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Appendix 4 - accoustic report · MCU19/0117
Attached to the e-mail MCU19/0117 - Response to Information Request - Visitor Accommodation Type 3 – Rural (Guest House and Private Lagoon).
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon,
500/90 Beach Road, Noosa North Shore
conducted for
Mark Bain Constructions Pty Ltd
Report No: R19099/D3453/Rev.0/21.01.2020
Revision No. Date Comment
Draft 19.12.2019 Draft report.
0 21.01.2020 Original report
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Report prepared for: Mark Bain Constructions Pty Ltd
15 Ross Crescent
SUNSHINE BEACH QLD 4567
Authorised by: Ms Michelle Jackson
Office Admin./Accounts Payable
Mark Bain Constructions Pty Ltd
Phone: 07 5447 4443
Mobile: 0412 711 151
Dates of assessment: Tuesday 19 to Tuesday 26 November 2019
Consultants: David Moore & Associates Pty Ltd
(PO Box 38)
7 Eleanor Drive
SILVAN VIC 3795
Telephone: 07 3170 3222
Mobile: 0417 717 506
...................................................................................................................................
David Moore, B App Sc, MAAS
Our reference: R19099/D3453/Rev.0/21.01.2020
Page 3
Table of Contents
Page No.
INTRODUCTION ..................................................................................................................................... 1
CRITERIA ................................................................................................................................................ 4
NOISE LIMITS ......................................................................................................................................... 4
AMBIENT NOISE LEVEL MEASUREMENTS........................................................................................ 5
SOURCE NOISE LEVELS ...................................................................................................................... 7
NOISE LEVEL IMPACT .......................................................................................................................... 8
STEADY STATE NOISE SOURCES............................................................................................................. 8
TIME VARYING NOISE SOURCE ............................................................................................................... 8
NOISE CONTROL ................................................................................................................................... 9
CONCLUSIONS ...................................................................................................................................... 9
RECOMMENDATION ............................................................................................................................. 9
APPENDIX A: NOISE LEVEL MEASUREMENT EQUIPMENT.......................................................... 10
APPENDIX B: RESULTS OF NOISE LEVEL MEASUREMENTS ...................................................... 11
APPENDIX C: ATMOSPHERIC CONDITIONS FOR NOVEMBER 2019 ............................................ 16
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Mark Bain Constructions Pty Ltd Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road, Noosa North Shore Page 1 of 16 INTRODUCTION It is proposed to establish a private wave lagoon at 500/90 Beach Road, Noosa North Shore (Lot 500 on SP 215779), in the south-east corner of this property. Potential noise sources associates with this wave lagoon, which will be approximately 0.4 Ha in area, are the blowers used to generate the waves and people noise. There will also be pumps used in association with the wave lagoon, for the purpose of water transfer and water filtration/treatment. The noise of the blowers and pumps is steady state whilst the noise of people is time varying. To determine the existing acoustic environment a 7-day ambient noise assessment was conducted from the subject site, from adjacent to one of the closest adjoining residences. Typical source noise data for the pumps and people is already held by the consultant, whilst wave lagoon blower noise was obtained from an acoustic report prepared for a similar scale wave lagoon at Palm Springs, California. With respect to noise limits the now superseded version of the Environmental Protection (Noise) Policy 2008 contained details of ‘background creep’ and allocated actual noise limits for both steady state and time varying noise sources. From previous work conducted by the consultant in the Noosa Council area this is the noise limit criteria which was applied. However, whilst background creep is still detailed in the current Environmental Protection (Noise) Policy 2019, no actual noise limits are defined. Currently the only noise criteria defined by the environmental protection legislation are the default noise standards of the Environmental Protection Act 1994 and the Acoustic Quality Objectives of the Environmental Protection (Noise) Policy 2019. In preparing this report the site plan prepared by Tim Ditchfield Architects, project 1732, drawing CD 1.01 dated June 2019 was referenced. Refer Figure 1 for locality plan and noise monitoring location and Figure 2 for proposed site plan. David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 2 of 16
SUBJECT
SITE
Closest
residence
to west
Lagoon
Admiralty Towers ll
7-day noise
logger
Closest
residence
to south
Figure 1
Locality Plan for Wave Lagoon, 500/90 Beach Road, Noosa North Shore (Top of the Page is North)
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 3 of 16
Figure 2
Site Plan
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
Page 7
Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 4 of 16
CRITERIA
All noise level measurements were conducted in accordance with the following:
general requirements of the Queensland environmental protection legislation;
Environmental Protection (Noise) Policy 2019;
Noise Measurement Manual, Queensland Government, Department of Environment and Heritage
Protection, Version 4, August 2013;
Australian Standard AS 1055-2018, Acoustics – Description and Measurement of Environmental
Noise.
