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App A Noise Assessment · MCU18/0102.02
Appendix A Entertainment Noise Assessment Request for an ‘Other Change’ to the Development Approval (MCU18/0102) 14 – 16 Mary Street, Noosaville 4566 QLD Lots 3 and 4 on RP 122928 Bounce Hostel Noosa Pty Ltd ATF The Bounce Hostel Unit Trust
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Entertainment Noise
Assessment
Bounce Noosa, Noosaville
Prepared for Bounce Noosa
Document Reference #1408d1-B
Document Revision BB
Date of Issue 14 October 2022
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Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Document Control
Prepared for
Mark Baldwin
14 Mary St, Noosaville QLD 4566
T 0416 897 259
[email protected]
Prepared by
Live It Acoustics
33 Tombarra Street, Mooloolaba QLD 4557
T 1300 775 800
[email protected]
Quality Information
Document Name Bounce Noosa, Noosaville – Entertainment Noise Assessment
Document No. 1408d1-B
Author (s) Jessica Appel
Reviewer Lachlan Gleeson
Authorised by Tristan Shalhoub
Revision History
Revision Status Date Principal Editor Comments
A Issue 13/10/2022 Jessica Appel
B Issue 14/10/2022 Lachlan Gleeson
Disclaimer
This report was compiled in accordance with the policies and procedures found within Live It Acoustics Quality
Management System (QMS) which is based on Australian and New Zealand Standard AS/NZS ISO 9001-2016
Quality management systems.
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Entertainment Noise Assessment
Glossary
Term Description
AS1055 Australian Standard AS1055:2018 Acoustics – Description and measurement of environmental noise.
Background Noise Background noise is the term used to describe the underlying level of noise present in the ambient noise, measured
in the absence of the noise under investigation when extraneous noise is removed.
BOM Bureau of Meteorology.
CEML Close external monitoring location. A location selected within 25m of the boundary of the licensed premises, in the
general direction of each of the representative affected premises.
dBA A-weighted decibels. The sound level meter replicates the human response of the ear by using an electronic filter
which is called the “A” filter.
dBC C-weighted decibels. C-Weighting is usually used for peak measurements and also in entertainment noise
measurements, where the transmission of bass noise can be a problem.
dBZ Z-weighted decibels. Z-Weighting is a flat frequency response of 10Hz to 20kHz ±1.5dB.
EPA 94 Environmental Protection Act 1994.
Free-field Free-field is a situation in which no sound reflections occur.
Impulsive noise Having a high peak of short duration or a sequence of such peaks. A sequence of impulses in rapid succession is
termed repetitive impulsive noise.
L10 The sound pressure level that is exceeded for 10% of the time for which the given sound is measured.
L90 The level of noise exceeded for 90% of the time. The bottom 10% of the sample is the L90 noise level expressed
in units of dB(A).
Leq The “equivalent noise level” is the summation of noise events and integrated over a selected time period.
NMM Noise Management Manual Version 4.01.
RAP Represented affected premises. A premise identified by the acoustic consultant that may be adversely affected by
noise emanating from the licensed premises.
RPL Reference point locations. A measurement location in a public place, near to a representative affected premise and
that is easily and safely accessible at all times.
SLPA Specific licensed premises areas. The specific licensed premises area should be selected such that is representative
of the typical loudest area within the licensed premises. A monitoring location within each of the identified
entertainment-producing areas to be used to determine the maximum operating noise level for the area (3m from
the source/speaker may be suitable but not obligatory).
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Bounce Noosa, Noosaville #1408d1-B 14 Mary St, Noosaville QLD 4566 Date: 14 October 2022 Entertainment Noise Assessment Table of Contents Glossary ................................................................................................................................................. ii 1 Introduction ................................................................................................................................... 1 1.1 Objectives .............................................................................................................................. 1 1.2 Assessment Limitations ....................................................................................................... 1 2 Site Description............................................................................................................................. 2 2.1 Licensed Premises Location ............................................................................................... 2 2.2 Representative Affected Premises ..................................................................................... 2 2.3 Proposed Operations ........................................................................................................... 3 3 Regulatory Requirements ............................................................................................................ 5 4 Assessment Methodology ........................................................................................................... 6 4.1 Quality Standards ................................................................................................................. 6 4.2 Instrumentation ..................................................................................................................... 6 4.3 Entertainment Scenarios ..................................................................................................... 6 4.4 Noise Measurements ........................................................................................................... 7 5 Results and Discussions ............................................................................................................12 5.1 Noise Limits at Close External Monitoring Locations ....................................................12 5.2 Noise Limits at Specific Licensed Premises Areas........................................................12 6 Conclusions and Recommendations .......................................................................................14 Appendix A – Calculation Summaries .............................................................................................15 Appendix B – Weather Observations...............................................................................................27 Appendix C – Detailed Measurement Locations ............................................................................29 List of Tables Table 1. Representative affected premises ...................................................................................... 3 Table 2. Noise survey instrumentation .............................................................................................. 6 Table 3. Background noise measurements ....................................................................................10 Table 4. Calculated final unreasonable noise limits for CEMLs pre-6:00PM .............................12 Table 5. Calculated final unreasonable noise limits for CEMLs 6:00PM – 10:00PM ................12 Table 6. Calculated maximum level limits at the SLPA .................................................................13 Table 7. Summary of limiting criteria at SLPA................................................................................13 List of Figures Figure 1. Aerial image of the site ....................................................................................................... 2 Figure 2. Site plan of proposed entertainment producing area ..................................................... 4 Figure 3. Scenario 1 source location ................................................................................................. 7 Figure 4. External noise measurement locations ............................................................................. 8 Figure 5. Internal noise monitoring locations ................................................................................... 9 Live It Acoustics Page iii
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Bounce Noosa, Noosaville #1408d1-B
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Entertainment Noise Assessment
1 Introduction
Bounce Noosa engaged Live It Acoustics to undertake an Entertainment Noise Assessment
(ENA) at their establishment. This is hereafter referred to as “the venue”. This assessment
aims to ascertain if the venue’s proposed entertainment will comply with regulatory
requirements (Liquor Act, Liquor Reg, Guideline 51) in relation to noise. It will also provide
noise management recommendations to ensure the venue consistently complies with this
obligation. In addition, it will allow the Office of Liquor and Gaming Regulation to condition the
venue objectively in order to avoid “unreasonable noise” as defined in Liquor Regulation 2002.
