Environmental Noise Assessment Feasibility Assessment 92 Plains Road East

Environmental Noise Assessment Feasibility Assessment 92 Plains Road East Novus Reference No. 16-0006 Version No. 1.1 (Final) February 26, 2016 NOVUS PROJECT TEAM: Specialist: Marcus Li, P.Eng. 16/02/26 Air Quality Sound & Vibration Sustainable Water Wind & Climate Novus Environmental Inc. 150 Research Lane, Suite 105, Guelph, Ontario, Canada N1G 4T2 Novus West Inc. 906 12 Avenue SW, Suite 600, Calgary, Alberta, Canada T2R 1K7

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Environmental Noise Assessment 92 Plains Road February 26, 2016 Table of Contents 1.0 INTRODUCTION... 1 1.1 Focus of Report... 1 1.2 Nature of the Subject Lands... 1 1.3 Nature of the Surroundings... 1 PART 1: IMPACTS OF THE ENVIRONMENT ON THE DEVELOPMENT... 2 2.0 Transportation Noise Impacts... 2 2.1 Transportation Noise Sources... 2 2.2 Surface Transportation Noise Criteria... 3 2.2.1 Ministry of the Environment Publication NPC-300... 3 2.2.2 Halton Region... 5 2.3 Traffic Data and Future Projections... 5 2.3.1 Roadway Traffic Data... 5 2.4 Projected Sound Levels... 6 2.4.1 Façade Sound Levels... 6 2.4.2 Outdoor Living Areas... 7 2.5 Façade Recommendations... 7 2.6 Ventilation and Warning Clause Requirements... 7 PART 2: IMPACTS OF THE DEVELOPMENT ON THE SURROUNDING AREA... 8 3.0 Impacts of the Development Mechanical Systems on Surrounding Properties... 8 PART 3: IMPACTS OF THE DEVELOPMENT ON ITSELF... 9 4.0 Outdoor Noise Impacts from Development Mechanical Systems... 9 5.0 CONUSIONS AND RECOMMENDATIONS... 9 5.1 Transportation Noise... 9 5.2 Industrial Stationary Noise... 10 5.3 Overall Assessment... 10 6.0 REFERENCES... 12 List of Tables Table 1: NPC-300 Sound Level Criteria for Road and Rail Noise... 3 Table 2: NPC-300 Ventilation and Warning Clause Requirements... 4 Table 3: MOE Publication NPC-300 Building Component Requirements... 5 Table 4: Summary of Road Traffic Data Used in the Transportation Noise Analysis... 6 Table 5: Summary of Predicted Façade Sound Levels... 6 Novus Environmental i

Environmental Noise Assessment 92 Plains Road February 26, 2016 List of Figures Figure 1: Context Plan List of Appendices Appendix A: Development Drawings Appendix B: Traffic Data and Modelling Appendix C: Façade Calculations Novus Environmental ii

Environmental Noise Assessment 92 Plains Road February 26, 2016 1.0 INTRODUCTION Novus Environmental Inc. (Novus) was retained by Chelton Developments Inc. to conduct an Environmental Noise Feasibility Assessment for the proposed mixed-use residential development located at 92 Plains Road East, in Burlington, Ontario. This noise study is to be used to support the Official Plan and Zoning By-law Amendment application for the proposed development. 1.1 Focus of Report In keeping with City of Burlington and Halton Region requirements, this report examines the potential for: Impacts of the environment on the proposed development; Impacts of the proposed development on the environment; and Impacts of the proposed development on itself. 1.2 Nature of the Subject Lands The subject property is located on the south side of Plains Road east, between Birchwood Avenue and Glenwood Avenue, as shown in Figure 1. The closest major intersection is Plains Road East and Waterdown Road, located west of the proposed development. The proposed development will consist of a four (4) storey structure, with residential units on the 2 nd through 4 th floors. The main floor will consist of commercial units, and a covered parking area. Private terraces are located along the east and west facades of the residential floors (2 nd through 4 th ). A public patio space is located at grade, along the west façade of the development. A copy of the site plan and floor plans are included in Appendix A. 1.3 Nature of the Surroundings The existing buildings surrounding the development are primarily two-storey single family homes to the east, south and west. Single-storey commercial uses are located on the north side of Plains Road East, with single family homes located beyond these properties. Novus Environmental 1