NOISE LIMITS
For all of the steady state and time varying noise sources the noise limits have been defined in
accordance with the Acoustic Quality Objectives and the default noise standards of the Queensland
environmental protection legislation.
In accordance with the default noise standards there are no noise limits for blowers, but the noise
limits for pumps (which, by definition includes spa blowers) are:
daytime (0700 to 1900 hours): background + 5 dB(A);
evening (1900 to 2200 hours): background + 3 dB(A);
night-time (2200 to 0700 hours): inaudible.
It has been assumed that the above noise limit criteria would be equally applicable to blowers as well
as pumps.
The acoustic quality objectives are:
Acoustic quality objectives, daytime and evening, external to dwelling:
o 50 dB(A) LAeq,adj,1H;
o 55 dB(A) LA10,adj,1H; and
o 65 dB(A) LA1,adj,1H;
Acoustic quality objectives, daytime and evening, inside dwelling:
o 35 dB(A) LAeq,adj,1H;
o 40 dB(A) LA10,adj,1H; and
o 45 dB(A) LA1,adj,1H;
Acoustic quality objectives, night-time, inside dwelling:
o 30 dB(A) LAeq,adj,1H;
o 35 dB(A) LA10,adj,1H; and
o 40 dB(A) LA1,adj,1H;
For the night-time period the internal noise criteria needs to be converted to be equivalent to outside
the closest residences. Allowing a 5 dB(A) noise level reduction from outside to inside (based on all of
the windows fully open and in accordance with the Queensland Environmental Protection Agency
Ecoaccess Guideline Planning for Noise Control) the internal criteria would be equivalent to the
following levels external to the dwelling:
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 5 of 16
Night-time
o 35 dB(A) LAeq,adj,1H;
o 40 dB(A) LA10,adj,1H; and
o 45 dB(A) LA1,adj,1H.
AMBIENT NOISE LEVEL MEASUREMENTS
Table 1 details the results of the ambient noise assessment conducted from the monitoring location on
the subject site for the daytime, evening and night-time periods – refer Figure 1 for further detail,
Appendix A for details of measurement equipment, equipment settings, calibration, etc., Appendix B
for graphical presentation of key parameters and Appendix C for atmospheric conditions.
With respect to noise the following should be noted:
daytime: 0700 to 1800 hours;
evening: 1800 to 2200 hours;
night-time: 2200 to 0700 hours;
‘A’ weighted: adjustment made by the sound level meter to the measured noise to
correspond to the response of the human ear. This adjustment is
standardised by international noise standards;
LAeq,T: the equivalent continuous (or approximately the ‘average’) ‘A’ weighted sound
pressure level for the measurement period ‘T’;
LA1,T: the ‘A’ weighted sound pressure level exceeded for 1% of the measurement
period ‘T’;
LA10,T: the ‘A’ weighted sound pressure level exceeded for 10% of the measurement
period ‘T’, which is an approximation of the ‘average of the maximum noise
levels’;
LA90,T: the ‘A’ weighted sound pressure level exceeded for 90% of the measurement
period ‘T’, which is an approximation of the ‘average of the minimum noise
levels’, which is also known as the ‘background’ noise level.
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 6 of 16
Table 1
Results of Ambient Noise Level Measurements, Noise Logger Monitoring Location
Ambient Noise Level, dB(A)
Time
Day Date LAeq LA1 LA10 LA90
Period
Range Av. Range Av. Range Av. Range Av.