1.1 Objectives
This assessment aims to achieve the following objectives:
a) Inspect the site and environs and collect relevant site-specific information.
b) Undertake a review of noise policy and regulatory requirements.
c) Identify all representative affected premises (RAPs).
d) Quantify the background noise levels through measurements.
e) Establish suitable noise limits for compliance with the regulatory requirements.
f) Measure noise levels at:
- Close External Noise Monitoring Locations (CEMLs)
- Specific Licensed Premises Areas (SLPAs)
- RAPs or Reference Point Locations (RPLs)
g) Assess the noise impacts from the venue on nearby RAPs.
h) Provide noise management and mitigation measures (if required).
1.2 Assessment Limitations
This assessment is dependent upon information provided by the client and/or third parties with
respect to the location of the proposed entertainment and how the venue is proposed to be
operated.
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2 Site Description
2.1 Licensed Premises Location
The venue is located at 14 Mary St, Noosaville QLD 4566 as shown in Figure 1 below. The
subject site is located over Lot 3 and 4 on RP122928 and is zoned as ‘District Centre Zone’,
as per the Noosa Plan 2020.
The existing acoustic environment is comprised of local road noise from Mary Street and
operational noise from surrounding businesses.
Image source: QLD Globe
Mark-ups: Live It Acoustics
RAP. 1
RAP. 2
RAP. 6
RAP. 5
RAP. 3
RAP. 4
Representative Affected Premises
Subject Site
Figure 1. Aerial image of the site
2.2 Representative Affected Premises
RAPs are identified as a property which may be adversely affected by noise emanating from
the licensed premises. Table 1 below lists the nearby RAPs with their designated identifier, as
well as their specific property information defined within the Noosa Plan. The RAPs were
determined due to their proximity to the venue.
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Table 1. Representative affected premises
SITE MAP TYPE / REAL PROPERTY
ADDRESS ADDITIONAL COMMENTS
IDENTIFIER ZONING ADDRESS
RAP.1 6 Ann St, NOOSAVILLE QLD 4566 Lot 1 on RP122928
Medium
Lot 1 on SP171708; and
RAP.2 Density 1 & 2/8 Ann St, NOOSAVILLE QLD 4566 Residential
Lot 2 on SP171708
Residential
RAP.3 PANDANUS 10 Ann St, NOOSAVILLE QLD 4566 Lot 0 – 10 on GTP414
RAP.4 District 18 Mary St, NOOSAVILLE QLD 4566 Lot 13 on RP69150 Retail Shops
RAP.5 Centre 12 Mary St, NOOSAVILLE QLD 4566 Lot 6 on RP66851 Residential
Medium
RAP.6 Density 4 Ann St, NOOSAVILLE QLD 4566 Lot 5 on RP66851 Residential
Residential
2.3 Proposed Operations
The venue has the potential to host amplified entertainment anywhere within their licensed
area in the centre of the complex. The bar/cafe is situated on the external Northern façade of
Pod A (Reception building), overlooking the venues pool and entertainment deck. Pod B, C
and D accommodation units surround the entertainment area around the Western, Northern
and Eastern boundaries. The venue proposes to use their in-house sound system for amplified
entertainment, where the speakers are mounted within the bar/café area and are directed out
towards the entertainment deck.
The licensed trading hours of the venue is 7:00AM to 10:00PM, 7 days a week. However, at
councils request, the operating times have been reduced to 9:00PM until an acoustic report is
provided.
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Entertainment Noise Assessment
Image source: Bounce Noosa
Mark Up’s: Live It Acoustics
Proposed entertainment producing area
Figure 2. Site plan of proposed entertainment producing area
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3 Regulatory Requirements
The Office of Liquor and Gaming Regulation is responsible for setting noise limits on licensed
premises in Queensland.
Regulation 40 of the Liquor Regulation 2002 (Qld) prescribes that if noise exceeds the
following limits, it is "unreasonable" as defined in the Liquor Act 1992 (Qld). Therefore, the
following criteria will be used in this assessment to ascertain compliance and/or non-
compliance with:
“Between 6am and 10pm - the adjusted maximum sound pressure level LA10 must
not exceed the background level LA90 by more than 10dB (A) when measured at any
affected premises.
Between 10pm and 6am - the sound pressure level LOCT10 in a full octave band with
centre frequencies from 63Hz to 2000Hz, must not exceed the background level,
LOCT90, by more than 8dB in any octave band when measured at any affected
premises.”
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4 Assessment Methodology
4.1 Quality Standards
Noise measurements were conducted in accordance with Australian Standard AS1055:2018
Acoustics – Description and measurement of environmental noise and the Department of
Environment and Science Noise Management Manual Version 4.01 (NMM 2020).
4.2 Instrumentation
Table 2 below displays a list of noise survey instrumentation used for this noise assessment.
Table 2. Noise survey instrumentation
Model Description Manufacturer Serial #
NL-52 Sound level meter Rion 01254317
NC-73 Field calibrator Rion 11248297
n/a Wall Speakers n/a n/a
Opera 15 Speakers DB Technologies n/a
4.2.1 Calibration of Instrumentation
The noise logger was calibrated with a Rion NC-73 calibrator at a sound pressure level of
94.0dBA at 1kHz before and after each set of measurements. Calibration drift was found to be
within ±0.5dB and therefore considered acceptable.
4.2.2 Meteorological Conditions
Wind speed was collected immediately prior to testing recording a wind speed of less than 5
m/s using a Kestrel 2000 anemometer.
Wind speed and direction were also acquired from the Bureau of Meteorology (BOM) Tewantin
(Station ID: 040908). A summary is provided in Appendix B – Weather Observations
4.3 Entertainment Scenarios
Bounce Noosa intends to utilise amplified entertainment through their in-house speakers
mounted within their undercover bar area. To set the noise limits for the entertainment-
producing areas, noise levels were assessed with one (1) venue operating configuration
(scenario) for the identified area. Details of the scenario are as follows:
Scenario 1. PA Speakers situated on the bar, facing the Northern boundary which
is directed at the entertainment deck, pool and Pod A accommodation
units.
