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Appendix G- Environmental Noise Assessment · MCU23/0078
Environmental Noise Assessment Noosa Civic Village Mixed Use Development At Eenie Creek Road, Noosaville On Behalf of Stockwell Development Group Pty Ltd 22BRA0078 R01_2
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About TTM
For 40 years, we’ve been at the centre of the
Australian development and infrastructure industry.
Our unique combination of acoustics, data, traffic
and waste services is fundamental to the success of
any architectural or development project.
We have over 50 staff, with an unrivalled depth of
experience. Our industry knowledge, technical
expertise and commercial insight allow us to deliver
an exceptional and reliable service.
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Revision Record
No. Author Reviewed/Approved Description Date
A A Ashworth S Yorke Internal draft 21/04/2023
0 A Ashworth Client draft 26/04/2023
1 I Llamas A Ashworth Client issue 03/05/2023
2 A Ashworth DA Issue 24/05/2023
© 2023 - TTM Consulting Pty Ltd ABN 65 010 868 621
Level 8/369 Ann Street, Brisbane. PO Box 12015 Brisbane QLD 4003
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Executive Summary
TTM was engaged by Stockwell Development Group Pty Ltd to undertake an environmental
noise assessment of the Noosa Civic Village Mixed Use Development located at Eenie Creek
Road, Noosaville. The assessment was based on the Noosa Council Planning Scheme (Noosa
Plan 2020).
Unattended noise monitoring was conducted to determine the current ambient noise levels at
the site location and nearest sensitive receivers.
Impacts from relevant onsite noise activities were assessed. Compliance with the relevant
planning scheme codes is predicted to be achieved with the inclusion of façade treatments and
noise management measures as outlined in Section 7 of this report.
Mechanical plant screening is recommended in accordance with Acceptable Outcome AO79
(Major Centre Zone Code). Additionally, it is recommended that a mechanical plant noise
assessment be completed once plant selections are finalised during detailed design stage.
Compliance with the Noosa Council Planning Scheme is predicted to be achieved based on the
implementation of the recommendations outlined in Section 7 of this report.
© 2023 - TTM Consulting Pty Ltd ABN 65 010 868 621
Level 8/369 Ann Street, Brisbane. PO Box 12015 Brisbane QLD 4003
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Contents
Executive Summary .......................................................................................................................................2
1 Introduction ..........................................................................................................................................6
1.1 Background .................................................................................................................................. 6
1.2 References.................................................................................................................................... 6
1.3 Scope ............................................................................................................................................ 6
2 Site Description .....................................................................................................................................7
2.1 Site Location ................................................................................................................................. 7
2.2 Current Site Conditions ................................................................................................................ 7
3 The Proposed Development ...................................................................................................................8
3.1 Development Description............................................................................................................. 8
4 Measurements ......................................................................................................................................9
4.1 Equipment .................................................................................................................................... 9
4.2 Unattended Noise Monitoring ..................................................................................................... 9
4.3 Noise Source Measurements .....................................................................................................10
4.4 Results of Measurements ...........................................................................................................10
4.4.1 Ambient Noise Levels .....................................................................................................10
5 Noise Criteria....................................................................................................................................... 12
5.1 Noosa Plan 2020.........................................................................................................................12
5.2 Environmental Protection (Noise) Policy ....................................................................................16
5.2.1 Acoustic Quality Objectives ............................................................................................16
5.2.2 Background Creep ..........................................................................................................16
6 Analysis – Onsite Noise ........................................................................................................................ 18
6.1 Noise Sensitive Receivers ...........................................................................................................18
6.2 Noise Source Levels ....................................................................................................................20
6.3 Calculation Assumptions ............................................................................................................20
6.4 Predicted Onsite Noise Levels at Receivers ................................................................................23
6.4.1 Acoustic Quality Objectives (EPP) ...................................................................................23
