Noise and Vibration Impact Study Fairview Development City of Burlington, Ontario

Size: px
Start display at page:

Download "Noise and Vibration Impact Study Fairview Development City of Burlington, Ontario"

Transcription

1 Noise and Vibration Impact Study Fairview Development City of Burlington, Ontario For Molinaro Group - Fairview JV Development 761 Brant Street, Suite 202 Burlington, ON L7R 2H4 Prepared by: Darryl McCumber, BASc, EIT Reviewed by: Brian Chapnik, PhD, PEng December 6, 2012

2 CONTENTS 1 INTRODUCTION AND SUMMARY SITE AND AREA DESCRIPTION NOISE AND VIBRATION CRITERIA ROAD AND RAIL NOISE GROUND-BORNE VIBRATION RAILWAY CONDITIONS FOR RESIDENTIAL DEVELOPMENTS STATIONARY SOURCE NOISES ROAD AND RAIL TRANSPORTATION NOISE ROAD TRAFFIC DATA BUS TRAFFIC DATA RAIL TRAFFIC DATA TRANSPORTATION NOISE PREDICTIONS TRANSPORTATION NOISE DISCUSSION AND RECOMMENDATIONS OUTDOOR LIVING AREAS VENTILATION REQUIREMENTS GLAZING EXTERIOR WALL CONSTRUCTIONS WARNING CLAUSES RAIL VIBRATION ASSESSMENT SITE MEASUREMENTS VIBRATION CONTROL SUMMARY OF RECOMMENDATIONS Figure 1: Key Plan Showing Fairview Figure 2: Fairview Site Plan Figure 3: Measurement Locations Figure : Vibration Measurements Appendix A Principal Mainline Requirements Appendix B Road and Rail Traffic Data

3 Fairview Development, Burlington Page 1 1 INTRODUCTION AND SUMMARY HGC Engineering was retained by The Molinaro Group to conduct a noise and vibration impact study for the proposed Fairview mixed use development to be located east of the intersection of Brant Street and Fairview Street, in the City of Burlington, Ontario. This study is required to support an application for site plan approval. This study is based on the preliminary site plan prepared by Graziani + Corazza Architects Inc. dated November 9, 2012, and preliminary drawings of the development. These preliminary drawings indicate that the development will consist of 5 residential towers above a common underground parking area. Towers A, B, and C will be located above a common 3-storey podium. Towers D and E are separated from the other towers and are located above a common 4-storey podium. The primary noise sources impacting the development were determined to be road traffic on Fairview Street and The Queen Elizabeth Way, and rail traffic on the Canadian National (CN) railway subdivisions to the north. Bus traffic associated with the Burlington GO Station to the east has also been assessed. Traffic volumes for the roadways and rail lines were obtained from the relevant authorities and adjusted as warranted to account for future potential growth. The road and rail traffic data were used to estimate future sound levels (L EQ ) at the location of the proposed building facades. The estimated sound levels were evaluated with respect to the guidelines of the Ministry of Environment (MOE) and the railways. Screens or other localized landscaping features can be considered in the design of the 3 rd floor amenity terrace on the north side of the development to help create quieter zones in this large outdoor amenity space. Similar considerations can be made for the 10 th floor terraces. Alternatively 3 m barriers would be required to protect these spaces. The impact of vibrations from the CN railway line to the north of the development has also been assessed. With suitable isolation measures integrated into the design of the foundation, it is

4 Fairview Development, Burlington Page 2 expected that sound and vibration from the rail line impacting the building can be reduced to reasonable levels for residential occupancies. The Burlington GO station is located directly to the east. Noises related to the station (warning bells) are considered safety measures which are exempt from assessment. A Walmart retail building is located to the west of the development. During our visit, no audible noise from the Walmart building was detected. While there are a number of industries located to the north of the development, there were no audibly significant sources of industrial noise noted during our visit. Central air conditioning is required for all residential units in the proposed buildings so that bedroom windows can remain closed against the night-time traffic noise, and will be provided in any case. Minimum acoustical ratings for the external façade elements are specified herein, which are anticipated to provide sufficient acoustical insulation for the indoor spaces. All residential units in the development will require noise warning clauses. Suggested wording for such clauses is provided herein. 2 SITE AND AREA DESCRIPTION The site is located east of the intersection of Fairview Street and Brant Street, on Fairview Street, in the City of Burlington. Figure 1 shows a key plan of the area and Figure 2 shows the development site plan. The development will consist of five residential towers. Three of the residential towers are located above a common 3-storey podium, and are connected by 9-storey podium sections. Each of the towers (A, B, C, D, and E) is indicated to be 20-storeys tall. Three levels of underground parking are currently shown, and there will be three levels of above grade parking located on the north side of the podium, facing the rail line. The first four floors of Towers D and E are indicated to include commercial and office space. The 4 th and 5 th floors of the development are

5 Fairview Development, Burlington Page 3 shown to include amenity space. The remainder of the buildings generally consists of residential suites. Fairview Street is located immediately south of the development. The CN Oakville (immediately adjacent) and CN Halton (approximately 280 m north-west) subdivisions are located north of the development, with the Queen Elizabeth Way beyond (approximately 650 m north of the development). The CN rail corridor and Fairview Street are the predominant sources of traffic noise in the area. Bus traffic associated with the GO station is accounted for in the road traffic volumes for the surrounding roadways. The Burlington GO Station is located directly to the east of the site. During our site visit conducted on August 2, 2012, it was noted that noise from bus traffic at this location was audible, and has therefore been included in our model of the site. When trains were operated in reverse, a warning bell is operated. Communications with GO transit staff indicate that these bells are safety devices used for warning purposes only, and are thus exempt from noise assessment under MOE guidelines. Other occasional noises emitted from this station (such as occasional announcements over the outdoor PA system) are not anticipated to be an issue. A Walmart retail store is located to the west of the development. However, the store parking lot separates the retail building from the development. During our visit, no audible noises from the Walmart building were detected. This facility may generate some audible noise at times, but no sources of particular concern were identified. Loading bays were noted to be on the north side of the facility, facing the tracks. Walmart is indicated to operate between 7:00am and 11:00 pm every day of the week. During our site visit it was also noted that there were several industrial buildings located north of the development, on the other side of the railway tracks. These include Bull Moose Tube Limited, and Cap Brick. No noise from these facilities was audible during our visit.

6 Fairview Development, Burlington Page 4 Cap Brick is located north-west of the development. Cap Brick operates between the hours of 7:00 am and 5:00 pm Monday to Friday, and 8:00 am to 2:00 pm on Saturdays. It was noted that the site operates as a sales and distribution centre, with a large amount of outdoor storage. Bull Moose Tube Company is located north-east of the development. The hours of operation of this plant are unknown. The company produces tube steel of various sizes. 3 NOISE AND VIBRATION CRITERIA 3.1 Road and Rail Noise Criteria for acceptable levels of noise are contained in the Ontario Ministry of Environment (MOE) publication LU-131, "Noise Assessment Criteria in Land Use Planning, 1997". Sound level limits from road and rail traffic sources are summarized in Table I below. Table I: Road/Rail Traffic Noise Criteria [dba] Area Daytime L EQ (16 hour) Night-time L EQ (8 hour) Outdoor Living Area Living or dining areas of residences, hospitals, schools, day-care centres, nursing/retirement homes, etc. 45 / Sleeping Quarters (bedrooms) / 35 Daytime refers to the period between 07:00 and 23:00. Night-time refers to the period between 23:00 and 07:00. Living areas include dining rooms, dens, studies, etc. Kitchens and washrooms are usually not considered to be noise-sensitive areas. The term "Outdoor Living Area" (OLA) is used in reference to an outdoor patio, a backyard, a terrace, a playground or other area where passive outdoor recreation is expected to occur. Balconies with a depth of less than 4 meters (measured perpendicular to the building façade) are not considered OLAs under MOE guidelines, and accordingly the noise criteria are not

7 Fairview Development, Burlington Page 5 applicable there. Balconies with a usable depth greater than 4 meters are considered to be OLAs and are subject to the outdoor noise guideline of 55 dba. Outdoor living areas generally have to be of a certain minimum size or dimension in order to qualify for acoustic protection. While there are no specific criteria for condominiums, for townhouses, terraces less than 400 ft 2 do not require a traffic noise assessment. The outside sound levels are determined considering the combination of all transportation noise sources. In cases where a minor excess (up to 5 db) over the sound level limit in an OLA is anticipated, MOE guidelines allow the excess to be addressed by including a warning clause in the titles, deeds or tenancy agreements for the affected dwellings. Where OLA sound levels exceed 60 dba, physical noise control measures, such as an acoustical barrier, are required. Where the noise is dominated by road traffic and outdoor façade sound levels exceed 60 dba at night-time or 65 dba during the daytime, building components must be designed to achieve the specified indoor sound level criteria, and central air conditioning is required so that windows can remain closed against the noise. Where the outdoor sound levels are dominated by rail traffic, these thresholds are 5 db lower, and exterior wall constructions should include brick or masonry (or an acoustical equivalent acceptable to the railways) at any location within 100 m of the railway right-of-way. The indoor sound level limits for rail sources are also 5 db more stringent than for road sources, to account for the additional low-frequency (rumble) components of locomotives, hence the façade sound insulation requirements are calculated separately and then combined. Safety devices associated with transportation sources (back-up beepers, warning bells or sirens) are exempt from consideration under MOE guidelines.