Photographs of the sound source measurement locations during on-site testing are presented
below in Figure 3.
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Figure 3. Scenario 1 source location
4.4 Noise Measurements
All potentially affected premises around the venue were identified, followed by selecting the
representative affected premises and all reference point test locations, as seen below in Figure
4 and Figure 5. For more details regarding the specific positioning of each monitoring location,
refer to Appendix C – Detailed Measurement Locations.
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Entertainment Noise Assessment
Image source: QLD Globe
Mark-ups: Live It Acoustics
L1
CEML1 L2
CEML2
CEML4
L5
L3
CEML3
Measurement Location
Subject Site
Figure 4. External noise measurement locations
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Entertainment Noise Assessment
Image source: Bounce Noosa
Mark-ups: Live It Acoustics
SLPA 1
SLPA monitoring locations
PA speaker locations
Figure 5. Internal noise monitoring locations
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4.4.1 Background Noise Measurements
It was observed that at each of the RAPs there was little variance in the ambient noise
environment. Therefore, the two (2) background noise measurement locations were chosen
to represent the RAPs, as listed below:
- L1 to represent RAP.1, RAP.2, RAP.3 & RAP.6; and
- L5 to represent RAP.4 and RAP.5
The pre-6:00PM and 6:00PM – 10:00PM background noise measurements were taken on 12
October 2022, between 11:00AM & 12:00AM and 9:00PM & 10:00PM. Measurements were
conducted at these specific times, as it is believed to have the lowest background noise levels
within each selected time period. The measurement location was positioned in a free-field
environment. The background noise measurements are summarised below in Table 3. The
measurement locations are provided in further detail in Appendix C – Detailed Measurement
Locations.
Table 3. Background noise measurements
Assessment Location Measurement Date Time Duration Overall L90
Period Number
Pre 6:00PM L2 100 11:12AM 10 minutes 42 dBA
L5 101 11:25AM 48 dBA
12/10/2022
6:00PM – 10:00PM L2 11 9:40PM 10 minutes 40 dBA
L5 12 9:55PM 43 dBA
4.4.2 Specific Licensed Premises Area Noise Measurements
In both entertainment producing areas, a measurement location which represents the SLPA
was selected to be 3 metres from the primary sound source (the PA speakers). The
measurement location within the identified entertainment-producing areas was chosen, as
shown in Figure 3 along with their location marked in Figure 5. The measurement taken from
this location was used to determine the maximum operating noise level for the entertainment
producing area.
It should be noted that our testing was undertaken using a specific music track typical of
modern music. The music track used for testing was Jimmy Barnes – ‘Good Times’.
4.4.3 Intrusive Noise Measurements
Intrusive noise measurements were conducted on 21 September 2022, between 10:00AM and
12:00PM. CEMLs were selected within 25m of the boundary of the venue, in the general
direction of each of the RAPs where the signal from the source was first detected.
Noise measurements were taken at the RAPs and where this was not possible due to
accessibility or poor signal to noise ratio, selected reference point locations (RPLs) to the
representative premises were used instead. These locations were used in conjunction with the
RAP noise measurements, to extrapolate the intrusive noise levels using acoustic theory back
to the façades of the RAPs where measurements were unable to be taken. Distance
attenuation was calculated in accordance with ISO 9613-2:1996 (section 7.1 – Geometrical
divergence). RPLs have been utilised in this assessment in the locations listed below:
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• L1 extrapolated back to RAP.1
• L2 extrapolated back to RAP.2.
• L3 extrapolated back to RAP.4.
• L5 extrapolated back to RAP.5.
• L1 extrapolated back to RAP.6.
Intrusive noise measurements were adjusted for noise character in accordance with the
procedure detailed within Australian Standard AS1055:2018.
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5 Results and Discussions
The results have been tabulated from the calculation summaries seen in Appendix A –
Calculation Summaries to present the maximum noise level limits which should be measured
for compliance.
5.1 Noise Limits at Close External Monitoring Locations
Presented below in Table 4 to Table 5 are the calculated level limits at the CEMLs
representative of the RAPs for the pre-10:00PM (dBA) and 6:00PM – 10:00PM (dBA)
scenarios.
Table 4. Calculated final unreasonable noise limits for CEMLs pre-6:00PM
Close external monitoring Final Maximum Noise Limit at
Maximum noise limit at CEML re: RAP, dBA [1]
location [2] CEML, dBA
Scenario 1
RAP.1 RAP.6
CEML1 56
57 56
RAP.2 RAP.3
CEML2 63
64 63
RAP.4
CEML3 77
77
RAP.5
CEML4 73
73
[1]
Measured in dBA using a ‘Fast’ Time Weighting.
[2]
CEML locations are marked in Appendix C – Detailed Measurement Locations.
Table 5. Calculated final unreasonable noise limits for CEMLs 6:00PM – 10:00PM
Close external monitoring Final Maximum Noise Limit at
Maximum noise limit at CEML re: RAP, dBA [1]
location [2] CEML, dBA
Scenario 1
RAP.1 RAP.6
CEML1 54
55 54
RAP.2 RAP.3
CEML2 61
62 61
RAP.4
CEML3 72
72
RAP.5
CEML4 68
68
[1]
Measured in dBC or dBZ using a ‘Fast’ Time Weighting.
[2]
CEML locations are marked in Appendix C – Detailed Measurement Locations.
5.2 Noise Limits at Specific Licensed Premises Areas
Presented below in Table 6 are the calculated SLPA level limits for the venue. The limits
presented indicate the calculated level limit for the scenario configuration, when measured at
the SLPA in either dBA (before 10:00PM) or dBC (after 10:00PM) using a ‘Fast’ time weighting.