Tuesday 19/11/19 Evening 36.7-49.2 42.3 38.4-62.0 53.7 37.5-48.7 43.0 35.4-41.9 36.8
Night 29.7-48.5 39.6 32.4-63.0 51.2 31.1-46.6 39.8 28.0-39.1 34.5
Daytime 38.8-51.7 45.5 43.0-65.2 54.5 40.1-49.8 46.5 34.7-45.0 41.8
Wednesday 20/11/19
Evening 35.9-59.5 48.3 37.5-74.9 63.0 36.7-49.9 42.7 35.0-44.0 38.0
Night 32.4-48.5 39.6 33.9-58.4 48.3 33.0-52.2 41.3 31.4-42.4 36.3
Daytime 39.6-52.4 45.2 44.8-66.1 55.4 40.5-57.9 47.5 35.9-42.8 40.0
Thursday 21/11/19
Evening 33.3-49.2 42.1 36.7-59.9 50.9 34.6-50.2 42.6 32.0-44.7 35.7
Night 32.6-48.2 39.0 34.4-61.1 49.1 33.2-47.8 39.4 31.4-38.5 34.3
Daytime 39.9-56.7 47.6 46.0-67.9 58.9 40.9-62.9 50.3 36.3-43.2 40.2
Friday 22/11/19
Evening 36.3-49.9 42.2 39.8-53.2 47.2 37.7-50.4 44.3 34.5-49.0 40.0
Night 36.5-46.8 42.0 38.6-58.9 48.9 37.5-48.0 43.1 35.3-43.8 39.4
Daytime 39.4-51.2 45.4 44.0-59.2 53.6 40.1-56.5 48.5 36.0-44.0 40.3
Saturday 23/11/19
Evening 37.8-51.6 45.5 39.5-63.1 54.4 38.5-52.6 46.2 36.4-50.6 42.9
Night 31.4-49.9 42.4 34.8-64.1 51.6 33.2-51.6 43.3 28.9-42.8 39.2
Daytime 39.9-48.5 45.7 43.5-60.4 51.9 40.9-52.4 48.6 37.5-44.7 41.8
Sunday 24/11/19
Evening 34.8-50.8 43.4 37.2-60.4 50.4 36.1-52.4 45.1 33.5-48.7 38.7
Night 33.8-52.8 42.4 35.8-65.9 53.3 34.7-53.9 43.3 32.5-44.0 37.9
Daytime 39.4-53.1 47.0 45.3-65.1 55.9 41.5-53.5 49.6 35.7-46.2 41.2
Monday 25/11/19
Evening 35.6-51.3 44.0 37.5-55.7 47.8 36.6-52.0 45.9 34.6-50.5 40.6
Night 37.2-56.3 45.4 39.9-71.5 59.0 38.2-50.9 42.5 35.0-41.4 38.2
Tuesday 26/11/19 Daytime 37.2-50.9 45.2 41.8-63.3 52.7 38.4-53.1 47.1 34.6-48.1 41.5
From Table 1, the following average ambient noise levels should be noted:
o LAeq,T:
o daytime: 45.2, 45.5, 45.2, 47.6, 45.4, 45.7, 47.0 Average = 45.9 dB(A);
o evening: 42.3, 48.3, 42.1, 42.2, 45.5, 43.4, 44.0 Average = 44.0 dB(A);
o night-time: 39.6, 39.6, 39.0, 42.0, 42.4, 42.4, 45.4 Average = 41.5 dB(A);
o LA1,T:
o daytime: 52.7, 54.5, 55.4, 58.9, 53.6, 51.9, 55.9 Average = 54.7 dB(A);
o evening: 53.7, 63.0, 50.9, 47.2, 54.4, 50.4, 47.8 Average = 52.5 dB(A);
o night-time: 51.2, 48.3, 49.1, 48.9, 51.6, 53.3, 59.0 Average = 51.6 dB(A);
o LA10,T:
o daytime: 47.1, 46.5, 47.5, 50.3, 48.5, 48.6, 49.6 Average = 48.3 dB(A);
o evening: 43.0, 42.7, 42.6, 44.3, 46.2, 45.1, 45.9 Average = 44.3 dB(A);
o night-time: 39.8, 41.3, 39.4, 43.1, 43.3, 43.3, 42.5 Average = 41.8 dB(A);
o LA90,T:
o daytime: 41.5, 41.8, 40.0, 40.2, 40.3, 41.8, 41.2 Average = 41.0 dB(A);
o evening: 36.8, 38.0, 35.7, 40.0, 42.9, 38.7, 40.6 Average = 39.0 dB(A);
o night-time: 34.5, 36.3, 34.3, 39.4, 39.2, 37.9, 38.2 Average = 37.1 dB(A).