Environmental Noise Assessment 92 Plains Road February 26, 2016 Commercial uses are located further to the west, surrounding Waterdown Road. Industrial land, including the Aldreshot Rail Yard, King Paving and CBM Ready-Mix Plant, are located approximately 600 m to 700 m to the north-west and west. A Context Plan is shown in Figure 1. PART 1: IMPACTS OF THE ENVIRONMENT ON THE DEVELOPMENT In assessing potential impacts of the environment on the proposed development, the focus of this report is on the roadway noise impacts from Plains Road East. Highway 403 and the closest railway line are both located at distances greater than 500 m, and are not anticipated to impact the proposed development. A site visit was completed on February 10, 2016 to review existing stationary noise sources. The adjacent commercial properties were found to have insignificant contributions of noise on the proposed development, and have not been assessed. The surrounding Class 3 industries (Aldershot Rail Yard, the King Paving Asphalt Plant, and the CBM Ready-mix facility) are located greater than 600 m from the proposed development. Given the large separation distance and the number of intervening buildings (including noise sensitive residential homes), the noise impacts from these Class 3 facilities are not anticipated to be a concern and have not been assessed. No significant sources of vibration are located in the surrounding area. Therefore, a vibration assessment was not considered necessary. 2.0 Transportation Noise Impacts 2.1 Transportation Noise Sources Transportation noise sources with the potential to produce noise at the proposed development include Plains Road East only. As mentioned above, Highway 403 and the railway are located greater than 500 m from the development and are not anticipated to impact the development. Sound exposure levels at the development due to Plains Road East have been predicted, and this information has been used to identify façade, ventilation, and warning clause requirements. Novus Environmental 2

Environmental Noise Assessment 92 Plains Road February 26, 2016 2.2 Surface Transportation Noise Criteria 2.2.1 Ministry of the Environment Publication NPC-300 Noise Sensitive Developments Ministry of the Environment (MOE) Publication NPC-300 provides sound level criteria for noise sensitive developments. The applicable portions of NPC-300 are Part C Land Use Planning and the associated definitions outlined in Part A Background. Table 1 to Table 3 below summarize applicable surface transportation (road and rail) criteria limits. Location Specific Criteria Table 1 summarizes criteria in terms of energy equivalent sound exposure (Leq) levels for specific noise-sensitive locations. Both outdoor and indoor locations are identified, with the focus of outdoor areas being amenity spaces. Indoor criteria vary with sensitivity of the space. As a result, sleep areas have more stringent criteria than Living / Dining room space. Table 1: NPC-300 Sound Level Criteria for Road and Rail Noise Type of Space Outdoor Amenity Area Living / Dining Room [3] Sleeping Quarters Notes: Time Period Daytime (0700 2300h) Daytime (0700 2300h) Nighttime (2300 0700h) Daytime (0700 2300h) Nighttime (2300 0700h) Energy Equivalent Sound Exposure Level L eq [5] (dba) Road Rail [1] Assessment Location 55 55 Outdoors [2] 45 40 Indoors [4] 45 40 Indoors [4] 45 40 Indoors [4] 40 35 Indoors [4] [1] Whistle noise is excluded for OLA noise assessments, and included for Living / Dining Room and Sleeping Quarter assessments, where applicable. [2] Road and Rail noise impacts are to be combined for assessment of OLA impacts. [3] Residence area Dens, Hospitals, Nursing Homes, Schools, Daycares are also included. During the nighttime period, Schools and Daycares are excluded. [4] An assessment of indoor noise levels is required only if the criteria in Table 3 are exceeded. [5] L eq the energy equivalent sound exposure level, integrated over the time period shown. Ventilation and Warning Clauses Table 2 summarizes requirements for ventilation where windows potentially would have to remain closed as a means of noise control. These requirements apply where the sound exposure levels found in Table 2 exceed the guideline limits in Table 1 for indoor spaces. Novus Environmental 3

Environmental Noise Assessment 92 Plains Road February 26, 2016 Despite the implementation of ventilation measures where required, some occupants may choose not to use the ventilation means provided, and as such, warning clauses advising future occupants of the potential excess over the Table 1 guideline limits are required. Warning Clauses also apply to the OLA where an excess of up to 5 dba over the 55 dba OLA limit is often acceptable to many, particularly in the context of an urban environment. Warning Clauses are discussed further in Section 2.6. Table 2: NPC-300 Ventilation and Warning Clause Requirements Assessment Location Time Period Energy Equivalent Sound Exposure Level L eq (dba) Road Rail [1] Ventilation and Warning Clause Requirements [2] Outdoor Amenity Area Daytime (0700 2300h) 56 to 60 incl. Type A Warning Clause 55 None Plane of Window Daytime (0700 2300h) Nighttime (2300 0700h) 56 to 65 incl. > 65 51 to 60 incl. > 60 Forced Air Heating with provision to add air conditioning + Type C Warning Clause Central Air Conditioning + Type D Warning Clause Forced Air Heating with provision to add air conditioning + Type C Warning Clause Central Air Conditioning + Type D Warning Clause Notes: [1] Whistle noise is excluded. [2] Road and Rail noise is combined for determining Ventilation and Warning Clause requirements. Building Shell Requirements Table 3 provides Leq thresholds which, if exceeded, require the building shell and components (i.e., wall, windows) to be designed and selected accordingly to ensure that the Table 1 indoor location criteria are met. Novus Environmental 4