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Table 6. Calculated maximum level limits at the SLPA
Representative affected Maximum noise limit at SLPAs [1]
Entertainment type
premises Pre – 6:00PM, dBA [2] 6:00PM – 10:00PM, dBA [2]
RAP.1 75 74
RAP.2 82 80
Amplified RAP.3 81 79
entertainment with
patron noise. RAP.4 95 90
RAP.5 87 82
RAP.6 75 73
[1]
Maximum noise limits is to be the lowest of the levels recorded for the SLPAs.
[2]
Measured at the SLPA location identified for the scenario, in dBA using a ‘Fast’ Time Weighting.
Table 7 below displays the final limiting criteria for the most affected premises. Should these
levels be adhered to, compliance should be achieved at all representative affected premises.
Table 7. Summary of limiting criteria at SLPA
Scenario Pre – 6:00PM, dBA [1] 6:00PM – 10:00PM, dBA [1]
1 75 73
[1]
Measured at the SLPA location identified for the scenario, in dBA using a ‘Fast’ Time Weighting.
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6 Conclusions and Recommendations
A noise assessment was conducted at Bounce Noosa by Live It Acoustics personnel.
The assessment demonstrated that noise emanating from the venue (amplified entertainment
i.e. DJs and/or non-amplified entertainment and patron noise) could produce nuisance noise
at the representative affected premises if noise levels at the source are not managed.
Therefore, to comply with the requirements of the Office of Liquor and Gaming Regulation with
regards to amplified entertainment at the venue, the following recommendations should be
adhered to:
1. Noise emanating from the premises including amplified and/or non-amplified noise
must not exceed the following levels, fast response, when measured at CEML1:
a) 56 dBA between 10:00AM and 6:00PM
b) 54 dBA between 6:00PM and 10:00PM.
Alternatively, should access to the licensed premises not be obtained:
2. Noise emanating from the premises including amplified and/or non-amplified
noise must not exceed the following levels, fast response, when measured at
CEML3:
a) 77 dBA between 10:00AM and 6:00PM
b) 72 dBA between 6:00PM and 10:00PM.
Should further information be required, do not hesitate to contact Live It Acoustics.
Assessment and Report by Assessment and Report overseen by
Jessica Appel Tristan Shalhoub
BEnvSc MDesSc (Audio and Acoustics), A.A.A.S.
Acoustic Consultant Principal Acoustic Consultant
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Appendix A – Calculation Summaries
Pre-6:00PM Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - pre-6pm
RAP.1 - 6 Ann St, NOOSAVILLE QLD 4566
PRE
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 1-1 L2 100 11:12AM 10 mins < 2m/s E L90 51 dBZ 44 dBZ 40 dBZ 39 dBZ 37 dBZ 35 dBZ 53 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 25 dBA 28 dBA 31 dBA 36 dBA 37 dBA 36 dBA 42 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 52 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - pre-6pm
Scenario 1 - RAP.1 - 6 Ann St, NOOSAVILLE QLD 4566
PRE
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 RAP1 \ \ 3 mins < 2m/s E L10 83 dBZ 82 dBZ 72 dBZ 71 dBZ 67 dBZ 65 dBZ 86 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 57 dBA 66 dBA 63 dBA 68 dBA 67 dBA 66 dBA 73 dBA
Row 2-6 L1 3 10:39AM 3 mins < 2m/s E L10 84 dBZ 83 dBZ 74 dBZ 73 dBZ 68 dBZ 66 dBZ 87 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 58 dBA 67 dBA 65 dBA 70 dBA 68 dBA 67 dBA 75 dBA
Row 2-11 CEML1 2 10:35AM 3 mins < 2m/s E L10 88 dBZ 87 dBZ 84 dBZ 86 dBZ 79 dBZ 78 dBZ 93 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 62 dBA 71 dBA 75 dBA 83 dBA 79 dBA 79 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
85 2-3,
dBZ whichever
87 dBZ is 69
applicable)
dBZ 67 dBZ 64 dBZ 62 dBZ 89 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 59 dBA 71 dBA 60 dBA 64 dBA 64 dBA 63 dBA 73 dBA
Row 2-22 Noise character 16
Row 2-23 Adjusted intrusive noise level due to noise character 78 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 52 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 27 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 46 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 57 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 75 dBA
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Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - pre-6pm
RAP.2 - 1 & 2/8 Ann St, NOOSAVILLE QLD 4566
PRE
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 1-1 L2 100 11:12AM 10 mins < 2m/s E L90 51 dBZ 44 dBZ 40 dBZ 39 dBZ 37 dBZ 35 dBZ 53 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 25 dBA 28 dBA 31 dBA 36 dBA 37 dBA 36 dBA 42 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 52 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - pre-6pm
PRE Scenario 1 - RAP.2 - 1 & 2/8 Ann St, NOOSAVILLE QLD 4566
6PM Measurement Details Wind Noise Octave band centre frequencies
Overall
Location Number Start Duration Speed Directio Descr- 63 125 250 500 1000 2000
Row 2-1 RAP2 \ \ 3 mins < 2m/s E L10 77 dBZ 78 dBZ 74 dBZ 72 dBZ 67 dBZ 64 dBZ 82 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 51 dBA 62 dBA 65 dBA 69 dBA 67 dBA 65 dBA 73 dBA
Row 2-6 L2 5 10:47AM 3 mins < 2m/s E 79 dBZ 79 dBZ 75 dBZ 73 dBZ 68 dBZ 65 dBZ 83 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 53 dBA 63 dBA 66 dBA 70 dBA 68 dBA 66 dBA 75 dBA
Row 2-11 CEML2 4 10:42AM 3 mins < 2m/s E L10 90 dBZ 89 dBZ 85 dBZ 86 dBZ 80 dBZ 77 dBZ 94 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 64 dBA 73 dBA 76 dBA 83 dBA 80 dBA 78 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
80 2-3,
dBZ whichever
83 dBZ is 71
applicable)
dBZ 68 dBZ 65 dBZ 62 dBZ 85 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 54 dBA 67 dBA 62 dBA 65 dBA 65 dBA 63 dBA 72 dBA
Row 2-22 Noise character 13