8 Fairview Development, Burlington Page Ground-Borne Vibration Criteria for rail vibrations are not provided by the MOE, but are stipulated in guideline documents circulated by CNR and GO Transit (see Appendix A). These guidelines require that a vibration assessment be performed for any dwelling within 75 m of the railway right-of-way, and that measured levels on the site during any part of a train pass-by should not exceed 0.14 mm/s. Further, GO/CNR stipulates that where measured levels on the ground exceed this threshold, isolation measures will be required to ensure that vibration levels impacting residential living areas do not exceed 0.14 mm/s (RMS). Vibration levels are typically measured in terms of oscillatory velocity or acceleration. A vibration velocity level of 0.14 mm/s correlates approximately with the threshold of human perception of vibrations, which can also be represented by vibration acceleration curves versus frequency, as outlined in ISO or ANSI S3.29. For this assessment, the frequencydependent acceleration curves are used to evaluate the ground-borne vibration measurements, as these give more accurate information about the nature of the vibrations. The levels discussed herein are presented in dbg, which refers to decibels of acceleration relative to the acceleration of gravity, as a function of one-third (1/3) octave band frequencies (Hz). The levels have been plotted against American National Standards Institute (ANSI) and International Standards Organization (ISO) criteria ANSI S3.29 and ISO for the threshold of human perception of vibrations. The ANSI/ISO criteria do not address noise; vibrations at frequencies over 20 Hz are of concern for re-radiated noise, even at levels well below the tactile perceptibility threshold. To illustrate this, vibration levels have been plotted against noise criterion (NC) curves. Experience suggests that while the train pass-bys will be audible in the building to some extent, if the levels impacting any noise sensitive spaces (e.g. residential units) are confined to about NC-30 (35 dba) or lower, the audibility of the pass-bys may be considered reasonable. This criterion level is similar to what is used by the TTC to assess the potential for intrusions from future

9 Fairview Development, Burlington Page 7 undertakings (subway expansions), and similar to criteria used by the US Federal Transit Administration to assess ground-borne noise intrusions from subways and trains. 3.3 Railway Conditions for Residential Developments Notwithstanding the noise and vibration criteria outlined above, CN Rail and GO Transit publish a recommended list of generic conditions, including specific setbacks, berm heights, and warning clauses, to reduce the incompatibility of residential developments adjacent or in close proximity to the railway right-of-way. Copies of these lists are included in Appendix A to this report. Some of the listed items relate to noise and vibration control. 3.4 Stationary Source Noises Industrial or commercial facilities or activities are referred to as stationary sources, and are typically assessed under a different set of criteria than transportation sources. The area is considered to be a Class I (urban) acoustical environment. There are several facilities in close proximity to the site, including a Walmart to the west, and several industries across the rail line to the north. Observations about these facilities were made while on site, as described above, but no detailed assessment has been performed. In any case, an associated warning clause should be considered. Suggested wording is as follows: Purchasers/tenants are advised that due to the proximity of this development to nearby retail and commercial facilities, sound levels from the facilities may at times be audible. Note that the Burlington GO station has not been considered as a stationary source in this context, but is considered separately below under Transportation Noise (Section 5).

10 Fairview Development, Burlington Page 8 4 ROAD AND RAIL TRANSPORTATION NOISE 4.1 Road Traffic Data Traffic data for the key roads throughout the site area and surrounding the site was obtained from the City of Burlington Traffic Services and is contained within Appendix B. Traffic volumes were conservatively assumed to grow at a typical rate of 2.5%/yr on all roadways, and average future daytime (07:00 to 23:00) and night-time (23:00 to 07:00) hourly volumes that will exist in 10 years (2022) were then calculated. The resulting future traffic volumes are listed in Table II, in addition to calculated and/or assumed commercial vehicle (truck) percentages and the posted speed limit for each roadway. An 85%/15% day/night split was used for both Brant Street and Fairview Street. Table II: 2022 Projected Road Traffic Data Daytime (7 am to 11 pm) Combined Two-way Traffic South of X North of X East of X West of X Cars HT Total Night-time (11 pm to 7 am) Combined Two-way Traffic South of X North of X East of X West of X Cars HT Total Notes: Brant Street is posted for a 50km/h speed limit, and Fairview Street is posted for a 60km/h speed limit. 'X' refers to the intersection of Fairview Street and Brant Street. Road traffic data for the Queen Elizabeth Way was obtained from the Ministry of Transportation and escalated to 2022 at a conservative growth rate of 2.5%/yr. An 88%/12% day/night split was determined from hourly traffic volumes. This was used to calculate average daytime and nighttime volumes, resulting in 8569 vehicles per hour during the daytime and 2328 vehicles per hour during the night-time. A commercial vehicle percentage of 25% was used for both daytime and nighttime volumes. These vehicles were assumed to be travelling at the posted maximum speed for the highway (100 km/hr).

11 Fairview Development, Burlington Page Bus Traffic Data Bus traffic from the GO Station was also obtained from GO Transit representatives, and was included in the acoustic model. A total of 25 arrivals and 28 departures take place during a typical weekday, and 18 arrivals and 18 departures take place during the weekend. Average daytime and night-time volumes were estimated to be 2 buses per hour. 4.3 Rail Traffic Data Rail traffic data was obtained from both GO Transit and CN representatives and is contained in Appendix B. These data were escalated to the year 2022 at an assumed growth of 2.5%/year, as required by MOE and CN guidelines. The rail volumes used in the analysis are summarized in Table III. Type of Train Number of Train Day / Night Table III: 2022 Projected Rail Traffic Data Number of Locomotives Number of Cars Maximu m Speed (km/h) Speed used North of Development (km/h) CN Oakville Subdivision Freight 1 / Way Freight 6 / Passenger 19 / GO Train 86 / CN Halton Subdivision Freight 17 / Way Freight 9 / Passenger 20 / Per discussions with GO Transit (See Appendix A), all GO trains are understood to stop at the station. A speed of 50 km/hr was used in the area north of the development for all GO Trains. 4.4 Transportation Noise Predictions To assess the levels of traffic noise which will impact the site in the future, predictions were made using a numerical computer modeling package (Cadna-A version ). The model is

12 Fairview Development, Burlington Page 10 based on the methods from ISO Standard , Acoustics - Attenuation of Sound During Propagation Outdoors, which accounts for reduction in sound level with distance due to geometrical spreading, air absorption, ground attenuation and acoustical shielding by intervening structures. The rail lines were included in the model as line sources with sound power levels equivalent to those published by the Department of Transportation (United States of America) Federal Transit Administration (FTA) in the publication entitled, Transit Noise and Vibration Impact Assessment. The road noise sources have been included in the model using the basic road element included in Cadna/A, which follows the German guideline RLS-90 for road traffic noise predictions. Our experience suggests that train sound levels predicted by FTA and road sound levels predicted by RLS-90 are reasonably accurate. The model road traffic values have been qualified on similar projects to be within 1-2 dba of those predicted in STAMSON 5.04, a computer algorithm developed by the MOE. Predictions of overall sound levels from all road/rail sources were made at various representative façade locations throughout the site. The predicted maximum sound levels from both road and rail impacting each tower are summarized in Table IV. Table IV: Sound Level Predictions [dba] from Future Traffic Location Day (16hr avg) Night (8hr avg) Road Rail Total Road Rail Total Podium (9-storey section) Tower A Tower B Tower C Tower D Tower E

13 Fairview Development, Burlington Page 11 5 TRANSPORTATION NOISE DISCUSSION AND RECOMMENDATIONS The predictions indicate that the future traffic sound levels will exceed MOE guidelines at the residential façades in the proposed development. Recommendations to address these excesses are discussed below. 5.1 Outdoor Living Areas The preliminary building plans indicate a landscaped roof area on north side of the 3-storey podium. This space is indicated to be used as an outdoor amenity terrace. This terrace is greater than 4 m in depth and therefore subject to the MOE criteria outlined in Table I. Assuming a standard 1.07 m parapet around the perimeter of the space, daytime sound levels were estimated to be in the range of dba. To reduce the sound level to within 60 dba throughout the terrace, a 6 m barrier would be required around the perimeter of the podium roof, which is not considered feasible. Consideration should be given in detail design to integrating some smaller structures, screens or landscaping features to create quiet pockets or zone on the larger terrace. There are other amenity terraces located on the south side of the podium and between Towers D and E, as shown in Figure 2. There is also a landscaped courtyard located in the centre of the development. Assuming a 1.07m high solid parapet or guard, predicted sound levels for the outdoor amenity terraces on the south side of the podium are between 55 and 60 dba, and sound levels for the terrace between Towers D and E and in the central landscaped courtyard are also less than 60 dba. Therefore no additional mitigation measures are anticipated to be required. There are a number of terraces on the 10 th and 13 th floors, which are greater than 400 sq ft in area. These terraces are subject to MOE criteria. Predicted sound levels on the 10 th floor terraces between Towers A and B and Towers B and C exceed 60 dba. In order to protect these spaces, a solid barrier 3 m in height would be required along the north side of the area. If these measures are not considered feasible, consideration could also be given in detail design to

14 Fairview Development, Burlington Page 12 integrating some smaller structures, screens or landscaping features to create quiet pockets or zone on the larger terrace. Assuming a 1.07 m high solid parapet or guard, predicted sound levels for the 10 th and 13 th floor terraces located on Towers D and E are less than 60 dba. Therefore, no additional mitigation measures are required. 5.2 Ventilation Requirements The predicted night-time sound levels at practically all facades throughout the site exceed 60 dba, and thus central air conditioning systems are required so that windows may remain closed. 5.3 Glazing Floor plans and elevations have not yet been sufficiently developed for the detailed acoustical specification of the building envelope. For the purposes of this preliminary analysis, typical window-to-floor areas were assumed to be 50% (i.e. 40% fixed, 10% operable relative to floor area). Based upon this assumption, the glazing for residential suites with direct exposure to the rail line should achieve the sound transmission class ratings shown in Table V. However, in an urban environment such as this, we do not typically recommend less than STC-34.

15 Fairview Development, Burlington Page 13 Table V: Preliminary Glazing Requirements* Location Fixed Glazing Requirement Operable Glazing Requirement Podium (9-storey section) Tower A Tower B Tower C Tower D Tower E *Based on assumed 50% window-to-floor area ratio Façades with less exposure to the CN rail corridor are somewhat less impacted, and accordingly a lower STC would be acceptable while still meeting the indoor targets. Conversely, if more glazing is incorporated, higher STC requirements may apply. Acoustical criteria for different façades can be optimized as part of the detail design of the building envelope, if required. 5.4 Exterior Wall Constructions The building exterior walls will consist largely of metal or glass spandrel panels with some areas of precast concrete or masonry. Exterior walls that are not glazed should have sufficient acoustical insulation value such that the noise transmitted through is negligible in comparison with the windows. Spandrel or metal panels with typical sound insulation ratings of STC-35 to 40, backed by an independent insulated drywall assembly, should meet these requirements. 5.5 Warning Clauses MOE guidelines recommend that appropriate warning clauses be included in the property titles, purchase and sale agreements, and tenancy agreements of properties where anticipated traffic sound level excesses are identified. The actual wording of the warning clause depends on the nature of the excess. Two clauses are recommended as follows. (a) Purchasers/tenants are advised that despite the inclusion of noise control features in the development and within the building units, sound levels due to increasing road/rail traffic may on occasion interfere with some activities of the dwelling

16 Fairview Development, Burlington Page 14 occupants as the sound levels exceed the Municipality s and the Ministry of the Environment s noise criteria. (b) This dwelling unit has been supplied with a central air conditioning system which will allow windows and exterior doors to remain closed, thereby ensuring that the indoor sound levels are within the Ministry of Environment s noise criteria. In addition, CN and GO Transit will require specific warning clauses to protect their interests. Representative wording for such a clause is suggested in the guideline documents provided in Appendix A, and reads as follows: Warning: <Canadian National Railway><GO Transit> or its assigns or successors in interest has or have a rights-of-way within 300 metres from the land the subject hereof. There may be alterations to or expansions of the railway facilities on such rights-of-way in the future including the possibility that the railway or its assigns or successors as aforesaid may expand its operations, which expansion may affect the living environment of the residents in the vicinity, notwithstanding the inclusion of any noise and vibration attenuating measures in the design of the development and individual dwelling(s). <CN><GO> will not be responsible for any complaints or claims arising from the use of such facilities and/or operations on, over or under the aforesaid rights-of-way. Aside from the warning safety bells which sound when trains reverse at the Burlington GO station, which are exempt from assessment under MOE guidelines, other occasional sounds from the station may at times be audible. An associated warning clause is recommended to advise future residents about noises from the GO station. The following wording is suggested: Purchasers/tenants are advised that due to the proximity of this development to the Burlington GO station, sounds from associated operations may at times be audible.