Environmental Noise Assessment 92 Plains Road February 26, 2016 Table 3: MOE Publication NPC-300 Building Component Requirements Assessment Location Time Period Energy Equivalent Sound Exposure Level L eq (dba) Road Rail [1] Component Requirements Plane of Window Daytime (0700 2300h) Nighttime (2300 0700h) > 65 > 60 > 60 > 55 Designed/ Selected to Meet Indoor Requirements [2] Notes: [1] Including whistle noise. [2] Building component requirements are assessed separately for Road and Railway noise. The resultant sound isolation parameter is required to be combined to determine and overall acoustic parameter. In summary, roadway noise impacts are to be predicted at the plane-of-window for the proposed development. Providing the plane-of-window sound levels exceed the daytime and nighttime sound levels indicated in Table 3, the determination of the building façade components is required for meeting the indoor sound level criteria outlined in Table 1. In addition, the ventilation requirements and warning clauses are determined, as outlined in Table 2, based on the plane-of-window noise levels. 2.2.2 Halton Region The Halton Region guidelines include the Noise Abatement Guidelines Regional Official Plan Guidelines and the Land Use Compatibility Guidelines Regional Official Plan Guidelines, both dated dated June 18, 2014. In general, the Halton Region guidelines are consistent with the MOE NPC-300 guidelines. Therefore, the guidelines have not been reiterated. 2.3 Traffic Data and Future Projections 2.3.1 Roadway Traffic Data Road traffic data was purchased from the Transportation Services Department of the City of Burlington. The projected 10-year future traffic volumes were determined based on a typical growth rate of 2% per year. Table 4 summarizes the road traffic volumes used in the analysis. A copy of the traffic data used can be found in Appendix B. Novus Environmental 5

Environmental Noise Assessment 92 Plains Road February 26, 2016 Table 4: Summary of Road Traffic Data Used in the Transportation Noise Analysis Notes: Roadway Link 10 yr Future Volume [1] Day / Night Volume Split [2] Commercial Traffic [1] [3] Vehicle Breakdown Speed (km/h) % Medium % Heavy (AADT) Daytime Nighttime Trucks Trucks Plains Road East 26,343 90 10 2.2 % 1.1 % 60 [1] based on City of Burlington TMC data. [2] per default MOECC day/night split for regional roads [3] medium/heavy split based on historical City of Burlington data. 2.4 Projected Sound Levels Road traffic sound levels at the proposed development were predicted using MOECC s ORNAMENT algorithms, calculated with the STAMSON v5.04 road traffic noise model. A copy of the STAMSON modelling output files are included in Appendix B. Given the minimal absorptive grounds (grass, vegetation, etc.) between the development and Plains Road, reflective ground has been applied. 2.4.1 Façade Sound Levels Sound levels were predicted at two (2) locations, as follows: along the north façade, corresponding to the location of a bedroom, and along the side of the building, corresponding to the location of the living room space. The predicted roadway noise levels are summarized in the following table. Table 5: Summary of Predicted Façade Sound Levels Facade Room Type Period North East/West Sleeping Quarters Living Rooms/Dining Rooms Predicted Sound Levels (dba) Daytime 67 Nighttime 61 Daytime 63 Nighttime 57 The façade sound levels are predicted to exceed 65 dba and 60 dba during the daytime and nighttime periods, respectively, along the north façade. Therefore, an assessment of building components is required for north façade sleeping quarters only. Novus Environmental 6

Environmental Noise Assessment 92 Plains Road February 26, 2016 2.4.2 Outdoor Living Areas Private terraces are located along the east and west facades of the proposed development. These terraces have been excluded from the assessment, since the MOECC minimum depth requirement of 4 m is not met. A patio space is located at grade, on the west side of the development. As this space is considered to be publicly accessible, it has not been included as an amenity space in this assessment. 2.5 Façade Recommendations An assessment of building components is required for the bedroom spaces along the north façade of the development. Two (2) bedrooms are located along the north façade, where the west bedroom (bedroom 1) has one (1) façade with glazing. The east bedroom (bedroom 2) has glazing included on both the north and east façade. Room, window and façade dimensions were determined from the current development drawings, included in Appendix A. The indoor sound levels and required Façade Sound Transmission Classes (STCs) were estimated using the procedures outlined in National Research Council Building Practice Note BPN-56. Details associated with the façade calculations are shown in Appendix C. A maximum rating of STC 24 was determined for the glazing on the north façade sleeping quarters, based on the room and façade dimensions. Therefore, windows conforming to the minimum structural requirements of the Ontario Building Code (STC 29 rating), are predicted to be adequate for all north façade sleeping quarters. No upgraded glazing is predicted to be required. 2.6 Ventilation and Warning Clause Requirements The requirements regarding warning clauses are summarized in Table 2. Where required, the Warning Clauses must be included in all agreements of purchase and sale or lease, and all rental agreements. Based on the predicted façade noise levels, the north façade units (facing Plains Road East) will require mandatory air conditioning and a Type D Warning Clause All other units will require forced air heating with a provision for air conditioning and a Type C Warning Clause. The Type D and C Warning Clauses are summarized below: Novus Environmental 7