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
[OCR of page images]
Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 6 of 16
Table 1
Results of Ambient Noise Level Measurements, Noise Logger Monitoring Location
Ambient Noise Level, dB(A)
Time
Day Date Period Laeq Lat Lato Laso
Range Av. Range Av. Range AV. Range AV.
Tuesday 19/11/19 | Evening | 36.7-49.2 | 42.3 | 38.4-62.0 | 53.7 | 37.5-48.7 | 43.0 | 35.4-41.9 | 36.8
Night 29.7-48.5 39.6 32.4-63.0 | 51.2 31.1-46.6 39.8 28.0-39.1 34.5
Daytime 38.8-51.7 45.5 | 43.0-65.2 | 54.5 40.1-49.8 46.5 34.7-45.0 41.8
Wednesday 20/11/19 .
Evening 35.9-59.5 48.3 37.5-74.9 | 63.0 36.7-49.9 42.7 35.0-44.0 38.0
Night 32.4-48.5 39.6 33.9-58.4 | 48.3 33.0-52.2 41.3 31.4-42.4 36.3
Daytime 39.6-52.4 45.2 | 44.8-66.1 55.4 40.5-57.9 47.5 35.9-42.8 40.0
Thursday 21/11/19 7
Evening 33.3-49.2 42.1 36.7-59.9 | 50.9 34.6-50.2 42.6 32.0-44.7 35.7
Night 32.6-48.2 39.0 34.4-61.1 49.1 33.2-47.8 39.4 31.4-38.5 34.3
Daytime 39.9-56.7 47.6 | 46.0-67.9 | 58.9 40.9-62.9 50.3 36.3-43.2 40.2
Friday 22/11/19 ,
Evening 36.3-49.9 42.2 39.8-53.2 | 47.2 37.7-50.4 44.3 34.5-49.0 40.0
Night 36.5-46.8 42.0 38.6-58.9 | 48.9 37.5-48.0 43.1 35.3-43.8 39.4
Daytime 39.4-51.2 45.4 | 44.0-59.2 | 53.6 40.1-56.5 48.5 36.0-44.0 40.3
Saturday 23/11/19 .
Evening 37.8-51.6 45.5 39.5-63.1 54.4 38.5-52.6 46.2 36.4-50.6 42.9
Night 31.4-49.9 42.4 34.8-64.1 51.6 33.2-51.6 43.3 28.9-42.8 39.2
Daytime 39.9-48.5 45.7 | 43.5-60.4 | 51.9 40.9-52.4 48.6 37.5-44.7 41.8
Sunday 24/11/19 ,
Evening 34.8-50.8 43.4 37.2-60.4 | 50.4 36.1-52.4 45.1 33.5-48.7 38.7
Night 33.8-52.8 42.4 35.8-65.9 | 53.3 34.7-53.9 43.3 32.5-44.0 37.9
Daytime 39.4-53.1 47.0 | 45.3-65.1 55.9 41.5-53.5 49.6 35.7-46.2 41.2
Monday 25/11/19 5
Evening 35.6-51.3 44.0 37.5-55.7 | 47.8 36.6-52.0 45.9 34.6-50.5 40.6
Night 37.2-56.3 45.4 39.9-71.5 | 59.0 38.2-50.9 42.5 35.0-41.4 38.2
Tuesday 26/11/19 | Daytime 37.2-50.9 45.2 | 41.8-63.3 | 52.7 38.4-53.1 47.1 34.6-48.1 41.5
From Table 1, the following average ambient noise levels should be noted:
oO Laeg,t:
o daytime:
© evening:
o night-time:
o Lait:
o daytime:
o evening:
o night-time:
oo Latot:
o daytime:
o evening:
o night-time:
oO Laso,t:
o daytime:
o evening:
o night-time:
45.2, 45.5, 45.2, 47.6, 45.4, 45.7, 47.0
42.3, 48.3, 42.1, 42.2, 45.5, 43.4, 44.0
39.6, 39.6, 39.0, 42.0, 42.4, 42.4, 45.4
52.7, 54.5, 55.4, 58.9, 53.6, 51.9, 55.9
53.7, 63.0, 50.9, 47.2, 54.4, 50.4, 47.8
51.2, 48.3, 49.1, 48.9, 51.6, 53.3, 59.0
47.1, 46.5, 47.5, 50.3, 48.5, 48.6, 49.6
43.0, 42.7, 42.6, 44.3, 46.2, 45.1, 45.9
39.8, 41.3, 39.4, 43.1, 43.3, 43.3, 42.5
41.5, 41.8, 40.0, 40.2, 40.3, 41.8, 41.2