17 Fairview Development, Burlington Page 15 6 RAIL VIBRATION ASSESSMENT 6.1 Site Measurements Ground-borne vibration measurements of rail pass-by events were conducted on site at the edge of the CN Oakville Subdivision right-of-way (corresponding to the proposed podium location), and at the location of the closest future towers which are set back 30 m from the right-of-way. Vibration measurements were conducted on August 2, Measurement locations are shown in Figure 3. Measurements were analyzed and compared to criteria as outlined in Section 3. The results indicate that vibration levels from train pass-bys were high, exceeding the criteria at the nearest measurement location (corresponding to the podium) for some pass-bys and approaching the criteria at the 30 setback, for some larger faster moving trains. Figures 4.1 to 4.3 display maximum vibration levels from representative rail pass-by events at several locations. There are occasional freight pass-bys on the Oakville line, but none on the day of measurement. Thus freight train pass-bys on this line were not measured. Such occasional pass-bys are expected to produce even higher levels than those measured. Notwithstanding this, the recommendations outlined herein are expected to be satisfactory to address this occasional source as well. 6.2 Vibration Control The degree of vibration transmission into the new structure will depend on the design of the foundation. Estimated re-radiated sound levels on the lower floors on the north side of the development are anticipated to be in the range of NC-45 to NC-50 during train pass-bys. Levels are expected to be lower on the upper floors of the development, and at the south towers (D and E). To further reduce vibration and noise transmitted by rail pass-bys into the building structure, consideration should be given in design to separating the podium structure from the adjacent

18 Fairview Development, Burlington Page 16 foundation walls using rubber isolation pads along the north side, returning for some distance along the east and west foundation walls. The design of the isolation pads depends on anticipated static and dynamic loads, and can be determined as required during detail design. In conjunction with such isolation measures, some additional features can be integrated into the structural design of the parking levels in order to better resist vibrations (e.g. heavier foundation wall, columns instead of shear walls, etc.). Selected measures can be developed further, as required, during detail design. As outlined above, the criteria for both sound and vibration are considered to be reasonable standards for acceptability. However, conformance with these standards does not imply that vibration levels will be imperceptible and/or sound levels will be inaudible. Therefore, consideration should be given to including warning clauses in all sales or rental agreements, and in Development Agreements with the municipality.

19 Fairview Development, Burlington Page 17 7 SUMMARY OF RECOMMENDATIONS The following list summarizes the recommendations made in this report: 1. For the outdoor amenity space located on the north side of the 3 rd floor podium, integration of localized screens or alternative landscaping features should be considered during detail design to create some quieter zones within the overall terrace area. For the 10 th floor terraces located on the north podium, a barrier 3 m in height is required to limit sound levels to less than 60 dba. Alternatively the size of the useable space could be limited, or landscaping features could be implemented. 2. Central air conditioning systems will be required for all dwelling units in the building. 3. The suggested minimum STC requirements for the glazing elements are anticipated to provide sufficient acoustical insulation for the indoor spaces, provided that window areas represent 50% or less of the floor area of each adjacent room. This should be reviewed when detailed floor plans and elevations are available, and adjustments made as required to suit spaces which may have greater areas of glazing. Higher STC values should be considered where feasible, to provide an additional safety factor. Seals on doors and operable windows must be tight and effective, to reduce leaks to the extent feasible. 4. Exterior wall assemblies will need to be verified in detailed design to ensure that noise transmitted through is negligible in comparison with the windows. 5. Warning clauses should be included in the property and tenancy agreements and offers of purchase and sale to inform future residents of the traffic noise issues, the railway right of way, and the proximity to the Burlington GO Station and to industries and commercial facilities in the area. The specific number and wording of warning clauses for this development are subject to discussions with the City and all stakeholders, and will

20 Fairview Development, Burlington Page 18 ultimately be incorporated into the list of conditions associated with planning approvals for this site. 6. Vibration levels from train pass-bys may exceed the suggested design criteria at the location of the nearest towers. Consideration should be given to including isolation measures against the north foundation wall, returning for some distance along the east and west foundation walls.

21 Fairview Development, Burlington Page 19 Industrial Areas GO Parking GO Station Fairview Project North True North Walmart Figure 1: Key Plan Showing Fairview Development

22 Fairview Development, Burlington Page 20 Amenity Space 10 th Floor Terraces Amenity Space 13 th Floor Terraces 10 th Floor Terraces Figure 2: Fairview Development Site Plan

23 Fairview Development, Burlington Page 21 Closest Point of Development (Podium) 30 meter setback (Towers A, B, C) Measurement Locations Figure 3: Measurement locations

24 Fairview Development, Burlington Page Vibration Vs. Criteria Eastbound Go Train m East Bound GO Train - 30 m NC-60 Vibration Level, dbg ANSI/ISO Curve NC-50 NC-40 NC-30 NC /3 Octave Band Mid-Frequency, Hz Figure 4.1: Vibration Measurements GO Train Pass-by Vibration Vs. Criteria Eastbound GO Train m Eastbound GO Train - 30 m NC-60 Vibration Level, dbg ANSI/ISO Curve NC-50 NC-40 NC-30 NC /3 Octave Band Mid-Frequency, Hz Figure 4.2: Vibration Measurements GO Train Pass-by

25 Fairview Development, Burlington Page 23 Vibration Vs. Criteria Eastbound Via Train m Eastbound Via Train - 30 m NC-60 Vibration Level, dbg ANSI/ISO Curve NC-50 NC-40 NC-30 NC /3 Octave Band Mid-Frequency, Hz Figure 4.3: Vibration Measurements - VIA Rail Pass-by

26 Fairview Development, Burlington Page 24 Appendix A- Principal Mainline Requirements

27 PRINCIPAL MAIN LINE REQUIREMENTS A. Safety setback of dwellings from the railway rights-of-way to be a minimum of 30 metres in conjunction with a safety berm. The safety berm shall be adjoining and parallel to the railway rights-of-way with returns at the ends, 2.5 metres above grade at the property line, with side slopes not steeper than 2.5 to 1. B. Noise attenuation barrier shall be adjoining and parallel to the railway rights-of-way, having returns at the ends, and a minimum total height of 5.5 metres above top-of-rail. Acoustic fence to be constructed without openings and of a durable material weighing not less than 20 kg. per square metre of surface area. Subject to the review of the noise report, GO Transit may consider other measures recommended by an approved Noise Consultant. C. Ground-borne vibration transmission to be evaluated in a report through site testing to determine if dwellings within 75 metres of the railway rights-of-way will be impacted by vibration conditions in excess of 0.14 mm/sec RMS between 4 Hz and 200 Hz. The monitoring system should be capable of measuring frequencies between 4 Hz and 200 Hz, + 3 db with an RMS averaging time constant of 1 second. If in excess, isolation measures will be required to ensure living areas do not exceed 0.14 mm/sec RMS on and above the first floor of the dwelling. D. The Owner shall install and maintain a chain link fence of minimum 1.83 metre height along the mutual property line. E. The following clause should be inserted in all development agreements, offers to purchase, and agreements of Purchase and Sale or Lease of each dwelling unit within 300m of the railway right-of-way. Warning: The Greater Toronto Transit Authority, carrying on business as GO Transit, and its assigns and successors in interest has or have a right-of-way within 300 metres from the land the subject hereof. There may be alterations to or expansions of the rail facilities on such right-of-way in the future including the possibility that GO Transit or any railway entering into an agreement with GO Transit to use the right-ofway or their assigns or successors as aforesaid may expand their operations, which expansion may affect the living environment of the residents in the vicinity, notwithstanding the inclusion of any noise and vibration attenuating measures in the design of the development and individual dwelling(s). GO Transit will not be responsible for any complaints or claims arising from use of such facilities and/or operations on, over or under the aforesaid right-of-way. F. Any proposed alterations to the existing drainage pattern affecting the railway right-of-way must receive prior concurrence from GO Transit and be substantiated by a drainage report to the satisfaction of GO Transit. G. The Owner shall through restrictive covenants to be registered on title and all agreements of purchase and sale or lease provide notice to the public that the safety berm, fencing and vibration isolation measures implemented are not to be tampered with or altered and further that the Owner shall have sole responsibility for and shall maintain these measures to the satisfaction of GO Transit. H. The Owner enter into an Agreement stipulating how GO Transit s concerns will be resolved and will pay GO Transit s reasonable costs in preparing and negotiating the agreement. I. The Owner may be required to grant GO Transit an environmental easement for operational emissions, registered on title against the subject property in favour of GO. August, 2006

28

29 Fairview Development, Burlington Page 25 Appendix B- Road and Rail Traffic Data

30

31

32

33 AECOM 5080 Commerce Boulevard tel Mississauga, ON, Canada L4W 4P fax Transmittal Form Date August 13, 2012 Project Number Contact Derryl McCumber Routing Company HGC Engineering Howe Gastmeier Chapnik Limited Address 2000 Argentia Road, Plaza One, Suite 203 Mississauga, Ontario L5N 1P7 Telephone # Sent By Patricia Henriques Copies To Nick Coleman, CN Adam Snow, Metrolinx Project Name Train Traffic Data CN s Oakville Subdivision north of Fairview Street and east of Brant Street, Burlington, Ontario Approximately at Mile and CN s Halton Subdivision north of Fairview Street and east of Brant Street, Burlington, Ontario - Approximately at Mile Urgent X For Your Use For Review For Your Information Confidential Comments: Please find attached the requested Train Traffic Data. Should you have any questions, please do not hesitate to contact the undersigned at ext Sent Via: mail courier picked up by hand X fax other Authorized Signature: Name (please print): Patricia Henriques Title: Project Coordinator RPT Train Traffic-HGC.Docx