Environmental Noise Assessment 92 Plains Road February 26, 2016 Type D Warning Clause This dwelling unit has been or will be fitted with a central air conditioning system which will enable occupants to keep windows closed if road and or air traffic noise interferes with the indoor activities. Type C Warning Clause This dwelling unit has been designed with the provision for adding central air conditioning at the occupant s discretion. Installation of central air conditioning by the occupant in low and medium density developments will allow windows and exterior doors to remain closed, thereby ensuring that the indoor sound levels are within the sound level limits of the Municipality and the Ministry of the Environment. PART 2: IMPACTS OF THE DEVELOPMENT ON THE SURROUNDING AREA 3.0 Impacts of the Development Mechanical Systems on Surrounding Properties In terms of the noise environment of the area, it is expected that the project will have a negligible effect on the neighbouring properties. The traffic related to the proposed development will be small in relation to the traffic volumes within the area, and is not of concern with respect to noise impact. Other possible sources of noise associated with the development with potentially adverse impacts on the surrounding neighbourhood are emergency generators and mechanical roof-top equipment. This equipment is required to meet MOE Publication NPC-300 requirements at the closest off-site noise sensitive receptors. Given the high ambient sound levels in the area and the fact that the systems will be designed to ensure that the applicable noise guideline are met at on-site receptors, off-site impacts are not anticipated. Regardless, potential impacts should be assessed as part of the final building design. The criteria can be met at all surrounding and on-site receptors by the appropriate selection of mechanical equipment, by locating equipment with sufficient setback from noise sensitive locations, and by incorporating control measures (e.g., silencers) into the design. It is recommended the mechanical systems be reviewed by an acoustical professional prior to final selection of equipment. Novus Environmental 8

Environmental Noise Assessment 92 Plains Road February 26, 2016 PART 3: IMPACTS OF THE DEVELOPMENT ON ITSELF 4.0 Outdoor Noise Impacts from Development Mechanical Systems The building mechanical systems have not been designed at this time. Although no adverse impacts are expected, such equipment has the potential to result in noise impacts on residential spaces within the development. This equipment is required to meet MOE Publication NPC-300 requirements at the facades of the noise sensitive spaces within the development.. Therefore, the potential impacts should be assessed as part of the final building design. The criteria is expected to be met at all on-site receptors with the appropriate selection of mechanical equipment, by locating equipment to minimize noise impacts within the development, and by incorporating control measures (e.g., silencers) into the design. It is recommended the mechanical systems be reviewed by an acoustical professional prior to final selection of equipment. 5.0 CONUSIONS AND RECOMMENDATIONS The potential for noise impacts on and from the proposed development have been assessed. Impacts of the environment on the development, the development on itself, and the development on the surrounding area have been considered. Based on the results of the study, the following conclusions have been reached: 5.1 Transportation Noise An assessment of roadway noise impacts has been completed. Façade walls and windows are predicted to not require upgrades, as outlined in Section 2.5. Ventilation requirements are recommended as outlined in Section 2.6 and include the requirement for Air Conditioning for the units along the north façade of the development, and the Provision for Air Conditioning for all other units. Warning Clauses must be included in all agreements of purchase and sale or lease and all rental agreements for units along select façades, as outlined in Section 2.6 and summarized as follows: Novus Environmental 9

Environmental Noise Assessment 92 Plains Road February 26, 2016 o North Façade Units require the following Type D Warning Clause: This dwelling unit has been or will be fitted with a central air conditioning system which will enable occupants to keep windows closed if road and or air traffic noise interferes with the indoor activities. o All other units require the following Type C Warning Clause: This dwelling unit has been designed with the provision for adding central air conditioning at the occupant s discretion. Installation of central air conditioning by the occupant in low and medium density developments will allow windows and exterior doors to remain closed, thereby ensuring that the indoor sound levels are within the sound level limits of the Municipality and the Ministry of the Environment. 5.2 Industrial Stationary Noise A review was completed of the surrounding area, and observations were made regarding stationary noise. The existing commercial properties surrounding the development are considered to be insignificant contributors of noise, and have not been assessed. Stationary noise impacts from surrounding industries (Aldershot Rail Yard, King Paving Asphalt plant and CBM Ready-Mix facility) are located greater than 600 m from the proposed development. Given the large separation distance, and intervening buildings (including noise sensitive receptors), noise impacts are not anticipated and have not been assessed. 5.3 Overall Assessment Impacts of the environment on the proposed development can be adequately controlled without upgrades to the building construction, ventilation requirements and warning clauses detailed in Part 1 of this report. Impacts of the proposed development are predicted to meet the applicable guideline limits, and can be adequately controlled by following the design guidance outlined Part 2 of this report. Novus Environmental 10

Environmental Noise Assessment 92 Plains Road February 26, 2016 Impacts of the proposed development on itself can be adequately controlled by following the design guidance outlined in Part 3 of this report. As the mechanical systems have not been designed at the time of this assessment, the acoustical requirements above should be confirmed by an Acoustical Consultant as part of the final building design. Novus Environmental 11

Environmental Noise Assessment 92 Plains Road February 26, 2016 6.0 REFERENCES Halton Region, 2014, Land Use Compatibility Guidelines Regional Official Plan Guidelines Halton Region, 2014, Noise Abatement Guidelines Regional Official Plan Guidelines Ontario Ministry of the Environment and Climate Change, 1989, Ontario Road Noise Analysis Method for Environment and Transportation (ORNAMENT) Ontario Ministry of the Environment and Climate Change, Publication NPC-300: Environmental Noise Guideline, Stationary and Transportation Sources Approval and Planning, 2013. Ontario Ministry of the Environment (MOE), 1996, STAMSON v5.03: Road, Rail and Rapid Transit Noise Prediction Model Novus Environmental 12

