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Future Solar Developments Inc.

Acoustic Assessment Report

Type of Document Final

Project Name Acoustic Assessment Report, LP10 1572 Story Road, Midhurst, ON

Project Number WSL-00002250-A0

Prepared By:

exp 561 Bryne Drive, Unit D Barrie, ON L4N 9Y3 CANADA

Future Solar Developments Inc. Acoustic Assessment Report, LP10

1572 Story Road, Midhurst, ON WSL-00002250-00

February 2012

Acoustic Assessment Report, LP10

1572 Story Road, Midhurst, ON

Prepared for

Future Solar Developments Inc.

8-3400 Pharmacy Ave.

Scarborough, ON

M1W 3J8

Prepared By:

00

Rebecca Orth, B.Sc. Environmental Scientist

Reviewed By:

Bob Jowett, B.Sc. Team Leader, Environmental Division

Exp Services Inc. 561 Bryne Drive Barrie, ON L4N 9Y3 T: 705.734.6222 F: 705.734.6224 www.exp.com Distribution:

3 Copies – Future Solar Developments Inc., Scarborough, ON

February 2012



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Executive Summary Exp services Inc. (exp) was retained by Future Solar Developments Inc. to conduct an acoustic assessment for a proposed solar facility on the site located at 1572 Story Road in Midhurst, located in the Township of Springwater (herein referred to as the “Site”). The assessment was required for a Type 3 solar panel project under O.Reg. 359/09, Renewable Energy Approvals Under Part V.0.1 of the Act as amended by O.Reg. 521/10 and O.Reg. 231/11.

The proposed facility would comprise of a solar panel array, ground mounts for the array, twenty (20) Power One Aurora Uno 5kW inverter to convert Direct Current (DC) energy harvested by the panels to Alternating Current (AC), and one (1) transformer to step-up the power to enable feed into the Hydro One distribution system.

The proposed facility is to be located at 1572 Story Road, Midhurst in the Township of Springwater, Ontario, northeast of the intersection between Story Road, which runs east-west, and Russell Road, which runs north-south. The solar equipment is to be located west of the house located on the property (see Site plans in Appendix A).

The property consists largely of unmanicured land for recreational all-terrain vehicle use, as well as one house used as a private residence. There are neighbouring residential properties located south and east of the site. The property directly north of the site is used as a shooting range and private game retreat, which is forested except for the shooting range.

The noise assessment conducted and reported below was based on MOE guidance documentation (“Basic Comprehensive Certificates of Approval (Air) – User Guide”, MOE, 2004). The following summary presents results, conclusions, and recommendations:

Equipment to be operated at the site that has the potential to give rise to environmental noise is limited to twenty (20) inverter units and one (1) transformer. The operation of solar panels does not give rise to environmental noise.

The critical noise receptors have been identified as permanent residences. Point of Reception 1 (POR1) is located approximately 90 south of the Site, POR2 is located approximately 184 m east of the Site, POR3 is located approximately 230 m east of the Site, POR4 is located approximately 260 m southeast of the Site, POR5 is located approximately 350 m northeast of the Site, POR6 is located approximately 350 m east of the Site, POR7 is located approximately 360 m southeast of the Site, POR 8 is located approximately 420 m east of the Site, POR9 is located approximately 430 m east of the Site, POR10 is located approximately 490 m east of the Site, and POR11 is located approximately 495 m east of the Site. The reported distance is between the noise sources and the closer of the point of reception property boundary and a point 30 m from the permanent residence.

Potential noise impact from operation of the solar facility on the critical receptors was calculated and assessed versus criteria detailed in MOE NPC-232.

Solar facilities operate during daylight hours. The earliest sunrise at the Site is approximately 5:35 am and the latest sunset is approximately 9:10 pm. As such, it is appropriate to evaluate



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the project against MOE daytime (07:00 – 19:00), evening (19:00 – 23:00) and nighttime (23:00 – 07:00) hours.

Simultaneous operation of stationary sources results in a calculated maximum noise impact of 30, 23, 21, 20, 18, 18, 18, 16, 16, 15, and 15 dBA at POR1, POR2, POR3, POR4, POR5, POR6, POR7, POR8, POR9, POR10 and POR11, respectively (all residential receptors). As the calculated noise impacts are significantly lower than the applicable MOE exclusionary limits of 45 / 40 / 40 dBA for daytime / evening /nighttime periods respectively, it is concluded that the proposed facility would be in compliance with MOE noise criteria.

This executive summary is a brief summary of the report and should not be used as substitute for reading the report in its entirety.



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Table of Contents Page

Executive Summary ....................................................................................................... i

Table of Contents ......................................................................................................... iii

1 Introduction ............................................................................................................ 1

2 Facility Description ................................................................................................ 2

3 Noise Source Summary ......................................................................................... 3

3.1 Noise Sources ............................................................................................................. 3

3.2 Road Traffic ................................................................................................................. 3

3.3 Technical Information – Sources ................................................................................. 3

4 Points of Reception ................................................................................................ 7

5 Assessment Criteria (Performance Limits) .......................................................... 9

6 Impact Assessment .............................................................................................. 10

7 Impact of Known Additional Planned Solar Facilities ....................................... 11

8 Proposed Noise Control Measures ..................................................................... 11

9 Conclusions .......................................................................................................... 12

10 References ............................................................................................................ 13

11 Limitations ............................................................................................................ 14



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List of Appendices

Appendix A – Figures

Appendix B –Tables

Appendix C –Manufacturer’s Data

Appendix D –Calculations


1572 Story Road, Midhurst, ON BRM-00002250-00

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1 Introduction

Exp services Inc. (exp) was retained by Future Solar Developments Inc. to prepare an acoustic assessment report (AAR) for a proposed solar facility on the site located at 1572 Story Road, Midhurst in the Township of Springwater (herein referred to as the “Site”). The assessment was required for a Type 3 solar panel project under O.Reg. 359/09, Renewable Energy Approvals Under Part V.0.1 of the Act as amended by O.Reg. 521/10 and O.Reg. 231/11.

The proposed facility would comprise of a solar panel array, ground mounts for the array, twenty (20) Power One Aurora Uno 5kW inverters to convert Direct Current (DC) energy harvested by the panels to Alternating Current (AC), and one (1) transformer to step-up the power to enable feed into the Hydro One distribution system.

The proposed facility is to be located at 1572 Story Road, Midhurst in the Township of Springwater, Ontario. The Site is located northeast of the intersection between Story Road, which runs east-west, and Russell Road, which runs north-south. The solar equipment is to be located towards the southwest corner of the property (see Site plans in Appendix A).