34 Page 2 August 13, 2012 Darryl McCumber HGC Engineering Howe Gastmeier Chapnik Limited 2000 Argentia Road, Plaza One, Suite 203 Mississauga, Ontario L5N 1P7 Dear Darryl: Project No: Regarding: Train Traffic Data CN s Oakville Subdivision north of Fairview Street and east of Brant Street, Burlington, Ontario Approximately at Mile The following is provided in response to your August 1 st, 2012 request for information regarding rail traffic north of Fairview Street and east of Brant Street, Burlington, Ontario, at Mile on CN s Oakville Subdivision. Typical daily traffic volumes are recorded below. However, traffic volumes may fluctuate due to overall economic conditions, varying traffic demands, weather conditions, track maintenance programs, statutory holidays and traffic detours that when required may be heavy although temporary. Typical daily traffic volumes at this site location are as follows: *Maximum train speed is given in Miles per Hour Eastbound Type of Train Volumes Max. Consist Max. Speed Max. Power Freight Way Freight Passenger Westbound Type of Train Volumes Max. Consist Max. Speed Max. Power Freight Way Freight Passenger Eastbound Type of Train Volumes Max. Consist Max. Speed Max. Power Freight Way Freight Passenger Westbound Type of Train Volumes Max. Consist Max. Speed Max. Power Freight Way Freight Passenger RPT Train Traffic-HGC.Docx

35 Page 3 August 13, 2012 The volumes recorded reflect eastbound and westbound way freight, freight and passenger operations on CN s Oakville Subdivision. Not included in the above data are GO Transit commuter trains running east and west on the Oakville Subdivision. For information regarding existing and projected commuter operations, Mr. Adam Snow, Transportation Planner, should be contacted directly through GO Transit/Metrolinx offices at 20 Bay Street, Suite 600, Toronto, Ontario M5J 2W3, Fax and phone Except where anti-whistling bylaws are in effect, engine-warning whistles and bells are normally sounded at all at-grade crossings. There are no at-grade road crossings in the immediate vicinity of the study area. Please note that engine warning whistles may be sounded in cases of emergency, as a safety and or warning precaution at station locations and pedestrian crossings and occasionally for operating requirements. With respect to equipment restrictions, the gross weight of the heaviest permissible car is 286,000 lbs. The three mainline tracks of the Oakville Subdivision are constructed of continuously welded rail throughout the study area. Be advised, at Mile and at Mile there are switches leading to siding tracks. Also, the presence of various switches, connected between Mile and Mile 32.48, may exacerbate the noise and vibration caused by train movements. The Junction at Mile will result in additional sharp sound impulses, as well as additional vibration caused by movements of the trains. This Junction connects the Halton Subdivision. RPT Train Traffic-HGC.Docx

36 Page 4 August 13, 2012 Regarding: Train Traffic Data CN s Halton Subdivision north of Fairview Street and east of Brant Street, Burlington, Ontario - Approximately at Mile The following is provided in response to your August 1 st, 2012 request for information regarding rail traffic north of Fairview Street and east of Brant Street, Burlington, Ontario at approximately Mile Halton Subdivision. Typical daily traffic volumes are recorded below. However, traffic volumes may fluctuate due to overall economic conditions, varying traffic demands, weather conditions, track maintenance programs, statutory holidays and traffic detours that when required may be heavy although temporary. Typical daily traffic volumes at this site location are as follows: *Maximum train speed is given in Miles per Hour Eastbound Type of Train Volumes Max. Consist Max. Speed Max. Power Freight Way Freight Passenger Westbound Type of Train Volumes Max. Consist Max. Speed Max. Power Freight Way Freight Passenger Eastbound Type of Train Volumes Max. Consist Max. Speed Max. Power Freight Way Freight Passenger Westbound Type of Train Volumes Max. Consist Max. Speed Max. Power Freight Way Freight Passenger The volumes recorded reflect eastbound and westbound freight, way freight and passenger operations on CN s Halton Subdivision. Except where anti-whistling bylaws are in effect, engine-warning whistles and bells are normally sounded at all at-grade crossings. There are no at-grade crossings in the immediate vicinity of the study area. Please note that engine warning whistles may be sounded in cases of emergency, as a safety and or warning precaution at station locations and pedestrian crossings and occasionally for operating requirements. RPT Train Traffic-HGC.Docx

37 Page 5 August 13, 2012 With respect to equipment restrictions, the gross weight of the heaviest permissible car is 286,000 lbs. The two mainline tracks of the Halton Subdivision are constructed of continuously welded rail throughout the study area. The Junction at Mile 49.5 will result in additional sharp sound impulses, as well as additional vibration caused by movements of the trains. Be advised, at Mile there is a switch leading to siding tracks. This Junction connects to the Oakville Subdivision. The Canadian National Railway continues to be strongly opposed to locating developments near railway facilities and rights-of-way due to potential safety and environmental conflicts. Development adjacent to the Railway Right-of-Way is not appropriate without sound impact mitigation measures to reduce the incompatibility. For confirmation of the applicable rail noise, vibration and safety standards, Mr. Nick Coleman, Canadian National Railway Properties at should be contacted directly. We trust the above information will satisfy your current request. Sincerely, AECOM Canada Ltd. Patricia Henriques patricia.henriques@aecom.com cc: Nick Coleman, CN Adam Snow, Metrolinx RPT Train Traffic-HGC.Docx

NOISE AND VIBRATION FEASIBILITY STUDY 316 BLOOR STREET WEST CITY OF TORONTO, ONTARIO

NOISE AND VIBRATION FEASIBILITY STUDY 316 BLOOR STREET WEST CITY OF TORONTO, ONTARIO NOISE AND VIBRATION FEASIBILITY STUDY 316 BLOOR STREET WEST CITY OF TORONTO, ONTARIO Prepared for: State Building Group Attn.: John Guanti 27 Dufferin Street, Unit 34 Toronto, Ontario M6B 4J3 Prepared

More information

Noise Feasibility Study Proposed Residential Building 103 Dundas Street West Oakville, Ontario

Noise Feasibility Study Proposed Residential Building 103 Dundas Street West Oakville, Ontario Noise Feasibility Study Proposed Residential Building 103 Dundas Street West Oakville, Ontario Prepared for: 103 Dundas Corporation Attn: Zaki Wahbeh 2184 Providence Road Oakville, ON L6H 6Z2 Prepared

More information

Noise Feasibility Study EMGO (North Oakville I) Ltd., Town of Oakville, Ontario

Noise Feasibility Study EMGO (North Oakville I) Ltd., Town of Oakville, Ontario Noise Feasibility Study EMGO (North Oakville I) Ltd., Town of Oakville, Ontario For Emgo (North Oakville I) Ltd. 2173 Turnberry Road Burlington, ON L7M 4P8 Prepared by Victor Garcia, BASc Reviewed by Sheeba

More information

Merivale Road Residential Development 1683 Merivale Road Noise Control Study

Merivale Road Residential Development 1683 Merivale Road Noise Control Study Merivale Road Residential Development 1683 Merivale Road Noise Control Study Prepared By: NOVATECH ENGINEERING CONSULTANTS LTD. Suite 200, 240 Michael Cowpland Drive Ottawa, Ontario K2M 1P6 Submitted:

More information

NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 47 HAVELOCK STREET OTTAWA, ON. REVISED with ADDENDUM for ROOFTOP OUTDOOR LIVING AREA

NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 47 HAVELOCK STREET OTTAWA, ON. REVISED with ADDENDUM for ROOFTOP OUTDOOR LIVING AREA NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 47 HAVELOCK STREET OTTAWA, ON. REVISED with ADDENDUM for ROOFTOP OUTDOOR LIVING AREA REPORT PREPARED FOR SURFACE DEVELOPMENTS 61 FOREST HILL AVE. OTTAWA,

More information

Orangeville railway development corporation (ordc)

Orangeville railway development corporation (ordc) POLICY ON THE ENVIRONMENTAL PROTECTION OF NEW RESIDENTIAL DEVELOPMENT ADJACENT TO THE ORANGEVILLE BRAMPTON RAILWAY Prepared by: Orangeville railway development corporation (ordc) JANUARY 2001 Revised:

More information

Noise Feasibility Study Proposed Residential Development, 361 Tanbark Road Niagara-on-the-Lake, Ontario

Noise Feasibility Study Proposed Residential Development, 361 Tanbark Road Niagara-on-the-Lake, Ontario Noise Feasibility Study Proposed Residential Development, 361 Tanbark Road Niagara-on-the-Lake, Ontario Prepared for: Blythwood Homes Inc. 7058 Ridgewood Crescent Niagara Falls, Ontario L2J 3H1 Prepared

More information

Noise Feasibility Study, McGibbon Condominium 71 Main Street South Georgetown, Ontario

Noise Feasibility Study, McGibbon Condominium 71 Main Street South Georgetown, Ontario Noise Feasibility Study, McGibbon Condominium 71 Main Street South Georgetown, Ontario Prepared for: Attn: Don Jackson Silvercreek Commercial Builders Inc. 66 Mill Street Georgetown, Ontario L5C 1V8 Prepared

More information

Noise Feasibility Study Proposed Residential Development Old Barber House 5155 Mississauga Road City of Mississauga, Ontario

Noise Feasibility Study Proposed Residential Development Old Barber House 5155 Mississauga Road City of Mississauga, Ontario Noise Feasibility Study Proposed Residential Development Old Barber ouse 5155 Mississauga Road City of Mississauga, Ontario Prepared for: City Park (Old Barber) omes Inc. 950 Nashville Road Kleinburg,

More information

Environmental Noise Assessment 1020, 1024, 1028, 1032 & 1042 Sixth Line Oakville, ON

Environmental Noise Assessment 1020, 1024, 1028, 1032 & 1042 Sixth Line Oakville, ON Environmental Noise Assessment 1020, 1024, 1028, 1032 & 1042 Sixth Line Oakville, ON Novus Reference No. 16-0173 Version No. 1.0 (Final) September 30, 2016 NOVUS PROJECT TEAM: Specialist: Marcus Li, P.Eng.