Figures Novus Environmental

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Aldershot GO Station 500 m radius Existing Residential Aldershot Rail Yard Existing Commercial Existing Residential Existing Residential Existing Commercial Subject Property 92 Plains Rd Existing Residential CMB Ready Mix Plant King Paving Asphalt Plant Existing Residential Aerial Photography from Google Earth Figure No. 1 Context Plan Scale: Date: 1: 10,000 16/02/15 92 Plians Road Development Burlington, Ontario True North File No.: Drawn By: 16-0006 MTL

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Appendix A Novus Environmental

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CZ A PHONE - 905.331.4480 LANDSCAPED AREA 3 BARRIER FREE ENTRANCE TRUE NORTH LOCATION MAP NTS IO A SSO C OF N TIO IA BARRIER FREE ENTRANCE ONTA R LANDSCAPED AREA ARCHITECTS CONST. NORTH CYNTHIA ZAHORUK LICENSE 4488 ASPHALT DRIVEWAY ONTARIO ASSOCIATION OF ARCHITECTS NOTES: 1.THE CONTRACTOR OR PROJECT MANAGER WILL CHECK AND VERIFY ALL DIMENSIONS AND JOB CONDITIONS ON THE JOB AND REPORT ANY DISCREPANCIES TO THE ARCHITECT PRIOR TO THE COMMENCEMENT OF CONSTRUCTION. COORDINATION OF WORK IS THE RESPONSIBILITY OF THE CONTRACTOR OR OWNER/CONTRACTOR 2.THIS DRAWING MUST NOT BE USED FOR CONSTRUCTION PURPOSES UNTIL SIGNED BY THE ARCHITECT. 3.ALL DRAWINGS ARE THE PROPERTY OF THE ARCHITECT AND MAY NOT BE COPIED, REPRODUCED OR ALTERED WITHOUT WRITTEN PERMISSION FROM THE ARCHITECT. 4.DO NOT SCALE THE DRAWINGS. DD/MM/YY REVISION 09/07/15 SUBMISSION FOR SPA ASPHALT DRIVEWAY LANDSCAPED AREA JOB NO. DRAWN BY: MGA SCALE: AS NOTED 2 NTS CONST. NORTH TRUE NORTH PROPOSED SITE PLAN 1 : 200 4 ZONING DATA NTS SITE PLAN LOCATION MAP ZONING DATA A 1.0 BURLINGTON, ON 3D VIEWS 92 PLAINS RD E 1 92 PLAINS ROAD MIXED USE DEVELOPMENT PRINT DATE: 19/01/2016

CZ A B C D E` F G H I J A B C D E F G H I J A 1 2 1 2 PHONE - 905.331.4480 OF ARCHITECTS ONTAR IO ASSOCIATION CYNTHIA ZAHORUK LICENSE 4488 3 3 ONTARIO ASSOCIATION OF ARCHITECTS 5 5 NOTES: 1.THE CONTRACTOR OR PROJECT MANAGER WILL CHECK AND VERIFY ALL DIMENSIONS AND JOB CONDITIONS ON THE JOB AND REPORT ANY DISCREPANCIES TO THE ARCHITECT PRIOR TO THE COMMENCEMENT OF CONSTRUCTION. COORDINATION OF WORK IS THE RESPONSIBILITY OF THE CONTRACTOR OR OWNER/CONTRACTOR 2.THIS DRAWING MUST NOT BE USED FOR CONSTRUCTION PURPOSES UNTIL SIGNED BY THE ARCHITECT. 3.ALL DRAWINGS ARE THE PROPERTY OF THE ARCHITECT AND MAY NOT BE COPIED, REPRODUCED OR ALTERED WITHOUT WRITTEN PERMISSION FROM THE ARCHITECT. 4.DO NOT SCALE THE DRAWINGS. DD/MM/YY REVISION 09/07/15 SUBMISSION FOR SPA 7 7 8 8 JOB NO. DRAWN BY: SCALE: PRINT DATE: MGA AS NOTED 09/07/2015 CONST. NORTH 11 TRUE NORTH 1 BASEMENT FLOOR 1 : 100 CONST. NORTH TRUE NORTH 11 2 MAIN LEVEL 1 : 100 92 PLAINS ROAD MIXED USE DEVELOPMENT 92 PLAINS RD E BURLINGTON, ON BASEMENT FLOOR MAIN FLOOR A 1.1