6.4.2 Background Creep (EPP) .................................................................................................25
6.5 Outdoor Entertainment Area Noise Emissions ...........................................................................26
7 Recommendations............................................................................................................................... 30
Site: Eenie Creek Road, Noosaville 3
Reference: 22BRA0078 R01_2
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7.1 Onsite Residential Building Attenuation .....................................................................................30
7.2 Management Strategies .............................................................................................................30
7.3 Mechanical Plant Noise ..............................................................................................................31
8 Conclusion ........................................................................................................................................... 32
Appendix A Development Plans................................................................................................................ 33
Appendix B Unattended Noise Monitoring Graphs ................................................................................... 38
Appendix C EPP Calculations .................................................................................................................... 47
Appendix D SoundPLAN Results................................................................................................................ 51
Table Index
Table 1: Measured Ambient Noise Levels – Location 1.................................................................................... 11
Table 2: Measured Ambient Noise Levels – Location 2.................................................................................... 11
Table 3: Noosa Plan 2020 with Relevant Noise Requirements ........................................................................ 12
Table 4: Major Centre Zone Code – Relevant to Noise for this development .................................................. 12
Table 5: Dual Occupancy and Multiple Dwelling Code – Relevant to Noise for this development .................. 13
Table 6: Business Activities Code – Relevant to Noise for this development ................................................... 14
Table 7: Entertainment Activities Code – Relevant to Noise for this development ......................................... 14
Table 8: Acoustic Quality Objectives at Noise Sensitive Receivers (EPP2008) ................................................. 16
Table 9: Background Creep Noise Limits at Noise Sensitive Properties (EPP2008) – Location 1 ..................... 17
Table 10: Background Creep Noise Limits at Noise Sensitive Properties (EPP2008) – Location 2 ................... 17
Table 11: Typical Noise Sources Associated with the Development ................................................................ 20
Table 12: Acoustic Quality Objective Predictions – Offsite Receivers .............................................................. 23
Table 13: Acoustic Quality Objective Predictions – Onsite Receivers .............................................................. 24
Table 14: Background Creep Predictions – Offsite Receivers........................................................................... 25
Table 15: Acoustic Quality Objective (Leq) Predictions – Offsite Receivers ..................................................... 27
Table 16: Background Creep Predictions – Offsite Receivers........................................................................... 27
Table 17: Recommended Residential Building Attenuation ............................................................................. 30
Figure Index
Figure 1: Site Locality ......................................................................................................................................... 7
Figure 2: Site Plan – Ground Level ..................................................................................................................... 8
Figure 3: Noise Monitoring Locations .............................................................................................................. 10
Figure 4: Offsite Noise Sensitive Receivers ...................................................................................................... 18
Figure 5: Onsite Noise Sensitive Receivers ....................................................................................................... 19
Figure 6: Noise Source Locations ..................................................................................................................... 22
Figure 7: Noise Source Locations – Outdoor Entertainment Area ................................................................... 26
Site: Eenie Creek Road, Noosaville 4
Reference: 22BRA0078 R01_2
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Figure 8: Outdoor Entertainment Area – Noise Contour Plot – Day and Evening time assumptions .............. 28 Figure 9: Outdoor Entertainment Area – Noise Contour Plot – Night time assumptions ................................ 29 Figure 10: Recommended Speaker Location.................................................................................................... 30 Site: Eenie Creek Road, Noosaville 5 Reference: 22BRA0078 R01_2
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1 Introduction
1.1 Background
TTM was engaged by Stockwell Development Group Pty Ltd to undertake an environmental noise
assessment of the Noosa Civic Village Mixed Use Development located at Eenie Creek Road, Noosaville. This
report will form part of a development application for consideration by Noosa Council.
1.2 References
This report is based on the following:
• Noosa 2020 Planning Scheme
• Development plans shown in Appendix A
• Site inspection, noise measurements, analysis and calculations conducted by TTM
1.3 Scope
The assessment includes the following:
• Description of the development site and proposal.
• Measurement of existing ambient noise levels.
• Statement of assessment criteria relating to noise emissions.
• Assessment of noise generated by the development onto nearby sensitive receivers.
• Analysis of measured and predicted noise levels.