More information

Mann Avenue Development 87 Mann Avenue Noise Control Study

Mann Avenue Development 87 Mann Avenue Noise Control Study Mann Avenue Development 87 Mann Avenue Noise Control Study Prepared By: NOVATECH ENGINEERING CONSULTANTS LTD. Suite 200, 240 Michael Cowpland Drive Ottawa, Ontario K2M 1P6 August 13, 2013 Novatech File:

More information

Noise Feasibility Study Stacked Townhouse Development Glenashton Drive (Block 55) Oakville, Ontario

Noise Feasibility Study Stacked Townhouse Development Glenashton Drive (Block 55) Oakville, Ontario Noise Feasibility Study Stacked Townhouse Development Glenashton Drive (Block 55) Oakville, Ontario Prepared for: Nathan Jamieson, P.Eng Senior Principal, Community Development Stantec Consulting Ltd 300W

More information

Noise Assessment Report

Noise Assessment Report Noise Assessment Report 176 Greenfield Avenue Prepared for: TC United Group Prepared by: Stantec Consulting Ltd. February 8, 2016 NOISE ASSESSMENT REPORT Introduction February 8, 2016 Table of Contents

More information

Table of Contents... ii 1. Introduction... 1

Table of Contents... ii 1. Introduction... 1 316 Somerset Street East SACL Project #SW18098 April 05, 2018 Page ii Table of Contents Table of Contents... ii 1. Introduction... 1 2. Noise Sources... 1 3. Noise Assessment Criteria... 1 3.1 Surface

More information

Environmental Noise Feasibility Assessment Proposed Guelph Woods Development Guelph, ON

Environmental Noise Feasibility Assessment Proposed Guelph Woods Development Guelph, ON Environmental Noise Feasibility Assessment Proposed Guelph Woods Development Guelph, ON Novus Reference No. 12-0292C DRAFT (v2.2) February 7, 2014 NOVUS PROJECT TEAM: Specialist: Marcus Li, B.Sc., B.Eng.Sc.

More information

1. Introduction Site Noise Impact... 1

1. Introduction Site Noise Impact... 1 Mixed Use Development SACL Report #B4-077 April 11, 2014 Table of Contents 1. Introduction... 1 2. Site... 1 3. Noise Impact... 1 3.1. Noise Sources... 1 3.2. Critical Noise Receptors... 1 3.3. Noise Levels...

More information

NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 12 HAMILTON AVENUE NORTH OTTAWA, ON.

NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 12 HAMILTON AVENUE NORTH OTTAWA, ON. NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 12 HAMILTON AVENUE NORTH OTTAWA, ON. REPORT PREPARED FOR SURFACE DEVELOPMENTS 61 FOREST HILL AVE. OTTAWA, ON, K2C 1P7 September 15, 2016 16419 1 NOISE IMPACT

More information

Noise and Vibration Feasibility Study 1 and 15 Stevenson St & 8 William St Guelph, Ontario

Noise and Vibration Feasibility Study 1 and 15 Stevenson St & 8 William St Guelph, Ontario Noise and Vibration Feasibility Study 1 and 15 Stevenson St & 8 William St Guelph, Ontario Prepared for: Jennark Homes 66 Wellington Road 7, Unit #1 Elora, Ontario N0B 1S0 Prepared by Rajjot Arora, BASc

More information

Noise Feasibility Study Proposed Residential Development Kemsley Farm St. Thomas, Ontario

Noise Feasibility Study Proposed Residential Development Kemsley Farm St. Thomas, Ontario Noise Feasibility Study Proposed Residential Development Kemsley Farm St. Thomas, Ontario Prepared for: Doug Tarry Limited 358 Elm Street St. Thomas, Ontario, N5R 1K1 Prepared by Victor Garcia, PEng Reviewed

More information

Noise Feasibility Study 2120 Hurontario Street and Grange Drive City of Mississauga, Ontario

Noise Feasibility Study 2120 Hurontario Street and Grange Drive City of Mississauga, Ontario Noise Feasibility Study 2120 Hurontario Street and Grange Drive City of Mississauga, Ontario For Gordon Woods Developments Limited c/o Edenshaw development Limited 260 Brunel Road Mississuaga, Ontairo

More information

Roadway Traffic Noise Assessment Chapel Street. Ottawa, Ontario

Roadway Traffic Noise Assessment Chapel Street. Ottawa, Ontario Roadway Traffic Noise Assessment 151-153 Chapel Street Ottawa, Ontario REPORT: GWE14-064 Noise Prepared For: Brad Caco Sun Life Financial Center, East Tower 3250 Bloor Street West, Suite 1000 Toronto,

More information

The anticipated critical noise receptors and their locations are identified as follows and are shown on Figure 3:

The anticipated critical noise receptors and their locations are identified as follows and are shown on Figure 3: 177 Cross Ave. B2-065 2 1.0 INTRODUCTION This document is a Noise and Vibration Impact Study regarding the proposed mixed use development at 177 Cross Avenue, Oakville. It is associated with rezoning application

More information

Noise Feasibility Study Proposed Hospice 2050 University Avenue East, Waterloo, Ontario

Noise Feasibility Study Proposed Hospice 2050 University Avenue East, Waterloo, Ontario Noise Feasibility Study Proposed Hospice 2050 University Avenue East, Waterloo, Ontario Prepared for: Hospice of Waterloo Region 298 Lawrence Avenue Kitchener, ON N2M 1Y4 Prepared by Sheeba Paul, MEng,

More information

Noise Assessment Report Riverside Drive Phase I

Noise Assessment Report Riverside Drive Phase I Noise Assessment Report - 2887 Riverside Drive Phase I Project # 160401333 Prepared for: Youth Services Bureau Prepared by: Stantec Consulting Ltd. Introduction Table of Contents 1.0 INTRODUCTION... 1

More information

Noise Feasibility Study Proposed Residential Development Brock Road Pickering, Ontario

Noise Feasibility Study Proposed Residential Development Brock Road Pickering, Ontario Noise Feasibility Study Proposed Residential Development Brock Road Pickering, Ontario Prepared for: Madison Brock Limited 369 Rimrock Road Toronto, Ontario M3J 3G2 Prepared by: Jingyi Guo Reviewed by:

More information

Guelph Curling Club Development Traffic Noise Impact Study

Guelph Curling Club Development Traffic Noise Impact Study Guelph Curling Club Development Traffic Noise Impact Study Development Location Prepared For: Guelph Curling Club Paradigm Transportation Solutions Ltd. 43 Forest Road Cambridge ON N1S 3B4 pgrubb@ptsl.com

More information

Noise Abatement Guidelines. Regional Official Plan Guidelines

Noise Abatement Guidelines. Regional Official Plan Guidelines Noise Abatement Guidelines Regional Official Plan Guidelines Halton Region Official Plan Guidelines The Regional Official Plan (ROP) is Halton s guiding document for land use planning. It contains policies

More information

Prepared for: Gapatas Inc Sherwoodtowne Boulevard, Unit 106 Mississauga, ON L4Z 1Y5. Our File No:

Prepared for: Gapatas Inc Sherwoodtowne Boulevard, Unit 106 Mississauga, ON L4Z 1Y5. Our File No: YARMOUTH HEIGHTS ESTATES PHASE IV PARTS 1,2,4,5 & 6 Plan 11R Being Part of Lot 9 Concession 8 Geographical Township of Yarmouth City of St. Thomas Prepared for: Gapatas Inc. 4255 Sherwoodtowne Boulevard,

More information

NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 47 HAVELOCK STREET OTTAWA, ON.

NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 47 HAVELOCK STREET OTTAWA, ON. NOISE IMPACT ASSESSMENT FOR SITE PLAN APPROVAL 47 HAVELOCK STREET OTTAWA, ON. REPORT PREPARED FOR SURFACE DEVELOPMENTS 61 FOREST HILL AVE. OTTAWA, ON, K2C 1P7 March 25, 2015 15078 1 NOISE IMPACT ASSESSMENT

More information

For The Regional Municipality of Waterloo 150 Frederick Street, 8 th Floor Kitchener, Ontario, N2G 4J3. Prepared by. Sheeba Paul, MEng, PEng

For The Regional Municipality of Waterloo 150 Frederick Street, 8 th Floor Kitchener, Ontario, N2G 4J3. Prepared by. Sheeba Paul, MEng, PEng Noise and Vibration Compatibility Feasibility Assessment Residential Component Proposed RMOW Transit Hub King Street West and Victoria Street North, Kitchener, ON For The Regional Municipality of Waterloo

More information

Draft Noise Abatement Guidelines

Draft Noise Abatement Guidelines Document under Separate Cover refer to IMLC01-13 Draft Noise Abatement Guidelines April 2013 Legislative & Planning Services Table of Contents 1.0 Introduction...1 1.1 Key Definitions...1 2.0 Existing

More information

Traffic and Stationary Noise Feasibility Study Proposed Lakeside Village Plaza 5353 Lakeshore Road Burlington, Ontario

Traffic and Stationary Noise Feasibility Study Proposed Lakeside Village Plaza 5353 Lakeshore Road Burlington, Ontario Traffic and Stationary Noise Feasibility Study Proposed Lakeside Village Plaza 5353 Lakeshore Road Burlington, Ontario Prepared for: United Burlington Retail Portfolio Inc. 986 St. Clair Ave. W. Toronto,

More information

Avalon Encore Stage Tenth Line Road Infusion Terrace, Block 233 City of Ottawa Environmental Noise Impact Assessment

Avalon Encore Stage Tenth Line Road Infusion Terrace, Block 233 City of Ottawa Environmental Noise Impact Assessment Avalon Encore Stage 6 2336 Tenth Line Road Infusion Terrace, Block 233 City of Ottawa Environmental Noise Impact Assessment Prepared For: Minto Communities Inc. Prepared By: Robinson Land Development Our

More information

NOISE CONTROL STUDY FOR PHOENIX HOMES 3654 & 3658 JOCKVALE ROAD APRIL 28, 2011 REV 1 TABLE OF CONTENTS 1.0 INTRODUCTION BACKGROUND...