36.8, 38.0, 35.7, 40.0, 42.9, 38.7, 40.6
34.5, 36.3, 34.3, 39.4, 39.2, 37.9, 38.2
Average = 45.9 dB(A);
Average = 44.0 dB(A);
Average = 41.5 dB(A);
Average = 54.7 dB(A);
Average = 52.5 dB(A);
Average = 51.6 dB(A);
Average = 48.3 dB(A);
Average = 44.3 dB(A);
Average = 41.8 dB(A);
Average = 41.0 dB(A);
Average = 39.0 dB(A);
Average = 37.1 dB(A).
David Moore & Associates Pty Ltd
Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 7 of 16
With respect to the above night-time ambient noise levels, the Acoustic Quality Objectives for the
night-time are:
o 35 dB(A) LAeq,adj,1H;
o 40 dB(A) LA10,adj,1H; and
o 45 dB(A) LA1,adj,1H.
The current average night-time ambient noise levels exceed this noise limit criteria by 6.5 dB(A)
LAeq,1H, 6.6 dB(A) LA1,1H and 1.8 dB(A) LA10,1H. This difference between the current average night-time
ambient noise levels and the noise limits should ensure that any noise from the proposed wave lagoon
will be either inaudible or only just barely audible at the closest residential.
Based on the above the noise limits are:
pumps and blowers:
o daytime (0700 to 1900 hours): 41 + 5 = 46 dB(A) LAeq,adj,T;
o evening (1900 to 2200 hours): 39 + 3 = 42 dB(A) LAeq,adj,T;
o night-time (2200 to 0700 hours): inaudible = ≤ 30 dB(A) LAeq,adj,T;
people noise:
o daytime and evening:
50 dB(A) LAeq,adj,1H;
55 dB(A) LA10,adj,1H; and
65 dB(A) LA1,adj,1H;
o night-time:
35 dB(A) LAeq,adj,1H;
40 dB(A) LA10,adj,1H; and
45 dB(A) LA1,adj,1H;
SOURCE NOISE LEVELS
Typical source noise levels are:
Steady state sources:
blower (total of 8):
o discharge air: 119 dB(A) LWA each;
o casing radiated: 88 dB(A) LWA;
pump (assumed 2 of): 90 dB(A) LWA;
Time varying noise source:
people: 62 dB(A) LAeq,adj,T, 70 dB(A) LA1,adj,T and 65 dB(A) LA10,adj,T @
10 m.
The blower source noise data was extracted from a report prepared for a wave lagon (believed to be
of similar size) at Palm Springs, California. The quoted blower is manufactured by Chicago Blower
Corporation, model 6105SW.
It is believed that the blowers and pumps will be located under-ground/built into an embankment and
contained within a concrete structure (or equivalent) – concrete floor, walls and roof. It has been
further assumed that the concrete structure will have a minimum Rw 50 (noise reduction of 45 dB(A)).
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 8 of 16
NOISE LEVEL IMPACT
The concrete structure containing the blowers and pumps is proposed to be located adjacent to the
western corner of the wave lagoon, which has a separation distance of approximately:
160 metres to the closest residence to the west:
700 metres from the closest residence to the south.