Row 2-23 Adjusted intrusive noise level due to noise character 72 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 52 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 20 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 52 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 64 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 82 dBA
Page 16 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 22
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - pre-6pm
PRE RAP.3 - PANDANUS 10 Ann St, NOOSAVILLE QLD 4566
6PM Measurement Details Wind Noise Octave band centre frequencies
Overall
Location Number Start Duration Speed Directio Descr- 63 125 250 500 1000 2000
Row 1-1 L2 100 11:12AM 10 mins < 2m/s E L90 51 dBZ 44 dBZ 40 dBZ 39 dBZ 37 dBZ 35 dBZ 53 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 25 dBA 28 dBA 31 dBA 36 dBA 37 dBA 36 dBA 42 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 52 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - pre-6pm
PRE Scenario 1 - RAP.3 - PANDANUS 10 Ann St, NOOSAVILLE QLD 4566
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 L2 5 10:47AM 3 mins < 2m/s E 79 dBZ 79 dBZ 75 dBZ 73 dBZ 68 dBZ 65 dBZ 83 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 53 dBA 63 dBA 66 dBA 70 dBA 68 dBA 66 dBA 75 dBA
Row 2-6 0 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 -26 dBA -16 dBA -9 dBA -3 dBA 0 dBA 1 dBA 5 dBA
Row 2-11 CEML2 4 10:42AM 3 mins < 2m/s E L10 90 dBZ 89 dBZ 85 dBZ 86 dBZ 80 dBZ 77 dBZ 94 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 64 dBA 73 dBA 76 dBA 83 dBA 80 dBA 78 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
81 2-3,
dBZ whichever
84 dBZ is 72
applicable)
dBZ 69 dBZ 66 dBZ 63 dBZ 86 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 55 dBA 68 dBA 63 dBA 66 dBA 66 dBA 64 dBA 73 dBA
Row 2-22 Noise character 13
Row 2-23 Adjusted intrusive noise level due to noise character 73 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 52 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 21 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) -19 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 63 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 81 dBA
Page 17 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 23
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - pre-6pm
PRE RAP.4 - 18 Mary St, NOOSAVILLE QLD 4566
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 1-1 L5 101 11:25AM 10 mins < 2m/s E L90 55 dBZ 50 dBZ 47 dBZ 45 dBZ 43 dBZ 41 dBZ 57 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 29 dBA 34 dBA 38 dBA 42 dBA 43 dBA 42 dBA 48 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 58 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - pre-6pm
PRE Scenario 1 - RAP.4 - 18 Mary St, NOOSAVILLE QLD 4566
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 RAP4 \ \ 3 mins < 2m/s E L10 71 dBZ 72 dBZ 64 dBZ 65 dBZ 61 dBZ 58 dBZ 75 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 45 dBA 56 dBA 55 dBA 62 dBA 61 dBA 59 dBA 66 dBA
Row 2-6 L3 7 10:56AM 3 mins < 2m/s L10 72 dBZ 74 dBZ 66 dBZ 66 dBZ 62 dBZ 60 dBZ 77 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 46 dBA 58 dBA 57 dBA 63 dBA 62 dBA 61 dBA 68 dBA
Row 2-11 CEML3 6 10:52AM 3 mins < 2m/s E L10 90 dBZ 92 dBZ 89 dBZ 85 dBZ 77 dBZ 76 dBZ 96 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 64 dBA 76 dBA 80 dBA 82 dBA 77 dBA 77 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
73 2-3,
dBZ whichever
77 dBZ is 61
applicable)
dBZ 60 dBZ 58 dBZ 56 dBZ 78 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 47 dBA 61 dBA 52 dBA 57 dBA 58 dBA 57 dBA 65 dBA
Row 2-22 Noise character 14
Row 2-23 Adjusted intrusive noise level due to noise character 65 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 58 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 7 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 58 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 77 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 95 dBA
Page 18 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 24
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - pre-6pm
PRE RAP.5 - 12 Mary St, NOOSAVILLE QLD 4566
6PM Measurement Details Wind Noise Octave band centre frequencies
Overall
Location Number Start Duration Speed Directio Descr- 63 125 250 500 1000 2000
Row 1-1 L5 101 11:25AM 10 mins < 2m/s E L90 55 dBZ 50 dBZ 47 dBZ 45 dBZ 43 dBZ 41 dBZ 57 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 29 dBA 34 dBA 38 dBA 42 dBA 43 dBA 42 dBA 48 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 58 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - pre-6pm
PRE Scenario 1 - RAP.5 - 12 Mary St, NOOSAVILLE QLD 4566
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 RAP5 \ \ 3 mins < 2m/s E L10 81 dBZ 81 dBZ 79 dBZ 73 dBZ 66 dBZ 63 dBZ 86 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 55 dBA 65 dBA 70 dBA 70 dBA 66 dBA 64 dBA 75 dBA
Row 2-6 L5 10 11:15AM 3 mins < 2m/s E L10 83 dBZ 82 dBZ 80 dBZ 75 dBZ 67 dBZ 64 dBZ 87 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 57 dBA 66 dBA 71 dBA 72 dBA 67 dBA 65 dBA 76 dBA
Row 2-11 CEML4 9 11:10AM 3 mins < 2m/s E L10 92 dBZ 97 dBZ 93 dBZ 89 dBZ 84 dBZ 83 dBZ 100 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 66 dBA 81 dBA 84 dBA 86 dBA 84 dBA 84 dBA 91 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
84 2-3,
dBZ whichever
86 dBZ is 75
applicable)
dBZ 69 dBZ 63 dBZ 60 dBZ 88 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 58 dBA 70 dBA 66 dBA 66 dBA 63 dBA 61 dBA 73 dBA
Row 2-22 Noise character 15
Row 2-23 Adjusted intrusive noise level due to noise character 73 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 58 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 15 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 58 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 73 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 87 dBA