NOISE CONTROL STUDY FOR PHOENIX HOMES 3654 & 3658 JOCKVALE ROAD APRIL 28, 2011 REV 1 TABLE OF CONTENTS 1.0 INTRODUCTION BACKGROUND... NOISE CONTROL STUDY PHOENIX HOMES 3654 & 3658 JOCKVALE ROAD APRIL 28, 2011 REV 1 NOISE CONTROL STUDY FOR PHOENIX HOMES 3654 & 3658 JOCKVALE ROAD APRIL 28, 2011 REV 1 TABLE OF CONTENTS 1.0 INTRODUCTION...

More information

DCR Phoenix. Type of Document 1st Submission. Project Name 256 Rideau Street Ottawa, Ontario. Project Number OTT A0. Prepared By: Nicole Ruyf

DCR Phoenix. Type of Document 1st Submission. Project Name 256 Rideau Street Ottawa, Ontario. Project Number OTT A0. Prepared By: Nicole Ruyf DCR Phoenix Noise Impact Assessment Study Type of Document 1st Submission Project Name 256 Rideau Street Ottawa, Ontario Project Number OTT-00206641-A0 Prepared By: Nicole Ruyf Reviewed By: Alam Ansari,

More information

Noise Control Study. Proposed Mixed-use Development. 112 Montreal Road City of Ottawa. Prepared for: DCR Phoenix Developments

Noise Control Study. Proposed Mixed-use Development. 112 Montreal Road City of Ottawa. Prepared for: DCR Phoenix Developments Noise Control Study Proposed Mixed-use Development 112 Montreal Road City of Ottawa Prepared for: DCR Phoenix Developments August 2014 10-13081-001-N01 August 28, 2014 10-13081-001-N01 Michael Boucher

More information

ENVIRONMENTAL NOISE ASSESSMENT

ENVIRONMENTAL NOISE ASSESSMENT ENVIRONMENTAL NOISE ASSESSMENT 2055 BROCK ROAD PROPOSED TOWNHOUSE DEVELOPMENT PART OF LOT 18, CONCESSION 2 CITY OF PICKERING PREPARED FOR: BROCK ROAD DUFFINS FOREST INC. Revised October 2017 December 2014

More information

ASSESSMENT OF THE TRAFFIC NOISE IMPACTS AT THE PROPOSED RESIDENTIAL DEVELOPMENT 364 ST. PATRICK STREET

ASSESSMENT OF THE TRAFFIC NOISE IMPACTS AT THE PROPOSED RESIDENTIAL DEVELOPMENT 364 ST. PATRICK STREET Ottawa, Ontario ASSESSMENT OF THE TRAFFIC NOISE IMPACTS AT THE PROPOSED RESIDENTIAL DEVELOPMENT 364 ST. PATRICK STREET CITY OF OTTAWA Prepared for Prepared by Hugh Williamson Associates Inc. 7 th May 2013

More information

3.5.1 Outdoor Living Areas (OLAs) Indoor Sound Levels... 8

3.5.1 Outdoor Living Areas (OLAs) Indoor Sound Levels... 8 RWDI was retained by Manor Park Management to conduct a traffic noise feasibility study as part of the Site Plan Approval (SPA) for the proposed development, to be located at the northwest corner of Vanier

More information

Roadway Traffic Noise Assessment Montreal Road. Ottawa, Ontario

Roadway Traffic Noise Assessment Montreal Road. Ottawa, Ontario Roadway Traffic Noise Assessment 807-825 Montreal Road Ottawa, Ontario REPORT: GWE15-086-TRAFFIC NOISE Prepared For: Anthony Nicolini 183 Michael Cowpland Drive Ottawa, Ontario K2M 0M3 Prepared By: Michael

More information

UAL URBAN AERODYNAMICS LTD

UAL URBAN AERODYNAMICS LTD UAL URBAN AERODYNAMICS LTD 23 Waterford Drive Telephone (613) 225-6362 Ottawa, Ontario, Canada Facsimile (613) 225-3022 K2E 7V4 e-mail standen.ual@sympatico.ca website: http://www.urban-noise.ca 1.0 Background

More information

Traffic Noise Assessment. 333 Montreal Road. Ottawa, Ontario

Traffic Noise Assessment. 333 Montreal Road. Ottawa, Ontario Traffic Noise Assessment 333 Montreal Road Ottawa, Ontario REPORT: GWE17-045 - Traffic Noise Prepared For: Michaela Jones The Salvation Army 2 Overlea Blvd Toronto, ON M4H 1P4 Prepared By: Joshua Foster,

More information

Fayez & Patrizia Ghadban

Fayez & Patrizia Ghadban Noise Impact Assessment Study 826 Pinecrest Road Type of Document Site Plan Submission Project Name 826 Pinecrest Road, Ottawa Project Number Prepared By: 100-2650 Queensview Drive Ottawa, ON K2B 8H6 Canada

More information

Noise Assessment Report Main Street, Residential Site Cambridge, ON

Noise Assessment Report Main Street, Residential Site Cambridge, ON Noise Assessment Report 825-875 Main Street, Residential Site Cambridge, ON Prepared for: 2536546 Ontario Inc. Prepared by: Stantec Consulting Ltd. 100-300 Hagey Boulevard Waterloo, ON N2L 0A4 Project:

More information

Noise Assessment Report

Noise Assessment Report Noise Assessment Report 19 & 23 Bachman Terrace Prepared for: Tega Homes Prepared by: Stantec Consulting Ltd. June 5, 2015 NOISE ASSESSMENT REPORT Table of Contents 1.0 INTRODUCTION... 1 1.1 PURPOSE OF

More information

Road and Rail and Vibration Noise Impact Study Valeriote Subdivision, Guelph, Ontario

Road and Rail and Vibration Noise Impact Study Valeriote Subdivision, Guelph, Ontario Road and Rail and Vibration Noise Impact Study Valeriote Subdivision, Guelph, Ontario For Attn: Nancy Shoemaker Black, Shoemaker, Robinson & Donaldson Limited 351 Speedvale Ave. West Guelph, Ontario N1H

More information

Rail Traffic Noise and Vibration Feasibility Study Proposed Zone Change for 6 Residential Lots Inkerman Street Guelph, Ontario

Rail Traffic Noise and Vibration Feasibility Study Proposed Zone Change for 6 Residential Lots Inkerman Street Guelph, Ontario Rail Traffic Noise and Vibration Feasibility Study Proposed Zone Change for 6 Residential Lots Inkerman Street Guelph, Ontario For Granite Holdings Ontario Limited 160 Southgate Drive Guelph, Ontario N1G

More information

ENVIRONMENTAL NOISE ASSESSMENT

ENVIRONMENTAL NOISE ASSESSMENT ENVIRONMENTAL NOISE ASSESSMENT PROPOSED TOWNHOUSE BLOCKS 273 LIBERTY STREET BLOCKS 197 to 199, INCLUDSIVE REGISTERED PLAN 40M-2332 AND PART OF LOT 10, CONCESSION 2 MUNICIPALITY OF CLARINGTON (BOWMANVILLE)

More information

TABLE OF CONTENTS 1.0 INTRODUCTION SITE AND AREA DESCRIPTION...1

TABLE OF CONTENTS 1.0 INTRODUCTION SITE AND AREA DESCRIPTION...1 VALCOUSTICS CANADA LTD. File: 12-286-211 Milton Heights Neighbourhood Royal Park South/Milton Noise Feasibility TABLE OF CONTENTS 1. INTRODUCTION...1 1.1 SITE AND AREA DESCRIPTION....1 2. ENVIRONMENTAL

More information

671 Victoria Road North City of Guelph Traffic Noise Study. Paradigm Transportation Solutions Limited

671 Victoria Road North City of Guelph Traffic Noise Study. Paradigm Transportation Solutions Limited 671 Victoria Road North City of Guelph Traffic Noise Study Paradigm Transportation Solutions Limited February 2016 Project Summary Project Number 152315 February 2016 Client 1830334 Ontario Limited Client

More information

ASSESSMENT OF THE TRAFFIC NOISE IMPACTS AT THE PROPOSED HOLIDAY INN DEVELOPMENT LOCATED AT 235 KING EDWARD AVENUE

ASSESSMENT OF THE TRAFFIC NOISE IMPACTS AT THE PROPOSED HOLIDAY INN DEVELOPMENT LOCATED AT 235 KING EDWARD AVENUE Ottawa, Ontario ASSESSMENT OF THE TRAFFIC NOISE IMPACTS AT THE PROPOSED HOLIDAY INN DEVELOPMENT LOCATED AT 235 KING EDWARD AVENUE CITY OF OTTAWA Prepared for Prepared by Hugh Williamson Associates Inc.

More information

ENVIRONMENTAL NOISE IMPACT ASSESSMENT THE MEADOWS IN HALF MOON BAY PHASE 5

ENVIRONMENTAL NOISE IMPACT ASSESSMENT THE MEADOWS IN HALF MOON BAY PHASE 5 REPORT PROJECT: 115496-5.2.2 ENVIRONMENTAL NOISE IMPACT ASSESSMENT THE MEADOWS IN HALF MOON BAY PHASE 5 Prepared for TAMARACK HOMES by IBI GROUP APRIL 2018 IBI GROUP ENVIRONMENTAL NOISE IMPACT ASSESSMENT

More information

Noise Feasibility Study Proposed 4 Storey Apartment Building 226 Woolwich Street South Breslau, Regional Municipality of Waterloo

Noise Feasibility Study Proposed 4 Storey Apartment Building 226 Woolwich Street South Breslau, Regional Municipality of Waterloo Noise Feasibility Study Proposed 4 Storey Apartment Building 226 Woolwich Street South Breslau, Regional Municipality of Waterloo Prepared for: RHH Rental Properties Inc. 6783 Wellington Road 34, RR22

More information

Noise Feasibility Study Proposed Mixed-Use Development 3385 Dundas Street West City of Toronto, Ontario

Noise Feasibility Study Proposed Mixed-Use Development 3385 Dundas Street West City of Toronto, Ontario Noise Feasibility Study Proposed Mixed-Use Development 8 Dundas Street West City of Toronto, Ontario Prepared for: Terra Firma Homes Corp High Park Ave, Suite Toronto, Ontario M6P S7 Prepared by Rajjot

More information

TRAFFIC NOISE IMPACT ASSESSMENT FOR THE PROPOSED MULTI-UNIT RESIDENTIAL DEVELOPMENT AT 20 MARK AVENUE

TRAFFIC NOISE IMPACT ASSESSMENT FOR THE PROPOSED MULTI-UNIT RESIDENTIAL DEVELOPMENT AT 20 MARK AVENUE Ottawa, Ontario, Canada TRAFFIC NOISE IMPACT ASSESSMENT FOR THE PROPOSED MULTI-UNIT RESIDENTIAL DEVELOPMENT AT 20 MARK AVENUE CITY OF OTTAWA Prepared for Prepared by Freefield Ltd. Issued: Postal Address:

More information

Traffic Noise Assessment Baseline Road Ottawa, Ontario

Traffic Noise Assessment Baseline Road Ottawa, Ontario Traffic Noise Assessment 2140 Baseline Road Ottawa, Ontario REPORT: GWE18-047 Traffic Noise Prepared For: Joey Theberge 905 Lady Ellen Place Ottawa, Ontario K1Z 5L5 Canada Prepared By: Omar Daher, B.Eng.,

More information

Noise Feasibility Study Proposed Stacked Townhouse Development, 3060 and 3072 Sixth Line, Town of Oakville, Ontario

Noise Feasibility Study Proposed Stacked Townhouse Development, 3060 and 3072 Sixth Line, Town of Oakville, Ontario Noise Feasibility Study Proposed Stacked Townhouse Development, 3060 and 3072 Sixth Line, Town of Oakville, Ontario Prepared for: 2457667 Ontario Inc. 3219 Yonge Street, Suite 365 Toronto, Ontario M4N

More information

Road and Rail and Vibration Noise Impact Study Valeriote Subdivision, Guelph, Ontario

Road and Rail and Vibration Noise Impact Study Valeriote Subdivision, Guelph, Ontario Road and Rail and Vibration Noise Impact Study Valeriote Subdivision, Guelph, Ontario Prepared for: Attn: Nancy Shoemaker Black, Shoemaker, Robinson & Donaldson Limited 351 Speedvale Ave. West Guelph,

More information

ENVIRONMENTAL NOISE ASSESSMENT

ENVIRONMENTAL NOISE ASSESSMENT ENVIRONMENTAL NOISE ASSESSMENT 3171 LAKESHORE ROAD WEST PROPOSED RESIDENTIAL DEVELOPMENT PART OF LOT 32, CONCESSION 4 SOUTH OF DUNDAS STREET AND BLOCK 79 REGISTERED PLAN M-257 TOWN OF OAKVILLE PREPARED

More information

ENVIRONMENTAL NOISE IMPACT ASSESSMENT MCGANN 9a LANDS BANK STREET LEITRIM DEVELOPMENT AREA

ENVIRONMENTAL NOISE IMPACT ASSESSMENT MCGANN 9a LANDS BANK STREET LEITRIM DEVELOPMENT AREA REPORT Project: 105202-5.2.2 ENVIRONMENTAL NOISE IMPACT ASSESSMENT MCGANN 9a LANDS - 4747 BANK STREET LEITRIM DEVELOPMENT AREA Prepared for Claridge Homes by IBI GROUP NOVEMBER 2017 IBI GROUP REPORT ENVIRONMENTAL

More information

DRAFT REPORT. Boyne East Catholic Secondary School #3CSS. Noise Impact Study. Louis St. Laurent Avenue, Milton. SACL #SW18060A0 December 11, 2018

DRAFT REPORT. Boyne East Catholic Secondary School #3CSS. Noise Impact Study. Louis St. Laurent Avenue, Milton. SACL #SW18060A0 December 11, 2018 DRAFT REPORT Boyne East Catholic Secondary School #3CSS Louis St. Laurent Avenue, Milton Noise Impact Study SACL #SW18060A0 Submitted to: Jeff Kenny Partner Strategy 4 Inc. 2620 Bristol Circle, Unit 100

More information

NOISE IMPACT ASSESSMENT RIVERSIDE SOUTH PHASE 13 CITY OF OTTAWA

NOISE IMPACT ASSESSMENT RIVERSIDE SOUTH PHASE 13 CITY OF OTTAWA NOISE IMPACT ASSESSMENT RIVERSIDE SOUTH PHASE 13 CITY OF OTTAWA February 2014 (Revised October 2014) (Revised December 2015) Prepared for: RIVERSIDE SOUTH DEVELOPMENT CORPORATION 2193 Arch Street Ottawa,

More information

2.0 April 18, 2017 Final - Issued to Client for Use

2.0 April 18, 2017 Final - Issued to Client for Use VALCOUSTICS CANADA LTD. File: 116-17 Villalago Residences/Bolton Environmental Noise Document Version Index: Version Date Description of Changes 2. April 18, 217 Final - Issued to Client for Use 3 Wertheim

More information

TABLE OF CONTENTS LIST OF TABLES

TABLE OF CONTENTS LIST OF TABLES TABLE OF CONTENTS INTRODUCTION... NOISE CRITERIA... Transportation Noise Sources... NOISE SOURCES... Transportation Sources... Stationary Noise Sources... PROJECTED SOUND LEVELS... VENTILATION AND WARNING

More information

ENVIRONMENTAL NOISE IMPACT ASSESSMENT 1208 OLD MONTREAL ROAD

ENVIRONMENTAL NOISE IMPACT ASSESSMENT 1208 OLD MONTREAL ROAD REPORT 109575-5.2.2.1 ENVIRONMENTAL NOISE IMPACT ASSESSMENT 1208 OLD MONTREAL ROAD CITY OF OTTAWA Prepared for DCR/PHOENIX HOMES by IBI Group February 9, 2018 IBI GROUP REPORT ENVIRONMENTAL NOISE IMPACT

More information

ENVIRONMENTAL NOISE ASSESSMENT

ENVIRONMENTAL NOISE ASSESSMENT ENVIRONMENTAL NOISE ASSESSMENT STONEPAY - PICKERING WEST OF BROCK ROAD AND SOUTH OF DERSAN STREET PART OF LOTS 19 AND 20, CONCESSION 3 PLAN 40R-28764 CITY OF PICKERING PREPARED FOR: STONEPAY 7603860 CANADA

More information

Noise Control Study. for. Avalon Public School Portobello Boulevard at Stormwind Avenue in Ottawa, Ontario. Revision 1

Noise Control Study. for. Avalon Public School Portobello Boulevard at Stormwind Avenue in Ottawa, Ontario. Revision 1 REP N45 Avalon School Traffic Noise Study - R1 Noise Control Study for Avalon Public School Portobello Boulevard at Stormwind Avenue in Ottawa, Ontario. Revision 1 Prepared for: N45 Architecture Inc. Prepared

More information

Traffic Noise Assessment. 5 Orchard Drive. Stittsville, Ontario

Traffic Noise Assessment. 5 Orchard Drive. Stittsville, Ontario Traffic Noise Assessment 5 Orchard Drive Stittsville, Ontario REPORT: GWE18-014 - Traffic Noise Prepared For: Cody Campanale 1187 Bank Street, Suite 200 Ottawa, Ontario K1S 3X7 Prepared By: Joshua Foster,

More information

The content of this supplement is based upon the that described in our letter of May 28, 2012.

The content of this supplement is based upon the that described in our letter of May 28, 2012. September 20, 2012 30 Wertheim Court, Unit 25 Richmond Hill, Ontario, Canada L4B 1B9 email solutions@valcoustics.com web www.valcoustics.com telephone 905 764-5223 fax 905 764-6813 Davis Howe Partners

More information

Noise Assessment & Control Transportation Noise Assessment 303 Lebreton Street South, 460 St. Laurent Boulevard Ottawa, Ontario Ottawa, Ontario

Noise Assessment & Control Transportation Noise Assessment 303 Lebreton Street South, 460 St. Laurent Boulevard Ottawa, Ontario Ottawa, Ontario Noise Assessment & Control Transportation Noise Assessment 303 Lebreton Street South, 460 St. Laurent Boulevard Ottawa, Ontario Ottawa, Ontario REPORT: GmE 13-051 - Traffic Noise - Final Prepared For:

More information

Policy for the Assessment and Mitigation of Traffic Noise on County Roads

Policy for the Assessment and Mitigation of Traffic Noise on County Roads Lanark County Policy for the Assessment and Mitigation of Traffic Noise on County Roads d r a f t f o r d i s c u s s i o n Prepared by: AECOM Canada Ltd. 302 1150 Morrison Drive, Ottawa, ON, Canada K2H

More information

Noise Control Feasibility Study 173 / 175 / 177 Preston Street Ottawa, Ontario

Noise Control Feasibility Study 173 / 175 / 177 Preston Street Ottawa, Ontario Noise Control Feasibility Study 173 / 175 / 177 Preston Street Ottawa, Ontario Type of Document Site Plan Application Client 1536 Prince of Wales Drive, Ottawa, Ontario K2C 1P1 Project Number Prepared

More information

Place Vanier Édifice AEFO

Place Vanier Édifice AEFO Place Vanier Édifice AEFO Martineau Architecture Inc. + Smith Carter Architects & Engineers Inc. TRAFFIC NOISE ASSESSMENT 250 Montreal Road Gradient Microclimate Engineering Inc. Prepared by Thomas Couper,

More information

Table of Contents. 174 Forward Avenue SACL Project #B7-170 Feb 22, Page ii

Table of Contents. 174 Forward Avenue SACL Project #B7-170 Feb 22, Page ii Page ii Table of Contents 1. Introduction... 1 2. Noise Assessment Criteria... 1 2.1. Surface Transportation Noise Assessment Criteria... 1 2.2. Neighbouring Stationary Source Noise Assessment Criteria...

More information

NOVATECH ENGINEERING CONSULTANTS LTD. Suite 200, 240 Michael Cowpland Drive Ottawa, Ontario K2M 1P6

NOVATECH ENGINEERING CONSULTANTS LTD. Suite 200, 240 Michael Cowpland Drive Ottawa, Ontario K2M 1P6 RESIDENTIAL / HOTEL DEVELOPMENT 141 GEORGE STREET / 325 DALHOUSIE STREET OTTAWA, ONTARIO Prepared By: NOVATECH ENGINEERING CONSULTANTS LTD. Suite 200, 240 Michael Cowpland Drive Ottawa, Ontario K2M 1P6

More information

8. Appendix F Acoustic Assessment

8. Appendix F Acoustic Assessment 8. Appendix F Acoustic Assessment HFT Ltd 06-Jun-2017 Assessment of Noise Effects Mixed Industrial Development at 28 Inlet Road, Takanini Mixed Industrial Development at 28 Inlet Road, Takanini Client:

More information

REP Fotenn Bank Phase 1 Feasibility Noise Study with Building Component AmendmentPage 1 of 21

REP Fotenn Bank Phase 1 Feasibility Noise Study with Building Component AmendmentPage 1 of 21 REP Fotenn 890-900 Bank Phase 1 Feasibility Noise Study with Building Component AmendmentPage 1 of 21 2018-02-28 Emilie Coyle, M.Pl Planner Fotenn Planning + Design 223 McLeod St, Ottawa, ON K2P 0Z8 Office:

More information

Transportation Noise & Vibration Assessment Scott Street. Ottawa, Ontario

Transportation Noise & Vibration Assessment Scott Street. Ottawa, Ontario Transportation Noise & Vibration Assessment 1946 Scott Street Ottawa, Ontario REPORT: GWE17 136 Noise & Vibration Prepared For: Michael Martin Construction Manager 88 Spadina Avenue Ottawa, ON K1Y 2C1

More information

NOISE CONTROL FEASIBILITY STUDY. MINTO COMMUNITIES INC. Clarke Lands CITY OF OTTAWA

NOISE CONTROL FEASIBILITY STUDY. MINTO COMMUNITIES INC. Clarke Lands CITY OF OTTAWA NOISE CONTROL FEASIBILITY STUDY MINTO COMMUNITIES INC. Clarke Lands CITY OF OTTAWA March 2016 Prepared for: Minto Communities Inc. 200-180 Kent Street Ottawa, Ontario K1P 0B6 Prepared by: J.L. RICHARDS

More information

NOISE IMPACT ASSESSMENT RIVERSIDE SOUTH PHASE 9-4 CITY OF OTTAWA

NOISE IMPACT ASSESSMENT RIVERSIDE SOUTH PHASE 9-4 CITY OF OTTAWA NOISE IMPACT ASSESSMENT RIVERSIDE SOUTH PHASE 9-4 CITY OF OTTAWA November 2013 Prepared for: RIVERSIDE SOUTH DEVELOPMENT CORPORATION 2193 Arch Street Ottawa, Ontario K1G 2H5 Prepared by: J.L. RICHARDS

More information

Environmental Noise Assessment Feasibility Assessment 92 Plains Road East

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

More information

MINTO COMMUNITIES INC GREENBANK ROAD NOISE CONTROL FEASIBILITY STUDY

MINTO COMMUNITIES INC GREENBANK ROAD NOISE CONTROL FEASIBILITY STUDY MINTO COMMUNITIES INC. 3311 GREENBANK ROAD NOISE CONTROL FEASIBILITY STUDY June 2017 Prepared for: MINTO COMMUNITIES INC. 180 Kent Street, Suite 200 Ottawa, Ontario K1P 0B6 Prepared by: J.L. RICHARDS &

More information

ASSESSMENT OF INWARD TRAFFIC NOISE IMPACT AT RESIDENTIAL DEVELOPMENT, WONDERFUL BARN, LEIXLIP, CO. KILDARE

ASSESSMENT OF INWARD TRAFFIC NOISE IMPACT AT RESIDENTIAL DEVELOPMENT, WONDERFUL BARN, LEIXLIP, CO. KILDARE ASSESSMENT OF INWARD TRAFFIC NOISE IMPACT AT RESIDENTIAL DEVELOPMENT, WONDERFUL BARN, LEIXLIP, CO. KILDARE Technical Report Prepared For Ardstone Capital Ltd. 48 Fitzwilliam Square Dublin Technical Report

More information

Noise Feasibility Study Framgard Apartments (South Block) NW corner of Britannia Road and Regional Road 25 Town of Milton, Ontario

Noise Feasibility Study Framgard Apartments (South Block) NW corner of Britannia Road and Regional Road 25 Town of Milton, Ontario Noise Feasibility Study Framgard Apartments (South Block) NW corner of Britannia Road and Regional Road 25 Town of Milton, Ontario Prepared for: Mattamy Homes Ltd. 433 Steeles Avenue East, Suite 110 Milton,

More information

DETAILED NOISE CONTROL STUDY OF PROPOSED PHASE 2 CONDOMINIUMS AT 655 & 755 ANAND PRIVATE OTTAWA Ontario Inc.

DETAILED NOISE CONTROL STUDY OF PROPOSED PHASE 2 CONDOMINIUMS AT 655 & 755 ANAND PRIVATE OTTAWA Ontario Inc. Ottawa, Ontario, Canada DETAILED NOISE CONTROL STUDY OF PROPOSED PHASE 2 CONDOMINIUMS AT 655 & 755 ANAND PRIVATE OTTAWA Prepared for Prepared by Hugh Williamson Associates Inc. 13 August 2015 Postal Address:

More information

Noise Feasibility Study 2480 Old Bronte Road, Oakville, Ontario

Noise Feasibility Study 2480 Old Bronte Road, Oakville, Ontario Noise Feasibility Study 2480 Old Bronte Road, Oakville, Ontario Prepared for: New Horizon Development Group (Bronte) Inc. 69 John Street South, Suite 400 Hamilton, Ontario L8N 2B9 Prepared by Sheeba Paul,

More information

From: Tyler Adams, Mei Wu Acoustics

From: Tyler Adams, Mei Wu Acoustics Experts in acoustics, noise and vibration To: Jim Inglis, Stanford University John D. Donahoe, Stanford University Doug Sams, ZGF jinglis@stanford.edu jdonahoe@stanford.edu doug.sams@zgf.com From: Tyler

More information

Stationary Noise Feasibility Assessment. 315 Chapel Street Ottawa, Ontario

Stationary Noise Feasibility Assessment. 315 Chapel Street Ottawa, Ontario Stationary Noise Feasibility Assessment 315 Chapel Street Ottawa, Ontario REPORT: GWE17-002 - Stationary Noise Prepared For: Leanne Moussa Allsaints 10 Blackburn Avenue K1N 6P8 Ottawa, Ontario Prepared

More information

Environmental Noise Assessment 80 Thomas Street Mississauga, Ontario

Environmental Noise Assessment 80 Thomas Street Mississauga, Ontario Environmental Noise Assessment 80 Thomas Street Mississauga, Ontario Novus Reference No. 16-0219 Version No. 1.0 (Final) October 21, 2016 NOVUS PROJECT TEAM: Scientist: Senior Specialist: Project Manager:

More information

A. INTRODUCTION B. NOISE ANALYSIS METHODOLOGY

A. INTRODUCTION B. NOISE ANALYSIS METHODOLOGY Chapter 8: and Vibration A. INTRODUCTION This chapter assesses the potential noise impacts resulting from operation of the proposed Wyandanch Intermodal Transit Facility by comparing existing noise levels

More information

NOISE GOALS / POLICIES / MEASURES

NOISE GOALS / POLICIES / MEASURES NOISE GOALS / POLICIES GOALS / POLICIES / MEASURES Authority The Government Code (Section 65302(f)) (GC) requires the preparation and adoption of "a Noise Element which shall identify and appraise noise

More information

NOISE GOALS / POLICIES / MEASURES

NOISE GOALS / POLICIES / MEASURES NOISE GOALS / POLICIES GOALS / POLICIES / MEASURES Authority The Government Code (Section 65302(f)) (GC) requires the preparation and adoption of "a Noise Element which shall identify and appraise noise

More information

NOISE IMPACT ASSESSMENT STUDY

NOISE IMPACT ASSESSMENT STUDY NOISE IMPACT ASSESSMENT STUDY Development Address: 765 Montreal Road Ottawa, Ontario City of Ottawa File Number: D07-12-18-0059 Client: Shepherds of Good Hope c/o: CSV Architects 402-1066 Somerset Street

More information

MOUNTAIN HOUSE SPECIFIC PLAN II

MOUNTAIN HOUSE SPECIFIC PLAN II CHAPTER ELEVEN: NOISE 11.1 INTRODUCTION 11.1 11.2 MOBILE SOURCE NOISE IMPACTS 11.1 11.2.1 Overall Mobile Noise Impacts 11.1 11.2.2 Arterial Roadways 11.3 11.2.3 Railroad 11.4 11.2.4 Byron Airport 11.4

More information

Transportation Noise & Vibration Assessment. Medical Council of Canada. Ottawa, Ontario

Transportation Noise & Vibration Assessment. Medical Council of Canada. Ottawa, Ontario Transportation Noise & Vibration Assessment Medical Council of Canada Ottawa, Ontario REPORT: GWE13-115 - Traffic Noise & Vibrations Prepared For: Derek Hardy 47 Clarence Street Ottawa, Ontario K1N 9K1

More information

NOISE IMPACT STUDY - HORIZONTAL DIRECTIONAL DRILLING FOR BLUEWATER RIVER CROSSING REPLACEMENT PROJECT

NOISE IMPACT STUDY - HORIZONTAL DIRECTIONAL DRILLING FOR BLUEWATER RIVER CROSSING REPLACEMENT PROJECT Stantec Consulting Ltd. 300-675 Cochrane Drive West Tower Markham ON L3R 0B8 Tel: (905) 944-7777 Fax: (905) 474-9889 August 9, 2012 File: 160960699 NOISE IMPACT STUDY - HORIZONTAL DIRECTIONAL DRILLING

More information

Stationary Noise Study. Stonebridge Golf and Country Club. Ottawa, Ontario

Stationary Noise Study. Stonebridge Golf and Country Club. Ottawa, Ontario Stationary Noise Study Stonebridge Golf and Country Club Ottawa, Ontario REPORT: GmE 09-042 Noise Prepared For: Kris Haynes 3584 Jockvale Road Ottawa, Ontario K2C 3H2 Prepared By: Thomas Couper, B.Eng.,

More information

SECTION 4 - NOISE INTRODUCTION

SECTION 4 - NOISE INTRODUCTION SECTION 4 - NOISE INTRODUCTION The Noise Element of the General Plan is a planning document, which is intended to provide a policy framework within which potential noise impacts may be addressed in the

More information

APPENDIX A. 2. That the road allowances included in this draft plan shall be shown and dedicated as public highways.

APPENDIX A. 2. That the road allowances included in this draft plan shall be shown and dedicated as public highways. APPENDIX A FILE NO: 04-T-2008-01 The City of Cornwall s conditions and amendments to final plan approval for registration of subdivision File No. 04-T-2008-01 are as follows: NO. CONDITIONS 1. That this

More information

Noise measurement and mitigation for urban building foundation excavation

Noise measurement and mitigation for urban building foundation excavation PROCEEDINGS of the 22 nd International Congress on Acoustics Challenges and Solutions in Acoustical Measurement and Design: Paper ICA2016-552 Noise measurement and mitigation for urban building foundation

More information