• Details of noise control recommendations to be incorporated to achieve predicted compliance.
Site: Eenie Creek Road, Noosaville 6
Reference: 22BRA0078 R01_2
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2 Site Description 2.1 Site Location The site is described by the following: • Noosa Civic Shopping Centre, Eenie Creek Road, Noosaville The site locality is shown in Figure 1. Figure 1: Site Locality 2.2 Current Site Conditions The current acoustic environment at the site and surrounding area is primarily comprised of noise activities associated with the Noosa Civic Shopping Centre and local road traffic noise. Site: Eenie Creek Road, Noosaville 7 Reference: 22BRA0078 R01_2
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3 The Proposed Development
3.1 Development Description
The proposal is for the Noosa Civic Village Mixed Use Development. The development is proposed to consist
of retail uses (including dining), commercial uses, entertainment, and residential uses. The proposed
operating hours for the various aspects of the development are as follows:
• Retail: 7am – 9pm
• Indoor entertainment: 9am – 2am
• Outdoor dining: 9am – 2am
• Outdoor entertainment area: 9am – 2am (infrequent use proposed)
• Deliveries – 24 hours a day
Operating limitations are recommended (Section 7). A site plan of the redevelopment is presented in Figure
2. Further samples of the development plans are shown in Appendix A.
Figure 2: Site Plan – Ground Level
Site: Eenie Creek Road, Noosaville 8
Reference: 22BRA0078 R01_2
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4 Measurements
4.1 Equipment
The following equipment was used to measure existing noise levels:
• ARL EL 316 Environmental noise logger (SN# 16-707-016)
• Norsonic 140 Environmental noise logger (SN# 1406507)
• Norsonic 131 Sound Level Meter (SN# 1313158)
• RION NC-73 Sound Calibrator (SN# TTMNC73-01)
All equipment was calibrated by a National Association of Testing Authorities (NATA) accredited laboratory.
The equipment was field calibrated before and after the measurement session. No significant drift from the
reference signal was recorded.
4.2 Unattended Noise Monitoring
Unattended noise monitoring was conducted between Thursday 23rd and Thursday 30th March 2023 to
establish the existing ambient noise levels at the site location and nearest residential receivers. The noise
monitoring locations are shown in Figure 3. The ambient monitors were in a position considered
representative of the ambient noise levels experienced at the site and surrounding locations with
consideration to both access and equipment security requirements.
The microphones were in free-field locations and 1.5m above ground level. The noise monitors were set to
measure statistical noise levels in 'A'-weighting, 'Fast' response, over 15 minute intervals. Ambient noise
levels were measured in accordance with Australian Standard AS1055:2018 Acoustics – Description and
Measurement of Environmental Noise (AS1055). Weather during the monitoring period was generally fine
with approx. 2mm of rain on the 29th of March and no / negligible rainfall on all other days. Rainfall affected
data was excluded from the analysis (source: Bureau of Meteorology).
Site: Eenie Creek Road, Noosaville 9
Reference: 22BRA0078 R01_2
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Figure 3: Noise Monitoring Locations
Noise Monitor
Location 1
Noise Monitor
Location 2
4.3 Noise Source Measurements
Noise levels associated with typical on-site activities were taken from similar investigations conducted by
TTM. All measurements were conducted generally in accordance with AS1055.
4.4 Results of Measurements
4.4.1 Ambient Noise Levels
Table 1 presents the measured ambient noise levels. The Rating Background Level (RBL) is an average
minimum background noise level (10th percentile average) in accordance with planning scheme
requirements. Graphical presentation of the measured levels is shown in Appendix B. The measurement
results were used to determine the assessment criteria for the development.