Page 19 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 25
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - pre-6pm
RAP.6 - 4 Ann St, NOOSAVILLE QLD 4566
PRE
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 1-1 L2 100 11:12AM 10 mins < 2m/s E L90 51 dBZ 44 dBZ 40 dBZ 39 dBZ 37 dBZ 35 dBZ 53 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 25 dBA 28 dBA 31 dBA 36 dBA 37 dBA 36 dBA 42 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 52 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - pre-6pm
Scenario 1 - RAP.6 - 4 Ann St, NOOSAVILLE QLD 4566
PRE
Measurement Details Wind Noise Octave band centre frequencies
6PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 RAP6 \ \ 3 mins < 2m/s E L10 84 dBZ 83 dBZ 73 dBZ 72 dBZ 68 dBZ 65 dBZ 87 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 58 dBA 67 dBA 64 dBA 69 dBA 68 dBA 66 dBA 74 dBA
Row 2-6 L1 3 10:39AM 3 mins < 2m/s E L10 84 dBZ 83 dBZ 74 dBZ 73 dBZ 68 dBZ 66 dBZ 87 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 58 dBA 67 dBA 65 dBA 70 dBA 68 dBA 67 dBA 75 dBA
Row 2-11 CEML1 2 10:35AM 3 mins < 2m/s E L10 88 dBZ 87 dBZ 84 dBZ 86 dBZ 79 dBZ 78 dBZ 93 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 62 dBA 71 dBA 75 dBA 83 dBA 79 dBA 79 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
86 2-3,
dBZ whichever
87 dBZ is 70
applicable)
dBZ 68 dBZ 65 dBZ 63 dBZ 90 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 60 dBA 71 dBA 61 dBA 65 dBA 65 dBA 64 dBA 74 dBA
Row 2-22 Noise character 16
Row 2-23 Adjusted intrusive noise level due to noise character 79 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 52 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 27 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 45 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 56 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 75 dBA
Page 20 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 26
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
6:00PM – 10:00PM Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - 6PM to 10PM
RAP.1 - 6 Ann St, NOOSAVILLE QLD 4566
6PM-
Measurement Details Wind Noise Octave band centre frequencies
10PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 1-1 L2 11 9:40PM 10 mins < 2m/s SE L90 43 dBZ 41 dBZ 39 dBZ 37 dBZ 36 dBZ 31 dBZ 47 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 17 dBA 25 dBA 30 dBA 34 dBA 36 dBA 32 dBA 40 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 50 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - 6PM to 10PM
Scenario 1 - RAP.1 - 6 Ann St, NOOSAVILLE QLD 4566
6PM-
Measurement Details Wind Noise Octave band centre frequencies
10PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 RAP1 \ \ 3 mins < 2m/s E L10 83 dBZ 82 dBZ 72 dBZ 71 dBZ 67 dBZ 65 dBZ 86 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 57 dBA 66 dBA 63 dBA 68 dBA 67 dBA 66 dBA 73 dBA
Row 2-6 L1 3 10:39AM 3 mins < 2m/s E L10 84 dBZ 83 dBZ 74 dBZ 73 dBZ 68 dBZ 66 dBZ 87 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 58 dBA 67 dBA 65 dBA 70 dBA 68 dBA 67 dBA 75 dBA
Row 2-11 CEML1 2 10:35AM 3 mins < 2m/s E L10 88 dBZ 87 dBZ 84 dBZ 86 dBZ 79 dBZ 78 dBZ 93 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 62 dBA 71 dBA 75 dBA 83 dBA 79 dBA 79 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
85 2-3,
dBZ whichever
87 dBZ is 69
applicable)
dBZ 67 dBZ 64 dBZ 62 dBZ 89 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 59 dBA 71 dBA 60 dBA 64 dBA 64 dBA 63 dBA 73 dBA
Row 2-22 Noise character 16
Row 2-23 Adjusted intrusive noise level due to noise character 78 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 50 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 28 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 44 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 55 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 74 dBA
Page 21 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 27
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - 6PM to 10PM
RAP.2 - 1 & 2/8 Ann St, NOOSAVILLE QLD 4566
6PM-
Measurement Details Wind Noise Octave band centre frequencies
10PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 1-1 L2 11 9:40PM 10 mins < 2m/s SE L90 43 dBZ 41 dBZ 39 dBZ 37 dBZ 36 dBZ 31 dBZ 47 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 17 dBA 25 dBA 30 dBA 34 dBA 36 dBA 32 dBA 40 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 50 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - 6PM to 10PM
6PM- Scenario 1 - RAP.2 - 1 & 2/8 Ann St, NOOSAVILLE QLD 4566
10PM Measurement Details Wind Noise Octave band centre frequencies
Overall
Location Number Start Duration Speed Directio Descr- 63 125 250 500 1000 2000
Row 2-1 RAP2 \ \ 3 mins < 2m/s E L10 77 dBZ 78 dBZ 74 dBZ 72 dBZ 67 dBZ 64 dBZ 82 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 51 dBA 62 dBA 65 dBA 69 dBA 67 dBA 65 dBA 73 dBA
Row 2-6 L2 5 10:47AM 3 mins < 2m/s E 79 dBZ 79 dBZ 75 dBZ 73 dBZ 68 dBZ 65 dBZ 83 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 53 dBA 63 dBA 66 dBA 70 dBA 68 dBA 66 dBA 75 dBA
Row 2-11 CEML2 4 10:42AM 3 mins < 2m/s E L10 90 dBZ 89 dBZ 85 dBZ 86 dBZ 80 dBZ 77 dBZ 94 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 64 dBA 73 dBA 76 dBA 83 dBA 80 dBA 78 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
80 2-3,
dBZ whichever
83 dBZ is 71
applicable)
dBZ 68 dBZ 65 dBZ 62 dBZ 85 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 54 dBA 67 dBA 62 dBA 65 dBA 65 dBA 63 dBA 72 dBA
Row 2-22 Noise character 13
Row 2-23 Adjusted intrusive noise level due to noise character 72 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 50 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 22 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 50 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 62 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 80 dBA