Compliance with the noise limits at the closest residence to the west will also result in noise limit
compliance at all other nearby residences.
Whilst it is most likely that the wave lagoon will only be used during daylight hours, this could be as
early as 0500 hours in the summer. There is also a small likelihood that the wave lagoon could be
used during the evening, up to 2200 hours. It has been assumed that the generation of waves could
occur at any time from 0500 hours to 2200 hours.
Steady State Noise Sources
At the closest residence to the west the noise of the plant and equipment, which will all be located
inside a concrete structure (or equivalent) the noise level impact would be:
blower discharge: 119 LWA + 9 (total of eight blowers) – 52 (distance of 160m) – 45
(concrete structure) – 7 (ground) = 24 dB(A) LAeq,adj,T;
122 LWA + 9 – 52 – 45 – 7 = 27 dB(A) LA1,adj,T;
120 LWA + 9 – 52 – 45 – 7 = 25 dB(A) LA10,adj,T;
blower radiated: 88 LWA + 9 (total of eight blowers) – 52 (distance of 160m) – 45
(concrete structure) – 7 (ground) = -7 dB(A) LAeq,adj,T;
91 LWA + 9 – 52 – 45 – 7 = -4 dB(A) LA1,adj,T;
89 LWA + 9 – 52 – 45 – 7 = -6 dB(A) LA10,adj,T;
pumps: 90 dB(A) LWA + 3 (two pumps) – 52 (distance of 160m) – 45
(concrete structure) – 7 (ground) = -11 dB(A) LAeq,adj,T;
93 dB(A) LWA + 3 – 52 – 45 – 7 = -8 dB(A) LA1,adj,T;
91 dB(A) LWA + 3 – 52 – 45 – 7 = -10 dB(A) LA10,adj,T;
combined: 24 dB(A) LAeq,adj,T, 27 dB(A) LA1,adj,T and 25 dB(A) LA10,adj,T.
The combined noise level of all of the eight blowers and two pumps comply with both the default noise
standard for pumps, as well as the acoustic quality objectives.
Time Varying Noise Source
The most likely time varying noise source is people noise from the wave lagoon, with a separation
distance of approximately 180 metres to the closest residence to the west.
At this closest residence to the west the noise level impact of the time varying noise source will be:
people: 62 dB(A) LAeq,adj,1H @ 10m – 25 (distance of 55m) – 7 (ground) = 30 dB(A)
LAeq,adj,1H;
70 dB(A) LA1,adj,1H @ 10m – 25 – 7 = 38 dB(A) LA1,adj,1H;
65 dB(A) LA10,adj,1H @ 10m – 25 – 7 = 33 dB(A) LA10,adj,1H;
The above people noise complies with the acoustic quality objective criteria for the daytime, evening
and night-time, with no additional noise control measures required.
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road, Noosa North Shore Page 9 of 16 NOISE CONTROL To be able to operate the wave lagoon from 0500 to 2200 hours daily, based on the source noise data available to the consultant at the time of preparing this report, all plant and equipment must be located inside a concrete structure (or equivalent) with a minimum Rw 50. Once all of the plant and equipment has been selected, the actual building location, design and materials of construction defined, together with manufacturers’ source noise data for the actual equipment to be installed, an acoustic consultant must be appointed to re-calculate noise level impact. If any of the noise limits are exceeded, appropriate noise control measures must be defined. CONCLUSIONS It is proposed to establish a private wave lagoon at 500/90 Beach Road, Noosa North Shore (Lot 500 on SP 215779), in the south-east corner of this property. Potential noise sources associates with this wave lagoon, which will be approximately 0.4 Ha in area, are the blowers used to generate the waves and people noise. There will also be pumps used in association with the wave lagoon, for the purpose of water transfer and water filtration/treatment. The noise of the blowers and pumps is steady state whilst the noise of people is time varying. To