Site: Eenie Creek Road, Noosaville 10
Reference: 22BRA0078 R01_2
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Table 1: Measured Ambient Noise Levels – Location 1
Time Period Measured Noise Levels, dB(A)
RBL L90 L eq
Day (7am – 6pm) 61 74
Evening (6pm – 10pm) 40 69
Night (10pm – 7am) 29 66
Operating hours (night)
Night (10pm – 2am) 31 65
Table 2: Measured Ambient Noise Levels – Location 2
Time Period Measured Noise Levels, dB(A)
RBL L90 L eq
Day (7am – 6pm) 49 66
Evening (6pm – 10pm) 37 60
Night (10pm – 7am) 29 59
Operating hours (night)
Night (10pm – 2am) 31 58
Site: Eenie Creek Road, Noosaville 11
Reference: 22BRA0078 R01_2
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5 Noise Criteria
The Noosa Shire Council (NSC) planning scheme, Noosa Plan 2020, details site specific planning scheme
zones, overlays and codes relevant to a site in the NSC local government area. Table 3 summarises the
planning scheme requirements for the site which are relevant to the noise assessment.
Table 3: Noosa Plan 2020 with Relevant Noise Requirements
Location Zone Code Development Code Policies
Dual Occupancy and Multiple
Dwelling Code Preparing a well-made
Site Major Centre Zone Code
Business Activities Code application - Appendix 1
Entertainment Activities Code
Nearest Residential Zone Code
N/A N/A
Receivers Major Centre Zone Code
Note: Safety and Amenity (Table 9.3.5.3 part) does not reference noise
5.1 Noosa Plan 2020
The Major Centre Zone Code specifies relevant noise requirements as presented in Table 4.
Table 4: Major Centre Zone Code – Relevant to Noise for this development
Performance Outcome Acceptable Outcome
PO39 AO39.1
Mixed-use buildings are designed and operated to ensure: Dwellings are designed to incorporate suitable noise
attenuation and privacy measures to reduce amenity impacts
(a) business uses manage potential impact on residents, from business uses.
including impacts associated with:
1. visual and acoustic privacy;
2. safety and security; and
3. lighting.
(b) residential uses do not limit the business opportunities of
the site.
Safety and Amenity AO78.2
PO78 Where adjoining non residential uses, dwellings are designed
Development: to incorporate suitable noise attenuation measures to reduce
a) provides a high level of residential amenity to users of amenity impacts to occupants of residential uses.
the subject site; and
b) does not unreasonably impact on the amenity
enjoyed by users of adjoining or nearby premises,
including privacy and access to sunlight.
Editor's note—Provisions for sill height, glazing, screening and
window openings are to improve the residential amenity for
occupants. Thermal performance requirements are contained in
Queensland Development Code MP4.1 Sustainable Buildings.
Energy efficiency requirements are contained in the National
Construction Code.
Site: Eenie Creek Road, Noosaville 12
Reference: 22BRA0078 R01_2
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PO79 AO79.3
Development, including mechanical plant, vehicle manoeuvring Mechanical plant is:
and communal outdoor recreation uses: a) located at least 2 metres from side or rear property
a) do not have an adverse effect on the amenity enjoyed boundary;
by users of adjacent or nearby premises through b) where located at ground level, screened by fencing
emission of noise, light, fumes or smoke; 1.5 metres in height or dense vegetation of at least
b) do not cause unreasonable disturbance to local fauna 1.5 metres in width incorporating grouped trees
through light or smoke emissions. and shrubs with maximum separation distance of 1
metre measured from the centre of the plant;
c) where located above ground level, enclosed or
screened such that it is not visible from the
street frontage nor adjoining properties; and
d) visually integrated into the line and plane of
the building and roof design and does not project
beyond the height or width of the building when
viewed from the street and adjoining properties.
Editor’s Note— Mechanical plant includes generators,
motors, compressors and pumps such as air-conditioning or
pool equipment.
To comply with AO39.1 and AO78.2, onsite activities have been assessed against the Environmental
Protection (Noise) Policy 2008 (EPP 2008).
To comply with AO79 it is recommended all mechanical plant is acoustically screened from nearby sensitive
receivers.
The Dual Occupancy and Multiple Dwelling Code specifies relevant noise requirements as presented in Table
5.