The proposed project is considered a Type 3 Renewable Energy Project as it would have a maximum name plate capacity greater than 12 kW. The electricity produced by the solar facility is intended to be fed into a local Hydro One distribution line. Equipment to be installed at the facility complies with the Ontario manufactured percentages as required by the Ontario Power Authority’s Feed-in-Tariff Program.

This report assesses noise arising from identified sources, details the anticipated impact on the nearest receptors, and evaluates the calculated impact versus MOE criteria.

In accordance with legislative requirements, a copy of this report is to be made available to interested parties including the public and the local municipality at least 60 days prior to the final public consultation meeting.



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2 Facility Description

The proposed facility consists of a ground-mounted solar array that will produce electricity from the sun’s energy. The direct current generated by the solar array will be converted into alternating current and transformed to enable power to be fed into the Hydro One Network.

The proposed solar array will be attached to mounts on concrete blocks installed in the ground and will occupy an area of approximately 65 by 66 metres. As such the facility represents a fixed system and therefore the array will not produce any noise (c.f. sun tracking arrays). The associated inverter and transformer will be located to the south side of the solar array.

The surrounding land use to the north, east, west, and south is Agricultural (A). A few areas of Environmental Protection (EP) are located northeast and east of the Site. Several zoning maps have been included in Appendix A, as well as Site Plan Aerial maps which show details of the surrounding properties. Zoning maps have been included in Appendix A, as well as Site Plan Aerial maps which show details of the surrounding properties. Given the existing land use and land use in the surrounding area, the project is considered to be in a rural environment. Whilst background sound measurements have not been taken in support of this assessment, the acoustical environment is expected to be dominated by natural sounds. The closest road is Story road, which is approximately 65 m from LP10. The next closest roads are Old 2 S which is 400 m away from LP10, and Russel road which is a distance of 660 m away from LP10. All three roads are unpaved; it can therefore be concluded that vehicles travelling on these roads are limited to local traffic (the roads aren’t used as major throughways) and traffic travels slower (50 km/hr) so as to not kick up gravel.

Solar facilities operate during daylight hours, the earliest sunrise at the Site is approximately 5:35 am and the latest sunset is approximately 9:10 pm. As such, it is appropriate to evaluate the project against MOE daytime (07:00 – 19:00), evening (19:00 – 23:00) and night time (23:00 – 07:00) hours.



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3 Noise Source Summary

The locations of all noise sources can be found in the Site Location Aerial Maps (Appendix A).

3.1 Noise Sources

The following noise sources were identified:

Twenty (20) Power One Aurora Uno 5 kW inverter located south of the farm buildings; and,

One (1) oil-filled step-up transformer (make and model to be confirmed) located adjacent to the inverter.

The proposed solar array is a fixed system and therefore does not include motors etc. as required with tracking systems.

3.2 Road Traffic

Other than construction traffic, the proposed renewable energy project will result in minimal increase in on-site road traffic associated with servicing / maintenance visits as required. As such visits will be infrequent, road traffic noise associated with the proposed project is considered negligible.

3.3 Technical Information – Sources

Table 1 summarizes the specifications and locations of each significant stationary noise source of the proposed renewable solar energy project:

Table 3.1. Technical Information and Locations of Noise Source

ID Description Location Make Model # Rating

I01 Inverter South of solar panels, 1572 Story Road, Midhurst, ON. Detailed location indicated on map in Appendix A.

Power One

Aurora Uno PVI-5000-OUTD-US

5 kW

I02 Inverter Inverters are grouped in one location; I02 is located adjacent to I01.

Power One


5 kW


Power One


5 kW



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Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW



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Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW


Power One


5 kW

T01 Transformer Adjacent to inverter To Be Confirmed

To Be Confirmed

To Be Confirmed

The planned locations of significant noise sources are provided in Appendix A and approximate co-ordinates are provided in Table 5, Appendix B.



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4 Points of Reception

Points of Reception for the approval of new sources, including verifying compliance with the Environmental Protection Act, are defined in Publication NPC-2051 as premises in use, or zoned for future use, as:

Permanent or seasonal residences;

Hotels/motels

Nursing/retirement homes;

Rental residences;

Hospitals;

Camp grounds; and,

Noise sensitive buildings such as schools and places of worship.

The closest points of reception are permanent residences located between 92 and 479 m east/northeast of the Site. Other receptors are located >500 m from the proposed project location. Below is a description of each point of reception. As per MOE noise guidelines for a Class 3 area, the points of reception have been taken as a point within 30 m of a dwelling or a camping area.

Table 3, Appendix B lists the PORs, the distance of the PORs from the Site, and position in relation to the Site.

Table 4.1. Details of Points of Reception

POR Identification

Distance from Noise Source Direction from Noise Source to POR

POR1 92 Southeast

POR2 204 East

POR3 252 East

POR4 259 East

POR5 348 Northeast

POR6 340 East

POR7 370 East

POR8 433 East



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POR Identification

Distance from Noise Source Direction from Noise Source to POR

POR9 444 East

POR10 456 East

POR11 479 East



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5 Assessment Criteria (Performance Limits)

The subject property is located in the Township of Springwater, a rural area (Class 3 Area). Criteria for assessing the impact of noise from stationary sources are provided in the MOE Publication NPC-232 (Sound Level Limits for Stationary Sources in Class 3 Areas (Rural), October 1995, Ministry of the Environment):

NPC-232 Table 232-1: Minimum Values of One Hour Leq or Llm by Time of Day

One Hour Leq (dBA) or LLM (dBAI)

Time of Day Class 3 Area

07:00 – 19:00 45

19:00 – 23:00 40

23:00 – 07:00 40

Dependent on day of the year, the facility may generate electricity between 5:35 and 21:10. All PORs are located in a Class 3 area where background noise is anticipated to be dominated by natural sounds. Therefore, the appropriate limits for total equipment operation are the MOE exclusionary limits of 45 dBA / 40 dBA (Class 3 Area, 07:00 – 19:00 (daytime operation) / 19:00 – 7:00 (evening and nighttime operation)).



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6 Impact Assessment

Noise produced by the inverters was assessed by using the sound rating given in the manufacturer’s specifications for the unit. The manufacturer’s specifications for the inverters is provided in Appendix C.

In the absence of a selected make and model number, noise produced by the transformer was assessed based on data published in Table 0.3 of NEMA Standards Publication No. TR 1-1993 (R2000). The transformer size was conservatively assumed to be in the range 101 – 300 kVA (expected size is 100 kVA).