CZ A B C D E F G H I J A B C D E F G H I J A 1 1 PHONE - 905.331.4480 2 2` 2 2` LAUNDRY WIC LAUNDRY WIC OF ARCHITECTS ONTAR IO ASSOCIATION CYNTHIA ZAHORUK LICENSE 4488 3 5 FRENCH BALCONY BALCONY LAUNDRY LAUNDRY LAUNDRY BALCONY BALCONY 3 5 FRENCH BALCONY BALCONY LAUNDRY LAUNDRY LAUNDRY BALCONY BALCONY ONTARIO ASSOCIATION OF ARCHITECTS NOTES: 1.THE CONTRACTOR OR PROJECT MANAGER WILL CHECK AND VERIFY ALL DIMENSIONS AND JOB CONDITIONS ON THE JOB AND REPORT ANY DISCREPANCIES TO THE ARCHITECT PRIOR TO THE COMMENCEMENT OF CONSTRUCTION. COORDINATION OF WORK IS THE RESPONSIBILITY OF THE CONTRACTOR OR OWNER/CONTRACTOR 2.THIS DRAWING MUST NOT BE USED FOR CONSTRUCTION PURPOSES UNTIL SIGNED BY THE ARCHITECT. 3.ALL DRAWINGS ARE THE PROPERTY OF THE ARCHITECT AND MAY NOT BE COPIED, REPRODUCED OR ALTERED WITHOUT WRITTEN PERMISSION FROM THE ARCHITECT. 4.DO NOT SCALE THE DRAWINGS. WIC DEN WIC WIC DEN WIC DD/MM/YY REVISION 09/07/15 SUBMISSION FOR SPA WIC LAUNDRY WIC LAUNDRY 7 LAUNDRY 7 LAUNDRY BALCONY BALCONY BALCONY BALCONY 8 8 JOB NO. DRAWN BY: MGA BALCONY BALCONY BALCONY BALCONY SCALE: PRINT DATE: AS NOTED 09/07/2015 CONST. NORTH 11 TRUE NORTH 1 SECOND AND THIRD FLOOR 1 : 100 WIC DEN LAUNDRY LAUNDRY DEN WIC CONST. NORTH 11 TRUE NORTH 2 FOURTH FLOOR 1 : 100 WIC DEN LAUNDRY LAUNDRY DEN WIC 92 PLAINS ROAD MIXED USE DEVELOPMENT 92 PLAINS RD E BURLINGTON, ON SECOND /THIRD FOURTH FLOOR A 1.2

CZ T/O HI ROOF 17.08 U/S 4TH FLOOR G 12.73 CURTAIN WALL WOOD BRACKETS SMOOTH STONE FINISH WOOD BRACKETS HARDIBOARD SIDING CURTAIN WALL STONE FINISH T/O HI ROOF 17.08 U/S 4TH FLOOR G 12.73 A CYNTHIA ZAHORUK Architect Inc. PHONE - 905.331.4480 CURTAIN WALL WOOD SIDING U/S 3RD FLOOR G 9.60 4TH FLOOR 9.98 WOOD SIDING 3RD FLOOR 6.86 FRENCH BALCONY 3RD FLOOR 6.86 ONTARIO ASSOCIATION OF ARCHITECTS STONE FINISH 2ND FLOOR 3.73 WOOD BRACKETS SMOOTH STONE FINISH T/O Main Floor 0.00 STONE FINISH METAL CANOPY WOOD BRACKETS METAL CANOPY WOOD BRACKETS 2ND FLOOR 3.73 T/O Main Floor 0.00 NOTE: THE CONTRACTOR WILL CHECK AND VERIFY DIMENSIONS AND SITE CONDITIONS ON THE PROJECT AND REPORT ANY DISCREPENCY TO THE ARCHITECT PRIOR TO THE COMM- ENCEMENT OF CONSTRUCTION. THIS DRAWING MUST NOT BE USED FOR CONSTRUCTION PURPOSES UNLESS SIGNED BY THE ARCHITECT. ALL DRAWINGS ARE THE PROPERTY OF THE ARCHITECT AND MAY NOT BE COPIED, REPRODUCED OR ALTERED WITHOUT WRITTEN PERMISSION FROM THE ARCHITECT. DO NOT SCALE THE DRAWING. DATE REVISION 1 NORTH ELEVATION 1 : 100 2 WEST ELEVATION 1 : 100 09/07/15 SUBMISSION FOR SPA T/O HI ROOF 17.08 T/O HI ROOF 17.08 METAL ROOF METAL ROOF CURTAIN WALL STONE FINISH WOOD BRACKETS U/S 4TH FLOOR G 12.73 WINDOW U/S 4TH FLOOR G 12.73 JOB NO. DRAWN BY: MGA HARDIBOARD SIDING WOOD SIDING SCALE: 1 : 100 4TH FLOOR 9.98 SPANDREL PANELS 4TH FLOOR 9.98 DATE: 09/07/15 WOOD SIDING PREFINISHED ALUMINUM FASCIA SOFFIT HARDIBOARD SIDING CURTAIN WALL HARDIBOARD SIDING 3RD FLOOR 6.86 2ND FLOOR 3.73 T/O Main Floor 0.00 STONE FINISH 3 SOUTH ELEVATION 1 : 100 WOOD SIDING STONE FINISH 4 EAST ELEVATION 1 : 100 3RD FLOOR 6.86 STONE FINISH WINDOW WELL 2ND FLOOR 3.73 METAL CANOPY WOOD BRACKETS T/O Main Floor 0.00 92 PLAINS ROAD MIXED USE DEVELEPMENT 92 PLAINS RD E BURLINGTON,ON ELEVATIONS A2.0