determine the existing acoustic environment a 7-day ambient noise assessment was conducted from the subject site, from adjacent to one of the closest adjoining residences. Typical source noise data for the pumps and people is already held by the consultant, whilst wave lagoon blower noise was obtained from an acoustic report prepared for a similar scale wave lagoon at Palm Springs, California. Whilst it is most likely that the wave lagoon will only be used during daylight hours, this could be as early as 0500 hours in the summer. There is also a small likelihood that the wave lagoon could be used during the evening, up to 2200 hours. It has been assumed that the generation of waves could occur at any time from 0500 hours to 2200 hours. For the steady state noise sources these all comply (individually and combined) with the default noise standards and the acoustic quality objectives. This is for the noise sources applied in this report and assuming that these steady state noise sources are located within a concrete structure with a minimum Rw 50. Once the actual noise sources are determined, and their associated noise levels available, an acoustic consultant must re-calculate noise impact. If any of the noise limits are still exceeded then noise control measures must be defined. For the time varying noise source – people – this complies with the acoustic quality objectives for the proposed hours of operation (0500 to 2200 hours daily), with no additional noise control measures required. RECOMMENDATION It is recommended that, from an environmental noise perspective, the proposed wave lagoon be approved, with no additional noise control measures required. David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 10 of 16
APPENDIX A: NOISE LEVEL MEASUREMENT EQUIPMENT
Measurement Equipment
The following equipment was used to conduct the ambient noise level measurements at the logger
monitoring location:
Bruel and Kjaer Type 2260 Precision Sound Level Analyzer, Serial No. 2487423, with Type BZ
7219, Version 1.2 Software and Prepolarised free-field ½” microphone, Type 4189, Serial No.
2469624;
Bruel and Kjaer Type 4231 Sound Level Calibrator, Serial No. 2292736.
All of the above equipment is Type 1 in accordance with the requirements of Australian Standard AS
1259-1990, Acoustics – Sound Level Meters.
Measurement Equipment Settings
The above equipment was used with the following settings:
Detector: RMS
Time Weighting: FAST
Frequency Weighting: linear in 1/3 octave bands from 20 to 20000 Hz
Sound Incidence: FRONTAL;
Sensitivity: -28.4 dB.
Calibration
The sound level meter was calibrated to the required value of 93.8 dB at 1000 Hz immediately before
and after the noise level measurements were conducted. At no time was an adjustment of more than
0.5 dB required. This complies with the requirements of the Australian Standard.
Monitoring Location
Adjacent to the western boundary of the subject site closest to the closest adjoining residence to the
south-west, which is a similar setback distance from the proposed wave lagoon (and the ocean) as all
other closest residences to the west, with the microphone elevated approximately 1.6 m above the
ground level. Refer Figure 1 for further detail.
Atmospheric Conditions
Throughout the noise level assessment atmospheric conditions generally complied with the
requirements of the Australian Standard. Refer Appendix C for details.
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 11 of 16
APPENDIX B: RESULTS OF NOISE LEVEL MEASUREMENTS
Instrument: 2260
Application: BZ7219 version 1.2
Start Time: 26/08/2019 11:42:26 AM
End Time: 02/09/2019 01:51:41 PM