As the noise producing stationary sources at the facility are limited to twenty-one (21) pieces of equipment, with twenty sources grouped together, a simple assessment considering only attenuation due to geometric divergence using procedures detailed in ISO 9613 Part 2 has been conducted. This method of assessment is expected to produce a conservative estimate of noise impact as no consideration is given to attenuation through ground absorption, atmospheric absorption or barrier affects.

The predicted sound levels at the selected PORs due to operation of each noise source are summarized in Table 3 (Appendix B). Distances between each source and POR are also provided in this table.

Sample calculations are provided in Appendix D and an Acoustic Assessment Summary Table is provided as Table 4 in Appendix B.

Consideration of additional solar facilities known to be planned on the property at 1572 Story Road is provided in Section 7.



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7 Impact of Known Additional Planned Solar Facilities

Exp has been requested to conduct a noise assessment of an additional proposed solar facility, Project LP9, that will be located on the property at 1572 Story Road in Midhurst. LP9 would be located approximately 500 m away from LP10, and further than 500 m away from PORs 1 through 11. It can therefore be concluded that the noise generated by the operation of LP 9 will have little effect on PORs 1 through 11.

8 Proposed Noise Control Measures

Noise control measures are not necessary for this renewable energy project since the noise resulting from the operation of the solar panels results in a noise level below the MOE exclusionary limits for daytime, evening and nighttime operation.



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9 Conclusions

It is concluded that operation of stationary sources at the Site located at 1572 Story Road, Midhurst, in the Township of Springwater, Ontario, would result in noise levels at critical points of reception that are below MOE exclusionary limits for a Class 3 Area.

It is further concluded that, with respect to noise impact, operation of the proposed site would be compatible with existing land use planning guidance.

Simultaneous operation of the facility with the additional planned solar facility for 1572 Story Road, Midhurst, Ontario would result in noise levels at critical points of reception that are below MOE exclusionary limits for a Class 3 Area.



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10 References

1. International Organization for Standardization, ISO 9613-2: Acoustics – Attenuation of Sound During Propagation Outdoors Part 2: General Method of Calculation, Geneva, Switzerland, 1996.

2. Ontario Ministry of the Environment, Publication NPC-232: Sound Level Limits for Stationary Sources in Class 3 Areas (Rural), October 1995.

3. Ontario Ministry of the Environment, Publication NPC-233: Information to be Submitted for Approval of Stationary Sources of Sound, October 1995.

4. Ontario Ministry of the Environment, Model Municipal Noise Control by-Law Publication NPC-103, August 1978.

5. Ontario Ministry of the Environment, Model Municipal Noise Control By-Law Publication NPC-104, August 1978.

6. Ontario Ministry of the Environment, Environmental Assessment and Approvals Branch, Basic Comprehensive Certificates of Approval (Air) User Guide Version 2.0, April 2004.



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11 Limitations

The objective of this report was to assess noise impact from operation of equipment and processes within the context of our contract with respect to existing Regulations and Guidelines within the applicable jurisdiction. Compliance of past and current owners with applicable local, provincial and federal government laws and regulations was not included in our contract for services.

The conclusions of this report are based, in part, on the information provided by others and any testing and analyses described in the report. The possibility remains that unexpected environmental conditions may be encountered. Should such an event occur, exp should be notified in order that we may determine if modifications to our conclusions are necessary.

This report has been prepared for the exclusive use of Future Solar Developments Inc. in accordance with accepted environmental study and/or engineering practices for a Noise Study. No other warranties, either expressed or implied, are made as to the professional services provided under the terms of the Survey and included in this report. Any use which a third party makes of this report, or any part hereof, or any reliance on or decisions to be made based on it, are the responsibility of such third parties. Exp Services Inc. accepts no responsibility for damages, if any, suffered by any third party as a result of decisions made or actions based on this report.

Appendix A – Figures

LP9

LP10

POR1

POR2 POR3

1572 Story Rd

POR5

POR4

POR6

POR7

POR8POR9

POR10

POR11

Shooting Range

N

Locations of transformers and inverters

Source UTM CoordinatesID Easting NorthingInverters (approx.) 601283 4926621Transformer 601283 4926621

Acoustic Assessment, LP10Future Solar Developments Inc. 8‐3400 Pharmacy Ave. Scarborough, Ontario M1W 3J8

Drawing Title: Site Plan Closest Receptors LP10Prepared By: Rebecca Orth Date: January 2012 Project No.: WSL‐00002250‐00

Exp Services Inc. 561 Bryne Drive, Barrie, Ontario L4N 9Y3 (705) 734‐6222

POR UTM CoordinatesID Easting NorthingPOR1 601369 4926611POR2 601436 4926726POR3 601477 4926745POR4 601536 4926693POR5 601510 4926890POR6 601614 4926729POR7 601642 4926670POR8 601673 4926767POR9 601696 4926750POR10 601763 4926721POR11 601775 4926682

UTM coordinates correspond to points 30 metres away from the residential receptor, as defined in NPC‐232

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R(H)

I

A

A

A

EP

A

ME

MO

EP

EP

AC

A

EP

EP

OS

EP

EP

OS

EP

RE-11

R(H)

A

EP

A

EP

A

A

A

AC

A

ME

I

AC

AC

A

A-17

RR

A

RE

EP

A

A

A

AC

CH

EP

EP

WD-1

AC

A

EP

A-40

I

I

A-1

EP

I

A

A

EP

CC

A

EP

EP

WD-1

EP

AC

I

ME

I

A

ME-1

EP

A

EP

R1

EP

R1(H)

A

WD-1

A

EP

ME-1

A

EP

A

A

A

AC-1

ME

EP

R1

ME-9

ME

A

A

A

EP

A

A

A

EP

A

A

R1

EP

I

EP

OS-8

A

RE

R1

A

OS

A

I

A

EP

A

ME-1

A

I

WD

A

ME

EP

A

A

OS

A

A

A

A

A-22

WD-1

EP

ME-14

A(H)

EP

M(H)

EP

EP

EP

OS

R(H)

A-34

EP

I

OS

A

EP

R1

EP

RE

EP

OSCCOS

EP

A-20

A

A

EP

EP-20

EP

A

OS

EP

EP

R1

ME-7

A

A

EP

R1

R1

A-12

A

A-19

A

OS

A

OS-4

A

EP

EP

EP

A

A

A

I

EP

R1

A

EP

EP-20

A

A

WD-1

R1

A

A

A

A

OS

A

EP

A

R1

A

EP

I

OS

A

MI

AC-1

RR

A

MI

A

A

EP

EP

EP

A

R1

K

A

A

ME

A-11

A-9

R1

R1

CR

A

AC

I

A

A

OS

OS

A

RR

A

ME-10

CC

AC

A

ME

R(H)