Table 5: Dual Occupancy and Multiple Dwelling Code – Relevant to Noise for this development
Performance Outcome Acceptable Outcome
PO5 AO5
Development is designed to minimise noise carrying Bedroom windows are at least 3 metres away from shared
between dwelling units or accommodation units by locating driveways, car parking areas, mechanical plant, refuse and
noise sensitive spaces such as bedrooms away from noise recycling areas, vents and exhausts.
generating areas of the development, such as car parking
areas or mechanical plant and equipment or recreational
facilities.
PO6 AO6.4
Where dwellings form part of a mixed use development, the Dwellings are designed to incorporate suitable noise attenuation
development provides residents with reasonable privacy and privacy measures to reduce amenity impacts from business
and security. uses.
It is recommended that the design of the development complies with Acceptable Outcome AO5 for
minimum residential facade setbacks (3m) from shared driveways, car parking areas, mechanical plant,
refuse and recycling areas, vents and exhausts.
Site: Eenie Creek Road, Noosaville 13
Reference: 22BRA0078 R01_2
Page 15
To comply with AO6.4, onsite activities have been assessed against the Environmental Protection (Noise)
Policy 2008 (EPP 2008).
The Business code specifies relevant noise requirements as presented in Table 6.
Table 6: Business Activities Code – Relevant to Noise for this development
Performance Outcome Acceptable Outcome
PO11 AO11.1
Business activities are operated in a The use or activity does not operate outside the hours of 7:00am to 9:00pm, seven
manner that avoids or minimises days a week, where the site directly adjoins land in the following zones:
evening, early morning or weekend
noise nuisances to sensitive land uses, a) All residential zones, except for the Tourist accommodation zone
particularly surrounding residential b) Major centre zone – High density residential precinct; or
uses. c) Rural residential zone.
AO11.2
Where the site is not specified above in AO11.1 the use does not operate outside the
hours of 6:00am to 10:00pm, seven days a week, except that a business use such as
a food and drink outlet, may operate until 12:00 midnight on a Friday and Saturday.
Noise, visual and odour impacts
PO13 AO13.1
Business activities are designed, sited Undesirable noise, visual or odour impacts on public spaces and residential uses, are
and operated to avoid environmental avoided or reduced by:
nuisances such as noise, visual or
odour impacts that unreasonably
diminish the amenity of the area or a) providing vehicle loading/unloading and refuse storage/collection facilities
surrounding uses. within enclosed service yards or courtyards; and
b) not locating site service facilities and areas along any frontage to a street or
other public space.
AO13.2
Where the business activity requires the use of acoustic attenuation measures to
mitigate adverse impacts on nearby sensitive land uses, such measures are designed
and constructed to be compatible with the local streetscape.
To comply with PO11 and PO13, onsite activities have been assessed against the Environmental Protection
(Noise) Policy 2008 (EPP 2008).
The Entertainment Activities Code specifies relevant noise requirements as presented in Table 7.
Table 7: Entertainment Activities Code – Relevant to Noise for this development
Performance Outcome Acceptable Outcome
Operation Management Plan AO11
PO11 An Operation Management plan is provided outlining how the entertainment activity will
Entertainment activities are minimise potential adverse impacts including:
located, designed and operated to a) noise mitigation and noise management protocols;
avoid significant adverse impacts b) safety and security measures;
associated with noise, privacy,
c) crowd control;
security, waste, and lighting, on
the amenity of the area. d) lighting;
e) waste management and collection; and complaint procedures.
Site: Eenie Creek Road, Noosaville 14
Reference: 22BRA0078 R01_2
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Noise
PO13 AO13
Entertainment activities avoid Noise attenuation measures are designed to be consistent with the local streetscape and
noise emissions that unreasonably do not include external roller shutters.
impact on the amenity of the area
and residential landuses.
Editor’s Note— An acoustic report
may be required to meet PO13.