Elapsed Time: 170:09:15
Bandwidth: 1/3 Octave
Peaks Over: 140.0 dB
Range: 22.4-102.4 dB
Time Frequency
Broad-band measurements: SFI AC
Broad-band statistics: F A
Octave measurements: F L
Logging
Log Rate: 0:15:00
Broadband Parameters: All
Spectrum Parameters: All
Instrument Serial Number: 2487423
Microphone Serial Number: 2469624
Input: Microphone
Windscreen Correction: None
S. I. Correction: Frontal
Calibration Time: 26/08/2019 11:38:24 AM
Calibration Level: 94.0 dB
Sensitivity: -28.4 dB
ZF0023: Not used
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
Page 15
Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 12 of 16
0002.S3D
dB
80
70
60
50
40
30
12:00:00 PM 02:00:00 PM 04:00:00 PM 06:00:00 PM 08:00:00 PM 10:00:00 PM 12:00:00 AM
LAeq LAF1 LAF10 LAF90
Cursor: 02/09/2019 12:45:00 AM - 01:00:00 AM LAeq=42.0 dB LAF1=45.0 dB LAF10=43.9 dB LAF90=40.0 dB
Day 1, Tuesday 19 November 2019, from 1145 hours
0002.S3D
dB
80
70
60
50
40
30
02:00:00 AM 06:00:00 AM 10:00:00 AM 02:00:00 PM 06:00:00 PM 10:00:00 PM
LAeq LAF1 LAF10 LAF90
Cursor: 02/09/2019 12:45:00 AM - 01:00:00 AM LAeq=42.0 dB LAF1=45.0 dB LAF10=43.9 dB LAF90=40.0 dB
Day 2, Wednesday 20 November 2019
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
Page 16
Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 13 of 16
0002.S3D
dB
80
70
60
50
40
30
02:00:00 AM 06:00:00 AM 10:00:00 AM 02:00:00 PM 06:00:00 PM 10:00:00 PM
LAeq LAF1 LAF10 LAF90
Cursor: 02/09/2019 12:45:00 AM - 01:00:00 AM LAeq=42.0 dB LAF1=45.0 dB LAF10=43.9 dB LAF90=40.0 dB
Day 3, Thursday 21 November 2019
0002.S3D
dB
80
70
60
50
40
30
02:00:00 AM 06:00:00 AM 10:00:00 AM 02:00:00 PM 06:00:00 PM 10:00:00 PM
LAeq LAF1 LAF10 LAF90
Cursor: 28/08/2019 12:15:00 AM - 12:30:00 AM LAeq=34.9 dB LAF1=36.4 dB LAF10=35.7 dB LAF90=34.1 dB
Day 4, Friday 22 November 2019
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
Page 17
Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 14 of 16
0002.S3D
dB
80
70
60
50
40
30
02:00:00 AM 06:00:00 AM 10:00:00 AM 02:00:00 PM 06:00:00 PM 10:00:00 PM
LAeq LAF1 LAF10 LAF90
Cursor: 28/08/2019 12:15:00 AM - 12:30:00 AM LAeq=34.9 dB LAF1=36.4 dB LAF10=35.7 dB LAF90=34.1 dB
Day 5, Saturday 23 November 2019
0002.S3D
dB
80
70
60
50
40
30
02:00:00 AM 06:00:00 AM 10:00:00 AM 02:00:00 PM 06:00:00 PM 10:00:00 PM
LAeq LAF1 LAF10 LAF90
Cursor: 28/08/2019 12:15:00 AM - 12:30:00 AM LAeq=34.9 dB LAF1=36.4 dB LAF10=35.7 dB LAF90=34.1 dB
Day 6, Sunday 24 November 2019
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
Page 18
Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 15 of 16
0002.S3D
dB
80
70
60
50
40
30
02:00:00 AM 06:00:00 AM 10:00:00 AM 02:00:00 PM 06:00:00 PM 10:00:00 PM
LAeq LAF1 LAF10 LAF90
Cursor: 28/08/2019 12:15:00 AM - 12:30:00 AM LAeq=34.9 dB LAF1=36.4 dB LAF10=35.7 dB LAF90=34.1 dB
Day 7, Monday 25 November 2019
0002.S3D
dB
80
70
60
50
40
30
12:00:00 AM 02:00:00 AM 04:00:00 AM 06:00:00 AM 08:00:00 AM 10:00:00 AM 12:00:00 PM 02:00:00 PM
LAeq LAF1 LAF10 LAF90
Cursor: 28/08/2019 12:15:00 AM - 12:30:00 AM LAeq=34.9 dB LAF1=36.4 dB LAF10=35.7 dB LAF90=34.1 dB
Day 8, Tuesday 26 November 2019, until 1400 hours
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
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Mark Bain Constructions Pty Ltd
Environmental Noise Level Impact Assessment for Proposed Wave Lagoon, 500/90 Beach Road,
Noosa North Shore Page 16 of 16
APPENDIX C: ATMOSPHERIC CONDITIONS FOR NOVEMBER 2019
David Moore & Associates Pty Ltd Our reference: R19099/D3453/Rev.0/21.01.2020
Used in these records
Appendix 4 - accoustic report.pdfRelated documentApplication case desk ↗
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