RE

A

EP

RR

CC-1

A

A

RE

EP

OS

A

R(H)

EP

EP

A

A

WD

A-7

A

RE

M(H)

A

EP

A

R1

A

CC-6

EP

RE-1

EP-7

CH

I

AC

A-31

R1

A

ME

EP

ME-5

A

R1

EP-6

EP

WD

WD-1

A

RE

I

EP

OS

MO

A

R1

A

OS-4

EP-10

A

R1

A

RE

R1

CC

EP

A

WD-1

R1

R1

EP

A-2

A

A

R(H) R1

RR

EP

R1

A

A

A

RREP

MI

R1

EP-20

EP

A

A

I

R1

A

EP

R1

EP

A

I

A-32OS

A

EP

EP

A-37

EP

CH-6

A

A

EP

OS

I

A

R1

EP-19

EP

A

CR-1

A

RE

A

R1

EP

EP

RR-1

R1

EP

A

R1

CC

A

A

I

I-3

R(H)

MI-2

A

A

CT(H)

A

A

I-1

A

R1

AC

ME-15

RS

WD-1

RE

EP

EP

RE

A

A

MO

ME-9

R(H)

EP-4

A

MO-8

RE

RE

A

I

AC-1

A

I-4

A

A

MO-6

A

CH-24

R1

R1

A

A

A

OS

A

OS-5

R1

R1

CH

R1-38

CR

REMO

R1

A-16

A

R1

OS-3

A

RE-17

A

RE

A

RR

R1

OS

A

R1

A

R1

A

A

MO

R1

R(H)

A-36

R1

A

CC-2

RR

A

A

A

R1

EP

A

R1

RE-17

A

R1-2

R1

R1

A

A

R2

R1

A

A

R1

R1

A

CPM

RC(H)

MO

R1-21

A

R1

A

R1

A-29

MO-9

R1

ARR

R1

CH

OS

EP

EP

ME-11

A

EP

EP

CT

CT

R1

EP

CT

A

EP

EP

EP

EP

EP

EP

A

R1

EP

EP

EP

R1

EP

OS

A

A

RE

EP

A

EP

CT

R1

EP

EP

EP

A

R1

R1-35(H)

A

I

EP

R1

R1EP

RR

R1

RR

I

ME-13

R(H)

EP

R1

R1

I

R1

EP

R1

EP

A

OSEP

EP

R1

EP

EP

EP

A

A

I

R1

A

RE-15

EP

RR

R1-38

RE

R1

EP

EP

R1

A

A

R1

RE

EP

EP

I

EP

R1

RR

WD

EP

CC-5

A

R1

OS

CG

RE

OS

R1

RE

I

R1

I

OS

EP

EP

I

EP

A

EP

A

EP

A

A-6

R1

EP

CT

R1

R1

A

R1

RE-14

R1

A

R1

R1

EP

RR

R1

I

OS

A

I

A

OS

EP

EP

RE

CT

R1

ME-4

R1

R1

R1

RR

R1R1

A

CT

AC

MO

A

RR

EP

A

I

CC

OS

RR

OS

R1

EP

OS

EP

A

EP-16

I

I

R1

R1

RR

EP

R1-2

R1-5

A-38

EP

OS

R1

A

R1

R1

RS

RE

R1

RE-15

RE

EP-3

A

A

WD-1

RS

EP

EP

R1

EP

EP-20

EP

I

RE-1

I

EP

EP

I

R1

A-2

EP

A

R1

A

EP

I

EP

R1

EP

R1

A

A

OS

RE-10

RR

R1-2

RE-7

RE

A

EP

A

OS

R1

RR

R1

RE-12

R1

A

OS

R1

A

CT

EP

A

CT

R(H)

EP

A

I

RR

EP

RS

A

CH-2

RER2

R1

EP-12

A

A

EP

A

A

EP

A

RR

R1

R1

A

R1

A

A

A

CG

R1

A

CR-2

I

A

OS

EP

RE-4

A

EP

R1

CT-4

RE-2

A

EP

I

EP

R1

I

RC(H)

CC

R1-2

OS

A

R1

EP-15

R1

A

OS

R1-10

EP-9OS

R1

A

CH-25

R1

A

EP

CT

CC-3

I

R1-12

R1

EP

A

A

EP

R1

EP

MI-1

A-10

EP

R1

A

RC(H)

R1-13

R1

R1

EP

EP

OS

RE-17

OS

R1

I

R1

I

R1

RE-15

A

A

A-28

A

A

WD-1

A

A

RE-6

RE-1

EP

EP

OS

R1

RE

RE

EPA

OS

R1

EP

WD-1

EP-18

R1

A

R1

A

R1

OS

RR

R1

R1-11

A

MO-2

OS

EP

A

RR(H)

A

R1

R1-34

A

OS

MO

CC-4

R1OS

R1

A

OS

A

A

I

R1

OS

A

R1

R1-2

A-15

I

EP

I

CG-9

CC-5

I

EP

RC(H)

R1

A

A-5

RE

MO-7

RE-4

RR-2

R1

A

A

A

R1

A

RE-17

CH-9

MI RC(H)

R1-23

RC

A

CH

EP

R1-2

R1-10

OS

R1-21

RR

CG

EP

A

A

A

R3

R1-21

MI-4

A

R1

A

R1

RC(H)

R1

OS

R(H)

CH-7

R1

RC(H)

A

R1-13

RR

WD-1

A

EP

A

A

R1

CT

A

A-35

RC

MI-7

EP

R1

CG

RC

EP

MO

R1

R1

EP

OS

CH-4

WD

R1-34

RC

R1

I

RS

CG

RR

R1

RS

A

R1

RC(H)

R1-21

EP

R1(H)

CH

R1-2

EP

I

R1

A

MO-1

EP

RE-10

R1

R(H)

R1-33

I

RC

CH

R1

EP

A

R2

R1

OS

R1

I

A

R1

RC(H)

CH-19

R1(H)

R1

EP

RC

A

I

A-30

EP

R1

R1-10

A-13

R1 OS

A

A

CC(H)

EP

R1

R1-13

RC

A

RE-18

A

RE-15

MI-4

A

A

EP

CT-3

EP-17

MO

R1-21

A

A

EP

R1

EP

CH

EPA

A

A

A-14

R1

RE-3

EP

I

A

A

A

A

RC(H)