Page 22 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 28
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - 6PM to 10PM
6PM- RAP.3 - PANDANUS 10 Ann St, NOOSAVILLE QLD 4566
10PM Measurement Details Wind Noise Octave band centre frequencies
Overall
Location Number Start Duration Speed Directio Descr- 63 125 250 500 1000 2000
Row 1-1 L2 11 9:40PM 10 mins < 2m/s SE L90 43 dBZ 41 dBZ 39 dBZ 37 dBZ 36 dBZ 31 dBZ 47 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 17 dBA 25 dBA 30 dBA 34 dBA 36 dBA 32 dBA 40 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 50 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - 6PM to 10PM
6PM- Scenario 1 - RAP.3 - PANDANUS 10 Ann St, NOOSAVILLE QLD 4566
Measurement Details Wind Noise Octave band centre frequencies
10PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 L2 5 10:47AM 3 mins < 2m/s E 79 dBZ 79 dBZ 75 dBZ 73 dBZ 68 dBZ 65 dBZ 83 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 53 dBA 63 dBA 66 dBA 70 dBA 68 dBA 66 dBA 75 dBA
Row 2-6 3 mins < 2m/s L10 0 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 -26 dBA -16 dBA -9 dBA -3 dBA 0 dBA 1 dBA 5 dBA
Row 2-11 CEML2 4 10:42AM 3 mins < 2m/s E L10 90 dBZ 89 dBZ 85 dBZ 86 dBZ 80 dBZ 77 dBZ 94 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 64 dBA 73 dBA 76 dBA 83 dBA 80 dBA 78 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
81 2-3,
dBZ whichever
84 dBZ is 72
applicable)
dBZ 69 dBZ 66 dBZ 63 dBZ 86 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 55 dBA 68 dBA 63 dBA 66 dBA 66 dBA 64 dBA 73 dBA
Row 2-22 Noise character 13
Row 2-23 Adjusted intrusive noise level due to noise character 73 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 50 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 23 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) -21 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 61 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 79 dBA
Page 23 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 29
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - 6PM to 10PM
6PM- RAP.4 - 18 Mary St, NOOSAVILLE QLD 4566
Measurement Details Wind Noise Octave band centre frequencies
10PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 1-1 L5 12 9:55PM 10 mins < 2m/s SE L90 47 dBZ 46 dBZ 41 dBZ 42 dBZ 38 dBZ 34 dBZ 51 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 21 dBA 30 dBA 32 dBA 39 dBA 38 dBA 35 dBA 43 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 53 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - 6PM to 10PM
6PM- Scenario 1 - RAP.4 - 18 Mary St, NOOSAVILLE QLD 4566
Measurement Details Wind Noise Octave band centre frequencies
10PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 RAP4 \ \ 3 mins < 2m/s E L10 71 dBZ 72 dBZ 64 dBZ 65 dBZ 61 dBZ 58 dBZ 75 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 45 dBA 56 dBA 55 dBA 62 dBA 61 dBA 59 dBA 66 dBA
Row 2-6 L3 7 10:56AM 3 mins < 2m/s L10 72 dBZ 74 dBZ 66 dBZ 66 dBZ 62 dBZ 60 dBZ 77 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 46 dBA 58 dBA 57 dBA 63 dBA 62 dBA 61 dBA 68 dBA
Row 2-11 CEML3 6 10:52AM 3 mins < 2m/s E L10 90 dBZ 92 dBZ 89 dBZ 85 dBZ 77 dBZ 76 dBZ 96 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 64 dBA 76 dBA 80 dBA 82 dBA 77 dBA 77 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
73 2-3,
dBZ whichever
77 dBZ is 61
applicable)
dBZ 60 dBZ 58 dBZ 56 dBZ 78 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 47 dBA 61 dBA 52 dBA 57 dBA 58 dBA 57 dBA 65 dBA
Row 2-22 Noise character 14
Row 2-23 Adjusted intrusive noise level due to noise character 65 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 53 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 12 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 54 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 72 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 90 dBA
Page 24 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 30
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - 6PM to 10PM
6PM- RAP.5 - 12 Mary St, NOOSAVILLE QLD 4566
10PM Measurement Details Wind Noise Octave band centre frequencies
Overall
Location Number Start Duration Speed Directio Descr- 63 125 250 500 1000 2000
Row 1-1 L5 12 9:55PM 10 mins < 2m/s SE L90 47 dBZ 46 dBZ 41 dBZ 42 dBZ 38 dBZ 34 dBZ 51 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 21 dBA 30 dBA 32 dBA 39 dBA 38 dBA 35 dBA 43 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 53 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - 6PM to 10PM
6PM- Scenario 1 - RAP.5 - 12 Mary St, NOOSAVILLE QLD 4566
Measurement Details Wind Noise Octave band centre frequencies
10PM Start Directio Descr- Overall
Location Number Duration Speed 63 125 250 500 1000 2000
Time n iptor
Row 2-1 RAP5 \ \ 3 mins < 2m/s E L10 81 dBZ 81 dBZ 79 dBZ 73 dBZ 66 dBZ 63 dBZ 86 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 55 dBA 65 dBA 70 dBA 70 dBA 66 dBA 64 dBA 75 dBA
Row 2-6 L5 10 11:15AM 3 mins < 2m/s E L10 83 dBZ 82 dBZ 80 dBZ 75 dBZ 67 dBZ 64 dBZ 87 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 57 dBA 66 dBA 71 dBA 72 dBA 67 dBA 65 dBA 76 dBA
Row 2-11 CEML4 9 11:10AM 3 mins < 2m/s E L10 92 dBZ 97 dBZ 93 dBZ 89 dBZ 84 dBZ 83 dBZ 100 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 66 dBA 81 dBA 84 dBA 86 dBA 84 dBA 84 dBA 91 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
84 2-3,
dBZ whichever
86 dBZ is 75
applicable)
dBZ 69 dBZ 63 dBZ 60 dBZ 88 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 58 dBA 70 dBA 66 dBA 66 dBA 63 dBA 61 dBA 73 dBA
Row 2-22 Noise character 15
Row 2-23 Adjusted intrusive noise level due to noise character 73 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 53 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 20 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 53 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 68 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 82 dBA