Appendix B Novus Environmental

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Plains Rd @ Waterdown Rd Annual Average Daily Traffic Diagram Total Factor = Monthly Factor(1.02) x Daily Factor(0.94) x 24 Hour Factor(1.85) = 1.773780 Municipality: Site #: Intersection: TFR File #: Count date: Burlington 0000201468 Plains Rd & Waterdown Rd 3 9-Apr-2014 Weather conditions: Sunny/Dry Person(s) who counted: Eugene ** Signalized Intersection ** Major Road: Plains Rd runs W/E North Leg Total: 14485 Cyclists 14 2 2 18 Cyclists 11 East Leg Total: 20844 North Entering: 7292 Trucks 291 35 137 463 Trucks 392 East Entering: 10822 North Peds: 156 Cars 2622 1696 2494 6811 Cars 6790 East Peds: 181 Peds Cross: Totals 2927 1733 2632 Totals 7193 Peds Cross: Cyclists Trucks Cars Totals 74 495 10832 11402 Plains Rd Cyclists Trucks Cars Totals 7 243 2815 3065 37 209 6187 6434 21 14 970 1006 66 467 9972 Waterdown Rd N W E S Lasalle Park Rd Cars Trucks Cyclists Totals 2019 106 0 2125 7377 181 32 7590 1084 23 0 1107 10479 310 32 Plains Rd Cars Trucks Cyclists Totals 9607 374 41 10022 Peds Cross: Cars 3750 Cars 834 1956 926 3716 Peds Cross: West Peds: 133 Trucks 73 Trucks 23 43 28 94 South Peds: 62 West Entering: 10504 Cyclists 23 Cyclists 28 4 2 34 South Entering: 3844 West Leg Total: 21906 Totals 3846 Totals 885 2003 956 South Leg Total: 7689 Comments

STAMSON 5.0 NORMAL REPORT Date: 14-02-2016 02:33:19 MINISTRY OF ENVIRONMENT AND ENERGY / NOISE ASSESSMENT Filename: 92pl_bdr.te Time Period: Day/Night 16/8 hours Description: Plains Road, Bedroom Road data, segment # 1: PlainsRd (day/night) -------------------------------------------- Car traffic volume : 22926/2547 veh/timeperiod Medium truck volume : 522/58 veh/timeperiod Heavy truck volume : 261/29 veh/timeperiod Posted speed limit : 60 km/h Road gradient : 0 % Road pavement : 1 (Typical asphalt or concrete) Data for Segment # 1: PlainsRd (day/night) ------------------------------------------ Angle1 Angle2 : -90.00 deg 90.00 deg Wood depth : 0 (No woods.) No of house rows : 0 / 0 Surface : 2 (Reflective ground surface) Receiver source distance : 20.90 / 20.90 m Receiver height : 5.30 / 5.30 m Topography : 1 (Flat/gentle slope; no barrier) Reference angle : 0.00 Results segment # 1: PlainsRd (day) ----------------------------------- Source height = 1.02 m ROAD (0.00 + 67.16 + 0.00) = 67.16 dba Angle1 Angle2 Alpha RefLeq P.Adj D.Adj F.Adj W.Adj H.Adj B.Adj SubLeq ---------------------------------------------------------------------------- -90 90 0.00 68.60 0.00-1.44 0.00 0.00 0.00 0.00 67.16 ---------------------------------------------------------------------------- Segment Leq : 67.16 dba Total Leq All Segments: 67.16 dba Results segment # 1: PlainsRd (night) ------------------------------------- Source height = 1.02 m ROAD (0.00 + 60.63 + 0.00) = 60.63 dba Angle1 Angle2 Alpha RefLeq P.Adj D.Adj F.Adj W.Adj H.Adj B.Adj SubLeq ---------------------------------------------------------------------------- -90 90 0.00 62.07 0.00-1.44 0.00 0.00 0.00 0.00 60.63 ---------------------------------------------------------------------------- Segment Leq : 60.63 dba Total Leq All Segments: 60.63 dba TOTAL Leq FROM ALL SOURCES (DAY): 67.16 (NIGHT): 60.63