RC

CH

CG

OSR1

R1

R1

A

EP

A

CH

CG

R1

OS

A

RC

R2

A

R2

RC

R1

R1

MI

R1

EP-17

RR

R1-21

MO-3

I

OS

EP-20

A

RC

OS

R1-21

RE-5

R1

R1

EP

R1

EP

EP

CH

OS

R1-13

CG

RR

R1-1

CH-3

EP

R1

CT-1

CH

R1-34

OS

R1

R1-26

RE-17

R2

I-2

R1-34

A

CG

EP

MO

RE

CR

MI-2

I

CG-7

CH

EP

RE-18

RE-13

CG

EP

R1(H)

A-25

A

R1

EP

R1A

EP

CH

R1

RC(H)

RS

R1-10

MO-10

A-23

RC

R1

EP

I

RC(H)

CG-2

A

R1-17

R2R1

R1

R1

CH-26

R1

EP

R1

R1

A

EP

CG

ME-3

R1

OS

RC(H)

EP

R1

EP

ME-3

EP

I

R2

CH-15

R1-26

CG-21(H)

OS

AC

I

RC

RC

R1

ME-12

R3(H)

MO-4

CH

I

RC(H)

RC

EP

EP

R1

CG

I

RC(H)R1

RC(H)

R1

R1

RR-3

OS

OS

A

R(H)

I

RC

A

A

MI-3

A

R2

RC

R1

R1

RC(H)

I

EP

I

EP

CT-2

R1(H)

EP

R1

CH

CT-5

R1-2

MO

MO

A

CH

OS

RC(H)

R1

EP

RC

R1-26

OS

ME-6(H)

R1-2

RE

R1-31

MO-1

RC(H)

R1

R1

MO-1

A

A

CH-23

MO-1

CH

R1

CH-11

CH

RR

CC

CR

CG-3

RC

RR

R1-26

R2

CH

CG

EP

CH

OS

CH

RC

I

CH

CG

RC(H)

I

EP

OS

CG-4

R1

EP

CH

A

RE-18

R1-4

R1-23

MI-5

R1-19

R1-34

A

RE-9

R1(H)

CH

CH(H)

EP

EP

EP

R3-6(H)

R2(H)

RC

CG

EP

CH

A

A-26

A-3

CG-27(H)

R3-3

CG-11

A

CG

CH

EP

RE

CH-16

A

A-24

RC

CG

RC

CT-4

AC

R1

A-4

A

RC

CH-12

CH-10

A

CG

RCR1(H)

R2(H)

RC

CH

RC(H)

RR

A

R1

CG

MI

RE

CH

CG

R1

EP-17

A

OS

R2

RR

RC(H)

CH(H)

EP

I

R1

A

OS

EP

RC(H)

CH-5

WD-1

RC(H)

A-27

RE-8

RC(H)

EP

EP-17

CG

CG-8

EP

RC

A

EP-17

RC(H)

R1-13

CH-18

R1

RC

A

R2

RC-3

CG

A

RC(H)

MO-1

RC

CG

R1

EP

RR

R2

CG-14

RC

OS-6

CH

A

CH

CG

R2

MI(H)

CG

EP R1-26

EP

EP-21

CH

EP-11

CH

RR-4

OS

R1-6

R1

RC(H)

MO-12(H)

RC-5

RC-13

EP

R1-22

RC(H)

EP

A

CG

EP

RR(H)

RC

RC-5

CG

A

I

R1-30

R1-8

EP-20

EP

RC(H)

CH-1

EP

RC(H)

MI-2(H)

CT

RC(H)

R1-3

EP-20

WD-1

A

A

A

OS

RC(H)

R1-39

CG-6

EP

EP

R1-37

EP

EP-17

CG

RC(H)

RS

EP-17

A

R1-6

A

EP

RC-5

OS

A

RC-5

EP

RC(H)

R1

RC(H)

R1-28

EP

OS

EP

A

EP

EP

OS

A

A

EP

EPA

EP

EP

HIGHWAY 26

HIG

HW

AY

40

0 S

WIL

SO

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OA

D

OL

D S

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ON

D S

FLOS ROAD SIX W

GIL

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OA

D

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HW

AY

400 N

COUNTY ROAD 90

SUNNIDALE ROAD

OL

D S

EC

ON

D N

FLOS ROAD EIGHT W

FLOS ROAD TEN W

SC

AR

LE

TT

LIN

E

FLOS ROAD SEVEN W

PE

NE

TA

NG

UIS

HE

NE

RO

AD

COUNTY ROAD 92

FLOS ROAD FOUR W

FLOS ROAD TEN E

GE

OR

GE

JO

HN

ST

ON

RO

AD

US

HE

RS

RO

AD

NU

RS

ER

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OA

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HORSESHOE VALLEY ROAD W

FLOS ROAD ELEVEN W

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LL

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AT

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RO

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SOUTH ORR LAKE ROAD

FORBES ROAD

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SNOW VALLEY ROAD

CR

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AN

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CARSON ROAD

MILL STREET W

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D

TOWNSHIP OF SPRINGWATER

DETAILED ZONING SCHEDULE 'A'

0 2 4 6 81Kilometers

Text

Revised October 27, 2005.

R1 R2 R3 RE RR RS RC CG CH CR CT CC CPM CA K MI MO ME WD I OS EP A AC

Residential Rural Residential Seasonal

ResidentialResidentialResidentialResidential Estate

Environmental Protection Agricultural Agricultural Consolidation

General Industrial/Outside StorageExtractive Industrial Waste DisposalInstitutional

General CommercialHighway CommercialRural Commercial

Open Space

General Industrial/Inside StorageKennel

ZONE LEGEND

Tourist & Recreational Commercial Campground CommercialPark Model Trailer CommercialAdult Entertainment Commercial

Residential Conversion

This is Schedule 'A' to By-law 5000-038 passed the 21st day of November, 2005

The Corporation of the Township of Springwater

_______________________ ______________________ Deputy Mayor Tony Guergis Clerk Eleanor J. Rath

A = Agricultural A‐9 = Agricultural EP = Environmental Protection = location of LP10 = location of LP9

LP9

Acoustic Assessment, LP10Future Solar Developments Inc. 8‐3400 Pharmacy Ave. Scarborough, Ontario M1W 3J8

Drawing Title: Zoning Map LP10 Prepared By: Rebecca Orth Date: January 2012 Project No.: WSL‐0002250‐00

Exp Services Inc. 561 Bryne Drive, Barrie, Ontario L4N 9Y3 (705) 734‐6222

STO

RY

RO

AD

TYPICAL CANADIAN SOLAR

CS6P-230 BLOCK

TYPICAL CANADIAN SOLAR

CS6P-230 BLOCK

f:\2250 - future solar\prelim eng\2250 - lp9 lp10.dwg

11/16/2011 11:03:14 AM----

11/15/2011 4:01:28 PM

Pen Table::Last Plotted:Last Saved:Filename:

Plotted by: HollingworthK

References: 2250 - Barrie Base.dwg

Canada

ww

w.exp.com

BU

ILDIN

GS

EA

RTH

& E

NV

IRO

NM

EN

T EN

ER

GY

IND

US

TRIA

L INFR

AS

TRU

CTU

RE

SU

STA

INA

BILITY

exp Services Inc.