Page 25 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 31
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - 6PM to 10PM
6PM- RAP.6 - 4 Ann St, NOOSAVILLE QLD 4566
10PM Measurement Details Wind Noise Octave band centre frequencies
Overall
Location Number Start Duration Speed Directio Descr- 63 125 250 500 1000 2000
Row 1-1 L2 11 9:40PM 10 mins < 2m/s SE L90 43 dBZ 41 dBZ 39 dBZ 37 dBZ 36 dBZ 31 dBZ 47 dBZ
Row 1-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 1-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 1-6 Calculated LA90 L90 17 dBA 25 dBA 30 dBA 34 dBA 36 dBA 32 dBA 40 dBA
Row 1-7 Overall intrusive noise limit (LA90 + 10dBA) L10 50 dBA
Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - 6PM to 10PM
6PM- Scenario 1 - RAP.6 - 4 Ann St, NOOSAVILLE QLD 4566
10PM Measurement Details Wind Noise Octave band centre frequencies
Overall
Location Number Start Duration Speed Directio Descr- 63 125 250 500 1000 2000
Row 2-1 RAP6 \ \ 3 mins < 2m/s E L10 84 dBZ 83 dBZ 73 dBZ 72 dBZ 68 dBZ 65 dBZ 87 dBZ
Row 2-2 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-3 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-4 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-5 Calculated Intrusive noise level L10 58 dBA 67 dBA 64 dBA 69 dBA 68 dBA 66 dBA 74 dBA
Row 2-6 L1 3 10:39AM 3 mins < 2m/s E L10 84 dBZ 83 dBZ 74 dBZ 73 dBZ 68 dBZ 66 dBZ 87 dBZ
Row 2-7 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-8 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-9 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-10 Calculated Intrusive noise level L10 58 dBA 67 dBA 65 dBA 70 dBA 68 dBA 67 dBA 75 dBA
Row 2-11 CEML1 2 10:35AM 3 mins < 2m/s E L10 88 dBZ 87 dBZ 84 dBZ 86 dBZ 79 dBZ 78 dBZ 93 dBZ
Row 2-12 Minus insects/frogs (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-13 Plus non-standard windscreen attenuation (if applicable) 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ 0 dBZ
Row 2-14 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-15 Calculated Intrusive noise level L10 62 dBA 71 dBA 75 dBA 83 dBA 79 dBA 79 dBA 86 dBA
Row 2-16 SLPA1 1 10:30AM 3 mins < 2m/s E L10 103 dBZ 104 dBZ 104 dBZ 103 dBZ 99 dBZ 98 dBZ 110 dBZ
A-Weighted SLPA Source Measurement L10 77 dBA 88 dBA 95 dBA 100 dBA 99 dBA 99 dBA 105 dBA
Row 2-17 Normalisation Moderator 105 dBZ 109 dBZ 100 dBZ 99 dBZ 96 dBZ 95 dBZ 102 dBA
Row 2-18 Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16) 2 dBZ 5 dBZ -4 dBZ -4 dBZ -3 dBZ -3 dBZ
Row 2-19 Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1,L10 2-2 or
86 2-3,
dBZ whichever
87 dBZ is 70
applicable)
dBZ 68 dBZ 65 dBZ 63 dBZ 90 dBZ
Row 2-20 'A' frequency weighting adjustment figures -26 -16 -9 -3 0 1
Row 2-21 'A' Weighted normalised intrusive noise level, L10 L10 60 dBA 71 dBA 61 dBA 65 dBA 65 dBA 64 dBA 74 dBA
Row 2-22 Noise character 16
Row 2-23 Adjusted intrusive noise level due to noise character 79 dBA
Row 2-24 Noise limit at affected premises (Row 1-7) 50 dBA
Row 2-25 Difference between intrusive & noise limit at affected premises 29 dBA
Row 2-26 Maximum noise level at Reference Point Location (RPL) 43 dBA
Row 2-27 Maximum noise level at Close External Monitoring Location (CEML) 54 dBA
Row 2-28 Maximum noise level at specific licence area (Source) 73 dBA
Page 26 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 32
Bounce Noosa, Noosaville #1408d1-B 14 Mary St, Noosaville QLD 4566 Date: 14 October 2022 Entertainment Noise Assessment Appendix B – Weather Observations Page 27 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 33
Bounce Noosa, Noosaville #1408d1-B 14 Mary St, Noosaville QLD 4566 Date: 14 October 2022 Entertainment Noise Assessment Page 28 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 34
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Appendix C – Detailed Measurement Locations
Location Identifier Specific Licensed Premises Area 1 Location 1 (L1) Location 2 (L2) Location 3 (L3)
(SLPA1)
Representative All RAPs RAP.1 & RAP.6 RAP.2 & RAP.3 RAP.4
Affected Premises
Description 3 metres from the PA speakers situated on 1 metre from fence, centred in-front of 1 metre from both Northern and Eastern Centred with external door on Eastern
the bar within he venues entertainment drain. fence corners. façade, 1 metre from the Eastern fence.
area.
Location on map
Marked with the
red symbol
Photograph
Page 29 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 35
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Location Identifier Location 5 (L5) Close External Monitoring Location 1 Close External Monitoring Location 2 Close External Monitoring Location 3
(CEML1) (CEML2) (CEML3)
Representative RAP.5 RAP.1 & RAP.6 RAP.2 & RAP.3 RAP.4
Affected Premises
Description 1 metre from venue gate to street, 1 metre Situated over tiled path and grass corner Situated over tiled path and grass corner Centred on path, 1 metre south of exit gate
from Western fence. between venue buildings (Pod B and C) between venue buildings (Pod C and D) on the South-eastern corner of venue.
towards the North-western corner. towards the North-eastern corner.
Location on map
Marked with the
red symbol
Photograph
Page 30 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 36
Bounce Noosa, Noosaville #1408d1-B
14 Mary St, Noosaville QLD 4566 Date: 14 October 2022
Entertainment Noise Assessment
Location Identifier Close External Monitoring Location 4
(CEML4)
Representative RAP.5
Affected Premises
Description Centred on path, 1 metre North of exit gate
on the South-eastern corner of venue.
Location on map
Marked with the
red symbol
Photograph
Page 31 of 35 | Version 1.6 ▪ 19 April 2021 Live It Acoustics | 1300 775 800
Page 37
a G STRATEGIC STRATEGIC SOLUTIONS, CREATIVE THINKING rgstrategic.com.au
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