Live Music
PO14 AO14.1
Live music creates entertainment Where the site is adjacent to land in a residential zone (excluding Tourist Accommodation
for patrons and vibrancy within Zone), the Noosa Business Centre High Density Residential Precinct or includes a nightclub
the streetscape and is sited to entertainment facility, live music is contained within an enclosed acoustically treated
avoid significant impacts on environment.
surrounding residential landuses.
AO14.2
Acoustic live music (not reliant on electric or electronic equipment) ceases to operate in
outdoor spaces by 9:00pm Sunday – Thursday, and by 10:00pm Friday and Saturday, with
the exception of within the Hastings Street Mixed Use Precinct or Noosa Junction
Hospitality precinct where it can operate until 10:00pm Sunday - Thursday, and by 12:00
midnight Friday and Saturday.
AO14.3
Amplified live music ceases to operate in outdoor space by 7:00pm seven days per week,
except if located within Hastings Street Mixed use precinct or Noosa Junction Hospitality
precinct where it can operate until 9:00pm Sunday - Thursday and 10:00pm Friday and
Saturday.
Editor’s Note— Liquor licences and noise matters are separately dealt with through
the Office of Liquor and Gambling.
To comply with PO13 and PO14, onsite activities have been assessed against the Environmental Protection
(Noise) Policy 2008 (EPP 2008).
Site: Eenie Creek Road, Noosaville 15
Reference: 22BRA0078 R01_2
Page 17
5.2 Environmental Protection (Noise) Policy
Schedule 6 Planning scheme policies part SC6.2 - PSP1 Preparing a well-made application, SC6.2.4 Appendix
1, states that noise emissions from onsite activities are assessed against the Environmental Protection (Noise)
Policy 2008 (EPP 2008). Details of the criteria and established noise limits are presented in the following
sections.
5.2.1 Acoustic Quality Objectives
Table 8 presents the acoustic quality objectives at noise sensitive receivers as detailed in Schedule 1 of the
EPP2008.
Table 8: Acoustic Quality Objectives at Noise Sensitive Receivers (EPP2008)
Acoustic Quality Objectives, dB(A)
Sensitive Receiver Time of Day
L Aeq,adj,1hr L A10,adj,1hr L A1,adj,1hr
Dwelling Day and Evening
50 55 65
(Outdoors) (7am – 10pm)
Day and Evening
35 40 45
Dwelling (7am – 10pm)
(Indoors) Night
30 35 40
(10pm – 7am)
5.2.2 Background Creep
This criterion is to prevent background noise progressively increasing or creeping higher over time with the
establishment of new developments in a locality. EPP2008 states that:
1. This section states the management intent for an activity involving noise.
2. To the extent that it is reasonable to do so, noise from an activity must not be—
- for noise that is continuous noise measured by LA90,T—more than nil dB(A) greater than the existing
acoustic environment measured by LA90,T; or
- for noise that varies over time measured by LAeq,adj,T—more than 5dB(A) greater than the existing
acoustic environment measured by LA90,T.
In accordance with the Environmental Protection Regulation 2008, the time period (T) is considered to be a
time interval of at least 15 minutes.
Site: Eenie Creek Road, Noosaville 16
Reference: 22BRA0078 R01_2
Page 18
The Background Creep criteria for Location 1 for steady-state and transient noise sources are stated in Table
9.
Table 9: Background Creep Noise Limits at Noise Sensitive Properties (EPP2008) – Location 1
Time Period Steady-State Noise Emission Criteria, Time Varying Noise Emission
dB(A) Criteria, dB(A)
L A90,T L Aeq,T
Day (7am – 6pm) 61 66
Evening (6pm – 10pm) 40 45
Night (10pm – 7am) 29 34
Operating hours (night)
Night (10pm – 2am) 31 36
The Background Creep criteria for Location 2 for steady-state and transient noise sources are stated in Table
10.