STAMSON 5.0 NORMAL REPORT Date: 14-02-2016 02:32:48 MINISTRY OF ENVIRONMENT AND ENERGY / NOISE ASSESSMENT Filename: 92Pl_Lvg.te Time Period: Day/Night 16/8 hours Description: Plains Road, Living Room Road data, segment # 1: PlainsRd (day/night) -------------------------------------------- Car traffic volume : 22926/2547 veh/timeperiod Medium truck volume : 522/58 veh/timeperiod Heavy truck volume : 261/29 veh/timeperiod Posted speed limit : 60 km/h Road gradient : 0 % Road pavement : 1 (Typical asphalt or concrete) Data for Segment # 1: PlainsRd (day/night) ------------------------------------------ Angle1 Angle2 : 0.00 deg 90.00 deg Wood depth : 0 (No woods.) No of house rows : 0 / 0 Surface : 2 (Reflective ground surface) Receiver source distance : 26.70 / 26.70 m Receiver height : 5.30 / 5.30 m Topography : 1 (Flat/gentle slope; no barrier) Reference angle : 0.00 Results segment # 1: PlainsRd (day) ----------------------------------- Source height = 1.02 m ROAD (0.00 + 63.08 + 0.00) = 63.08 dba Angle1 Angle2 Alpha RefLeq P.Adj D.Adj F.Adj W.Adj H.Adj B.Adj SubLeq ---------------------------------------------------------------------------- 0 90 0.00 68.60 0.00-2.50-3.01 0.00 0.00 0.00 63.08 ---------------------------------------------------------------------------- Segment Leq : 63.08 dba Total Leq All Segments: 63.08 dba Results segment # 1: PlainsRd (night) ------------------------------------- Source height = 1.02 m ROAD (0.00 + 56.55 + 0.00) = 56.55 dba Angle1 Angle2 Alpha RefLeq P.Adj D.Adj F.Adj W.Adj H.Adj B.Adj SubLeq ---------------------------------------------------------------------------- 0 90 0.00 62.07 0.00-2.50-3.01 0.00 0.00 0.00 56.55 ---------------------------------------------------------------------------- Segment Leq : 56.55 dba Total Leq All Segments: 56.55 dba TOTAL Leq FROM ALL SOURCES (DAY): 63.08 (NIGHT): 56.55

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Appendix C Novus Environmental

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Page 1 of 1 BPN 56 Calculation Procedure Required Glazing STC Rating (Fixed Veneer) 92 Plains Road, 16 0006 ROADWAY Receptor ID Receptor Description Sound Levels Room / Façade Inputs Source Inputs Veneer Component 1 Façade Sound Level: Required Free field Indoor Correction: Sound Level: Required Noise Reduction: Glazing as % of Wall Area Exposed Wall Height (m) Exposed Wall Length (m) Room Depth (m) Total Floor Area Veneer Wall Area Glazing Wall Area Veneer as % of Floor Area: Glazing as % of Floor Area: Room Absorption: Incident Sound Angle: Angle Correction Spectrum type: Factor: Assumed Veneer Component Category: STC (dba) (dba) (dba) (dba) (m 2 ) (m 2 ) (m 2 ) (%) (%) (deg) (STC) (%) (%) (STC) (STC) DAYTIME Bedroom1_West North Façade Bedroom, West Side 67 3 45 25 34% 2.7 3.3 3.8 12.8 6.0 3.1 46 24 Intermediate 0 90 0 D. mixed road traffic, distant aircraft 45 D. sealed thick window, or exterior wall, or roof/ceiling 2 7 15 5 C. sealed thin window, or openable thick window 5 4 95 0 24 24 Bedroom2_East_N North Façade Bedroom, East Side, North Wall 67 3 45 25 19% 2.7 3.9 3.1 12.1 8.5 2.0 70 17 Intermediate 0 90 0 D. mixed road traffic, distant aircraft 45 D. sealed thick window, or exterior wall, or roof/ceiling 1 7 14 5 C. sealed thin window, or openable thick window 7 4 95 0 22 Bedroom2_East_E North Façade Bedroom, East Side, East Wall 64 3 45 22 14% 2.7 3.1 3.9 12.1 7.3 1.2 60 10 Intermediate 0 90 0 D. mixed road traffic, distant aircraft 45 D. sealed thick window, or exterior wall, or roof/ceiling 1 7 17 5 C. sealed thin window, or openable thick window 9 4 95 0 17 23 NIGHT TIME Bedroom1_West North Façade Bedroom, West Side 61 3 40 24 34% 2.7 3.3 3.8 12.8 6.0 3.1 46 24 Intermediate 0 90 0 D. mixed road traffic, distant aircraft 45 D. sealed thick window, or exterior wall, or roof/ceiling 2 7 16 5 C. sealed thin window, or openable thick window 5 4 95 0 23 23 Bedroom2_East_N North Façade Bedroom, East Side, North Wall 61 3 40 24 19% 2.7 3.9 3.1 12.1 8.5 2.0 70 17 Intermediate 0 90 0 D. mixed road traffic, distant aircraft 45 D. sealed thick window, or exterior wall, or roof/ceiling 1 7 15 5 C. sealed thin window, or openable thick window 7 4 95 0 21 22 Bedroom2_East_E North Façade Bedroom, East Side, East Wall 58 3 40 21 14% 2.7 3.1 3.9 12.1 7.3 1.2 60 10 Intermediate 0 90 0 D. mixed road traffic, distant aircraft 45 D. sealed thick window, or exterior wall, or roof/ceiling 1 7 18 5 C. sealed thin window, or openable thick window 9 4 95 0 16 Room Correction Frequency Correction Sound Energy Correction % Total Transmitted Energy Glazing Component 2 Component Category: Room Correction Frequency Correction % Total Transmitted Energy Sound Energy Correction Require Glazing STC Combined Glazing STC 160215 BPN56 STC Reqts 92 Plains Rd 16 0006.xlsx\BPN56 Road

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