The new identity of Trow

Associates

t: +1.905.573.6400 | f: +1.905.573.756580 B

ancroft Street

Ham

ilton, ON

L8E 2W

5

Appendix B –Tables

Table 1: Noise Summary Table

Source Sound Power Level (dBA)

Location Sound Characteristics

Existing Noise Control Measures

Power One Aurora Uno 5kW Inverter

66.0a O S, T U

Transformer (liquid filled) 71.0a O S, T U

a A 5 dB penalty has been applied to these sources as required by the MOE publication NPC 104, and included in the Sound Power Level provided in this table.

Location Sound Characteristics Existing Noise Control Measures

O – Outside building S – Steady S – Silencer I – Inside building QSI – quasi-steady impulsive A – Acoustic Lining I – Impulsive B – Barrier B – Buzzing L - Lagging T – Tonal E – Enclosure C – Cyclic O – Other U – Uncontrolled

Table 2: Performance Limits Summary Table

Point of Reception ID MOE Designation Performance Limit (dBA)

Day-time Evening / Night-time

POR1 Class 3 45 40

POR2 Class 3 45 40

POR3 Class 3 45 40

POR4 Class 3 45 40

POR5 Class 3 45 40

POR6 Class 3 45 40

POR7 Class 3 45 40

POR8 Class 3 45 40

POR9 Class 3 45 40

POR10 Class 3 45 40

Point of Reception ID MOE Designation Performance Limit (dBA)

Day-time Evening / Night-time

POR11 Class 3 45 40

POR1 Class 3 45 40

Table 3: Point of Reception Noise Impact Table

Source ID

POR1 POR2 POR3 POR4 POR5 POR6 POR7 POR8 POR9 POR10 POR11

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

Distance (m)

Sound Level (dBA)

D E/N D E/N D E/N D E/N D E/N D E/N D E/N D E/N D E/N D E/N D E/N

I01 86 16 16 184 10 10 230 8 8 263 7 7 351 4 4 348 4 4 362 4 4 416 3 3 432 2 2 490 1 1 496 1 1

I02 85 16 16 184 10 10 229 8 8 262 7 7 351 4 4 347 4 4 361 4 4 415 3 3 431 2 2 489 1 1 495 1 1

I03 84 17 17 183 10 10 228 8 8 261 7 7 350 4 4 346 4 4 360 4 4 414 3 3 430 2 2 488 1 1 494 1 1

I04 83 17 17 182 10 10 227 8 8 260 7 7 349 4 4 345 4 4 359 4 4 413 3 3 429 2 2 487 1 1 493 1 1

I05 82 17 17 181 10 10 227 8 8 259 7 7 349 4 4 344 4 4 358 4 4 412 3 3 428 2 2 486 1 1 492 1 1

I06 86 16 16 185 10 10 230 8 8 263 7 7 352 4 4 348 4 4 362 4 4 416 3 3 433 2 2 490 1 1 496 1 1

I07 85 16 16 184 10 10 230 8 8 262 7 7 351 4 4 347 4 4 361 4 4 415 3 3 432 2 2 489 1 1 495 1 1

I08 84 17 17 183 10 10 229 8 8 261 7 7 351 4 4 346 4 4 360 4 4 414 3 3 431 2 2 488 1 1 494 1 1

I09 83 17 17 183 10 10 228 8 8 260 7 7 350 4 4 345 4 4 359 4 4 413 3 3 430 2 2 487 1 1 493 1 1

I10 82 17 17 182 10 10 227 8 8 259 7 7 350 4 4 344 4 4 358 4 4 412 3 3 429 2 2 486 1 1 492 1 1

I11 86 16 16 186 10 10 231 8 8 263 7 7 353 4 4 348 4 4 362 4 4 416 3 3 433 2 2 491 1 1 496 1 1

I12 85 16 16 185 10 10 230 8 8 262 7 7 352 4 4 347 4 4 361 4 4 415 3 3 432 2 2 490 1 1 495 1 1

I13 84 17 17 184 10 10 229 8 8 261 7 7 352 4 4 346 4 4 360 4 4 415 3 3 431 2 2 489 1 1 494 1 1

I14 83 17 17 183 10 10 228 8 8 260 7 7 351 4 4 345 4 4 359 4 4 414 3 3 430 2 2 488 1 1 493 1 1

I15 82 17 17 182 10 10 228 8 8 259 7 7 350 4 4 344 4 4 358 4 4 413 3 3 429 2 2 487 1 1 492 1 1

I16 86 16 16 186 10 10 231 8 8 263 7 7 354 4 4 349 4 4 362 4 4 417 3 3 433 2 2 491 1 1 496 1 1

I17 85 16 16 185 10 10 231 8 8 262 7 7 353 4 4 348 4 4 361 4 4 416 3 3 432 2 2 490 1 1 495 1 1

I18 84 17 17 185 10 10 230 8 8 262 7 7 352 4 4 347 4 4 360 4 4 415 3 3 431 2 2 489 1 1 494 1 1

I19 83 17 17 184 10 10 229 8 8 261 7 7 352 4 4 346 4 4 359 4 4 414 3 3 430 2 2 488 1 1 493 1 1

I20 82 17 17 183 10 10 228 8 8 260 7 7 351 4 4 345 4 4 358 4 4 413 3 3 429 2 2 487 1 1 492 1 1

T01 86 21 21 184 15 15 230 13 13 263 12 12 351 9 9 348 9 9 362 9 9 416 8 8 432 7 7 490 6 6 496 6 6

Table 4: Acoustic Assessment Summary Table

POR ID

POR Description

Time of Day

Sound Level at

POR (dBA)

Verified by Acoustic Audit?