Table 10: Background Creep Noise Limits at Noise Sensitive Properties (EPP2008) – Location 2
Time Period Steady-State Noise Emission Criteria, Time Varying Noise Emission
dB(A) Criteria, dB(A)
L A90,T L Aeq,T
Day (7am – 6pm) 49 54
Evening (6pm – 10pm) 37 42
Night (10pm – 7am) 29 34
Operating hours (night)
Night (10pm – 2am) 31 36
Site: Eenie Creek Road, Noosaville 17
Reference: 22BRA0078 R01_2
Page 19
6 Analysis – Onsite Noise
An assessment of relevant on-site activities associated with the proposed development was conducted to
determine potential impacts at the nearest noise sensitive receivers. The primary noise sources with the
potential to impact nearby noise sensitive receivers are:
• Outdoor dining and entertainment
• Loading dock vehicle use
• Traffic movements (vehicle passby, parking noises)
6.1 Noise Sensitive Receivers
The nearest noise sensitive receivers are outlined below and shown in Figure 4 and Figure 5. If compliance
can be achieved at these receivers, then all remaining noise sensitive locations are expected to comply.
• Receiver 1: Residential dwellings to the north of the site
• Receiver 2: Residential dwellings to the west of the site
• Receivers A-C: Onsite residential dwellings
Figure 4: Offsite Noise Sensitive Receivers
Receiver 1
Receiver 2
Site: Eenie Creek Road, Noosaville 18
Reference: 22BRA0078 R01_2
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Figure 5: Onsite Noise Sensitive Receivers
Receiver A
Receiver C
Receiver B
Site: Eenie Creek Road, Noosaville 19
Reference: 22BRA0078 R01_2
Page 21
6.2 Noise Source Levels
Table 11 presents the typical noise sources associated with the development with the potential to impact
the nearest noise sensitive receivers. The noise source levels were calculated to one metre and include
corrections for tonality and impulsiveness as per AS1055. The number of events was estimated for a ‘peak’
one-hour time period providing a ‘worst case scenario’ applied to all time periods.
Outdoor entertainment area noise emissions are assessed in Section 6.5.
Table 11: Typical Noise Sources Associated with the Development
Noise Level at 1m, dB(A) ‘Peak’ events
Measured
Noise Source per hour or
Duration (sec)
L eq,T L A10,T L A1,T % of period
Car door close 2 75* 77* 83* 1397
Car pass-by 6 69 75 75 1397
Car engine start 3 72 74 74 1397
Truck pass-by / manoeuvring 20 80 82 83 18
Delivery (non-refrigerated) 60 80 83 88 9
Delivery (refrigerated) 60 85# 86# 86# 9
Roller door operation 5 69* 78* 80* 18
Waste collection 40 93* 94* 105* 4
Conversation Long term avg 65 68 72 100%
Outdoor dining Long term avg 75 78 80 100%
*Includes 2dB(A) adjustment to account for impulsiveness characteristics in accordance with AS1055
#
Includes 5dB(A) adjustment to account for tonal noise characteristics in accordance with AS1055
6.3 Calculation Assumptions
The following assumptions have been made for noise calculations:
• The onsite traffic generation rate (supplied by SLR Traffic) in the peak (1 hour) period was applied. Car
movements were considered at the nearest car parking or driveway area to the receiver. Car door
closures and engine starts were predicted from the nearest group of car parking spaces relative to the
receiver.
• The method of predicting vehicle noise from the nearest single location is conservative as the noise
sources would be spread out across the car park at varying distances from the receiver.
• The onsite heavy vehicle generation rate in a peak (1 hour) period was based on a maximum 2 deliveries
per hour per loading bay (18 per hour total). Deliveries were assumed to be 50% refrigerated.
• Waste collection was assumed as a maximum of 2 collections per hour per loading area (4 per hour).
• Truck deliveries and waste collection were predicted from the nearest loading bay and include all
activities associated with loading and unloading.
Site: Eenie Creek Road, Noosaville 20
Reference: 22BRA0078 R01_2
Page 22
• Conversation noise was assumed from the nearest loading bay, car parking or driveway area to the
receiver.
• Conversation noise was based on a ‘male’ voice with ‘raised’ vocal effort as reported in published data
contained in Harris, C.M., Handbook of Acoustical Measurements and Noise Control – 3rd ed. