be exposed if they were present at depth. APEC 2 Fuel Oil Storage Associated With Heating System for Former House The former house had a natural gas furnace at the time of the phase two investigation but had historically used fuel oil as a heating source. A fuel oil aboveground storage tank (AST) was located in the house prior to demolition. BH1 was advanced at the exterior fill pipe for the former heating oil AST. No staining was observed and results for soil analytical testing for PHCs, metals and PAHs were below Table 2 SCS. There are no COCs associated with APEC 2. As well, there were no subsurface structures or utilities in APEC 2 hence there is no potential to affect contaminant transportation and transport. APEC 3 Possible Maintenance of Vehicles on Adjacent Property A trucking facility is located adjacent site to the north of phase two property. It is possible that vehicle maintenance has occurred in the past. There are no indications that there are underground storage tanks located on the property to the north. The environmental concern is limited to near surface contamination by oil and greases on the north property boundary at the west (rear) corner of the off-site building. Test pits were excavated adjacent to the property to the north which indicated that the fill material associated with APEC 1 extended to the northern property boundary. The remedial excavation for APEC 1 extended to the north property boundary in this area eliminating APEC 3 as an environmental concern. There were no subsurface structures or utilities at the property boundary at APEC 3 hence there is no potential to affect contaminant transportation and transport. As all contaminants are associated with soil, any climatic or meteorological conditions would not have influenced the distribution and migration of the contaminants. 4. REMEDIATION PROGRAM Figures 8, 9 and 10 show the extent of the soil excavation and locations of confirmatory soil sampling. Remediation involved the removal and stockpiling of the overlying fill material. The total volume of this fill material was 2,550 m 3. Sampling according to Section 36 of Schedule E of 6

45 Phase Two Conceptual Site Model 350 Dundas Street South, Cambridge, Ontario O.Reg. 153/04 and analysis of this material was completed. A total of 17 samples were analyzed for the COCs and were confirmed to meet Table 2 SCS. The material will be used as part of the overall site grading. No fill will be required to be imported for the proposed development. The waste fill material was excavated and stockpiled within the limits of the excavation. The limits of the waste fill material were visually evident. Samples were collected to confirm that the material had concentrations of COCs that exceed Table 2 SCS. A total of 6,780 m 3 (14, tonnes) of waste material were disposed at an approved facility. All impacted soil was excavated and removed from the site. No soil treatment occurred on site. The area of the excavation was approximately 3,600 m 2. Confirmatory floor and wall samples were collected and analyzed for COCs according to Section 39.7 of Schedule E of O.Reg. 153/04. A total of 33 confirmatory soil samples were collected from the floor of the excavation. The sample density was about one sample per 110 m 2 which exceeds the requirements. Samples were analyzed for PHC, PAHs and metals. Concentrations of PAHs in one confirmatory soil sample (F-12-5) were above the SCS. The excavation was deepened by 1 m in this area and the confirmation sample confirmed that all contaminated material had been removed. A total of 9 confirmatory samples were collected along the walls of the excavation. There were no walls of the excavation in some areas and the excavation extended to the property line on the northwest and southeast extents. The excavation and removal of the waste fill material confirmed that the waste fill material was placed in a depression and/or excavation on the property and subsequently covered with a layer of sand and gravel material which was likely native material from the property to the south. 7

46 Legend: PCA 37. Inferred & Confirmed Groundwater Flow Direction Phase One Study Area Limit Phase Two Property Boundary 200 Franklin Blvd. Commercial PCA 28. Residential Commercial APEC Description Imported Fill Material Fuel oil storage associated with heating system for former house Off-site - possible maintenance of vehicles (adjacent site to north) PCA No. 205 Franklin Blvd. us h D B nk lin Fr a Commercial Ell iot S Commercial Autobody Shops 28. Gasoline and Associated Products Storage in Fixed Tanks 30. Importation of Fill Material of Unknown Quality Operation of Dry Cleaning Equipment (where chemicals are used) 52. Storage, maintenance, fueling and repair of equipment, vehicles and material used to maintain transportation e 37. References: Du nd PCA 30. Aerial Imagery provided by First Base Solution (2008). as or Tay l PCA 10. St re 50 et S ou th 25 O 50 Client: Freure Construction Ltd. D ri v e Residential Residential 0 Meters Project: Residential PCA Description 10. ap l PCA Residential PHC, PAH M lv d. 2 3 t re et B PCA 52. Residential ri v e Commercial Dundas St. Commercial Contaminants of Potential Concern PHC, PAH, Metals PHC, PAH Phase Two ESA 350 Dundas Street South Cambridge, Ontario Figure: Phase One Conceptual Site Model Recreational Address 171 Victoria St. N., Kitchener, O ntario, N2H 5C5 Tel: Fax: Moffat Creek Residential Project Number: W-B Verified By: MD Drawn By: Figure No: Designed By: MD KC Revision: August 11,

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52 LEGEND Site Boundary Building Test Pit Location (WESA) Borehole Location (WESA) Monitoring Well Location (WESA) Borehole Location (Stantec) Monitoring Well Location (Stantec) Test Pit Location (approximate) (Stantec) Approximate Extent of Dark Fill Thickness of Dark Fill SCS: Site Condition Standard: Table 2, coarse grained, soil, residential Concentrations in µg/g REFERENCES 0 m 5 m 10 m 15 m 20 m 25 m THIS SCALE TO BE USED TO OBTAIN APPROXIMATE DIMENSIONS FOR INFORMATION CLIENT FREURE CONSTRUCTION LTD. PROJECT PHASE TWO ESA 350 DUNDAS STREET SOUTH CAMBRIDGE ONTARIO TITLE SOIL ANALYTICAL RESULTS FOR CONTAMINANTS OF CONCERN PROJECT # W-B DRAWN DATE CHECKED DWG NO. REV MBB MD FIGURE 7 0 B10506 SP Aug 2014.dwg

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