(Yes/No)

Performance Limit (dBA)

Leq

Compliance with

Performance Limit

(Yes/No)

POR1 Permanent residence

Day 30 No 45 Yes

Evening/ night

30 No 40 Yes


Day 23 No 45 Yes

Evening/ night

23 No 40 Yes


Day 21 No 45 Yes

Evening/ night

21 No 40 Yes


Day 20 No 45 Yes

Evening/ night

20 No 40 Yes


Day 18 No 45 Yes

Evening/ night

18 No 40 Yes


Day 18 No 45 Yes

Evening/ night

18 No 40 Yes


Day 18 No 45 Yes

Evening/ night

18 No 40 Yes


Day 16 No 45 Yes

Evening/ night

16 No 40 Yes


Day 16 No 45 Yes

Evening/ night

16 No 40 Yes


Day 15 No 45 Yes

Evening/ night

15 No 40 Yes

POR11 Permanent Day 15 No 45 Yes

POR ID

POR Description

Time of Day

Sound Level at

POR (dBA)

Verified by Acoustic Audit?

(Yes/No)

Performance Limit (dBA)

Leq

Compliance with

Performance Limit

(Yes/No)

residence Evening/ night

15 No 40 Yes

Table 5. Coordinates of Noise Sources and Points of Reception

ID ETM Coordinates

Easting Northing

Inverters

I01 601283 4926621

I02 601284 4926621

I03 601285 4926621

I04 601286 4926621

I05 601287 4926621

I06 601283 4926620

I07 601284 4926620

I08 601285 4926620

I09 601286 4926620

I10 601287 4926620

I11 601283 4926619

I12 601284 4926619

I13 601285 4926619

I14 601286 4926619

I15 601287 4926619

I16 601283 4926618

ID ETM Coordinates

Easting Northing

I17 601284 4926618

I18 601285 4926618

I19 601286 4926618

I20 601287 4926618

Transformer

T01 601283 4926621

Points of Reception

POR1 601369 4926611

POR2 601436 4926726

POR3 601477 4926745

POR4 601536 4926693

POR5 601510 4926890

POR6 601614 4926729

POR7 601642 4926670

POR8 601673 4926767

POR9 601696 4926750

POR10 601763 4926721

POR11 601775 4926682

Appendix C –Manufacturer’s Data

Features

1AURORA UNO

UNOPVI-5000-OUTD-US

PVI-6000-OUTD-US

GENERAL SPECIFICATIONSOUTDOOR MODELS

Designed for residential and small commercial PV installations, this inverter fills a specific niche in the Aurora product line to cater for those installations producing between 5kW and 20kW.

This inverter has all the usual Aurora benefits, including dual input section to process two strings with independent MPPT, high speed and precise MPPT algorithm for real-time power tracking and energy harvesting, as well as transformerless operation for high performance efficiencies of up to 97.1%.

The wide input voltage range makes the inverter suitable to low power installations with reduced string size. This outdo-or inverter has been designed as a completely sealed unit to withstand the harshest environmental conditions.

Each inverter is set on specific grid codes which can be selected in the fieldSingle phase outputDual input sections with independent MPP tracking, allows optimal energy harvesting from two sub-arrays oriented in diff erent directionsWide input rangeHigh speed and precise MPPT algorithm for real time power tracking and improved energy harvestingFlat efficiency curves ensure high efficiency at all output levels ensuring consistent and stable performance across the entire input voltage and output power rangeOutdoor enclosure for unrestricted use under any environmental conditionsRS-485 communication interface (for connection to laptop or datalogger)Compatible with PVI-RADIOMODULE for wireless communication with Aurora PVI-DESKTOP

•••••••••

Block Diagram and Effi ciency Curves

2 AURORA UNO

PVI-6000-OUTD-US PVI-6000-OUTD-US

90

91

92

93

94

95

96

97

98

99

100

0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100%

E�ci

ency

, %

% of Rated Output Power

250 Vdc

345 Vdc

480 Vdc

250

300

345

400

480

10% 20% 30% 50% 75% 100%

96,8

96,5

96,2

95,9

95,6

95,3

95 94,7

94,4 94,1

93,8

93,5

93,2

92,9

92,6

97,1

97,1

96,8

96,5

96,2

95,9

96,5

96,2

95

[%] o

f Rat

ed P

ower

MPPT Voltage [V]

BLOCK DIAGRAM OF PVI-5000-OUTD AND PVI-6000-OUTD FOR NORTH AMERICA

IN1

+

-

MPPT 1(DC/DC)

IN2

+

-

MPPT 2(DC/DC)

BULK CAPSINVERTER(DC/AC)

LINEFILTER

GRID PARALLELRELAY

L1

L2

PE

RESIDUAL CURRENTDETECTION

DC/DCDSP

CONTR.

DC/ACDSP

CONTR.

µP

CONTROL CIRCUIT

RS485

+ T/R

- T/R

RTN

REMOTE CONTROL

+ R

- R

ALARM

N.C

N.O

C

IN1(+)

IN1(-)

IN1

IN2

+

-

+

-

IN2(+)

IN2(-)

GROUNDFAULT

DETECTION

-S VERSION

N

3AURORA UNO

PARAMETER PVI-5000-OUTD-US PVI-6000-OUTD-US

Input SideAbsolute Maximum DC Input Voltage (Vmax,abs) 600 VStart-up DC Input Voltage (Vstart) 200 V (adj. 120...350 V)Operating DC Input Voltage Range (Vdcmin...Vdcmax) 0.7 x Vstart...580 VRated DC Input Power (Pdcr) 5150 W 6180 WNumber of Independent MPPT 2Maximum DC Input Power for each MPPT (PMPPTmax) 4000 WDC Input Voltage Range with Parallel Configuration of MPPT at Pacr 200...530 VDC Power Limitation with Parallel Configuration of MPPT Linear Derating From MAX to Null [530V≤VMPPT≤580V]

DC Power Limitation for each MPPT with Independent Configuration of MPPT at Pacr , max unbalance example

4000 W [225V≤VMPPT≤530V] the other channel: Pdcr-4000W

[90V≤VMPPT≤530V]

4000 W [230V≤VMPPT≤530V] the other channel: Pdcr-4000W

[120V≤VMPPT≤530V] Maximum DC Input Current (Idcmax) / for each MPPT (IMPPTmax) 36.0 A / 18.0 AMaximum Input Short Circuit Current for each MPPT 22.0 ANumber of DC Inputs Pairs for each MPPT 1DC Connection Type Screw Terminal Block, 3 Knock-Outs: 1 ½” or 1” (w/ Ring Reducer)Input ProtectionReverse Polarity protection Yes, from limited current sourceInput Over Voltage Protection for each MPPT - Varistor 2Photovoltaic Array Isolation Control GFDI (for use with either Positive or Negative Grounded Arrays)DC Switch Rating for each MPPT (-S Version) 25 A / 600 V Output Side 208 V 240 V 277 V 208 V 240 V 277 VAC Grid Connection Type Single phase / Split phaseRated AC Power (Pacr) 5000 W 6000 WMaximum AC Output Power (Pacmax) 5000 W 6000 WRated AC Grid Voltage (Vac,r) 208 V 240 V 277 V 208 V 240 V 277 VAC Voltage Range 183...228 V 211...264 V 244...304 V 183...228 V 211...264 V 244...304 VMaximum AC Output Current (Iac,max) 27.0 A 23.0 A 20.0 A 30.0 A 28.0 A 24.0 ARated Output Frequency (fr) 60 HzOutput Frequency Range (fmin...fmax) 59.3...60.5 HzNominal Power Factor (Cosphiac,r) > 0.995Total Current Harmonic Distortion < 2%AC Connection Type Screw terminal blockOutput Protection 208 V 240 V 277 V 208 V 240 V 277 VAnti-Islanding Protection According to UL 1741/IEE1547Maximum AC Overcurrent Protection 35.0 A 30.0 A 25.0 A 40.0 A 35.0 A 30.0 AOutput Overvoltage Protection - Varistor 2 (L1 - L2 / L1 - PE)Operating Performance 208 V 240 V 277 V 208 V 240 V 277 VMaximum Efficiency (ηmax) 97.1% 97.1%Weighted Efficiency (EURO/CEC) 96.0% 96.5% 96.5% 96.0% 96.5% 96.5%Feed In Power Threshold 20.0 WStand-by Consumption < 8.0 WCommunicationWired Local Monitoring PVI-USB-RS485_232 (opt.), PVI-DESKTOP (opt.)Remote Monitoring PVI-AEC-EVO (opt.), AURORA-UNIVERSAL (opt.)Wireless Local Monitoring PVI-DESKTOP (opt.) with PVI-RADIOMODULE (opt.)User Interface 16 characters x 2 lines LCD displayEnvironmentalAmbient Temperature Range -25...+60°C (-13...+ 140°F) with derating above 50°C (122°F)Relative Humidity 0...100% condensingNoise Emission <50 db(A) @ 1 mMaximum Operating Altitude without Derating 2000 m / 6560 ftPhysical Environmental Protection Rating IP 65Cooling NaturalDimension (H x W x D) 1052mm x 325mm x222mmm / 41.4” x 12.8” x 8.7”Weight < 27.0 kg / 59.5 lbMounting System Wall bracketSafetyIsolation Level TransformerlessMarking cCSAusSafety and EMC Standard UL 1741, CSA - C22.2 N. 107.1-01Grid Standard IEEE 1547Available Products VariantsWith DC Switch PVI-5000-OUTD-US PVI-6000-OUTD-US

www.power-one.com

4 AURORA UNO

Ver.

2011

-02.

2-EN

- Al

l pro

duct

s are

subj

ect t

o te

chni

cal i

mpr

ovem

ents

with

out n

otic

e.

Power-One Renewable Energy Worldwide Sales OfficesCountry Name/Region Telephone EmailAustralia Asia Pacific +61 2 9735 3111 [email protected] Asia Pacific +86 755 2988 5888 ext.5588 [email protected] Asia Pacific +65 6896 3363 [email protected] Europe 00 800 00287672 Choix n°4 [email protected] Europe +49 7641 955 2020 [email protected] Europe +39 055 9195 396 [email protected] Europe +34 629253564 [email protected] Kingdom Europe +44 1903 823 323 [email protected] Middle East +971 50 100 4142 [email protected] North America +1 877 261-1374 [email protected] East North America +1 877 261-1374 [email protected] Central North America +1 877 261-1374 [email protected] West North America +1 877 261-1374 [email protected]

Appendix D –Calculations

Calculation of Sound Power Levels

Inverter

Power One Aurora Uno 5kW inverter specifications indicate a sound pressure level of <50 dB(A) at a distance of 1 m. Sound power level for the inverter has been calculated using the following equation:

Lw = Lp – log(dr/dt) +11

Where:

Lw = sound power (dBA)

dr = Reference distance (1 m)

dt = Test distance

Lw = 50 – log(1/1) + 11 = 61 dB(A)

In the absence of frequency spectra for the inverter it has been assumed that noise from the inverter is tonal and a 5 dB penalty has therefore been applied as required by Section 4 of NPC-104.

Transformer

In the absence of a transformer make and model number, sound pressure has been calculated using data published in NEMA TR 1 – 1993 (R2000) Table 0.3. From Table 0.3, for an immersed (fluid filled) transformer:

Transformer Size Average Sound Pressure (at ≤1 m)

51 – 100 kVA 51 dB

101 – 300 kVA 55 dB

Anticipated transformer size is 100 kVA, as this size is at the limit of a size range the average sound pressure (at ≤1m) for the next highest size range has been conservatively applied. The sound power level for the transformer has been calculated using the following equation:

Lw = Lp – log(dr/dt) +11

Where:

Lw = sound power (dBA)

dr = Reference distance (1 m)

dt = Test distance

Lw = 55 – log(1/1) + 11 = 66.0 dB(A)

In the absence of frequency spectra for the inverter it has been assumed that noise from the transformer is tonal and a 5 dB penalty has therefore been applied as required by Section 4 of NPC-104.

Sound Pressure Levels

Sound pressure levels have been calculated conservatively assuming that sound attenuation between the source and the PORs was due solely to geometric divergence (atmospheric absorption, barriers and absorptive ground were not taken into consideration).

The on-site road traffic associated to the renewable energy project will be restricted to occasional visits for maintenance or engineering purposes. As such traffic will be infrequent and so excluded as per Annex to Publication NPC-232 section A.3 (2).

The following equations were employed to calculate sound pressure at points of reception from source power levels including attenuation due to geometric divergence only (from ISO 9613 (Part 2) and to calculate the total sound pressure level at points of reception due to operation of multiple stationary sources:

2 1 20 log1

2

Where:

r1 = distance 1 (reference)

r2 = distance 2 (receptor

Lp1 = Sound pressure level at r1

Lp2 = Sound pressure level at r2

10logLn

10

Where:

Ltot = total sound pressure at POR for all sources

Ln = sound pressure level at POR from source n

Example Calculations:

I01 – Inverter is located 86 m from POR1 and generates a sound pressure of <50 dBA at a distance of 1 m (manufacturer’s specifications). In the absence of frequency data a penalty of 5 dBA has been applied for possible tonality.

Sound pressure at 1 m = 55 dBA

2 1 20 log

2 55 20 log86

116

As each inverter generates the same sound pressure level at 1 m and is approximately the same distance from POR1:

10log Ln

10

10 log 2016

10

21

1030

Tables 3 and 4 in Appendix B summarize results obtained through application of the above equations.

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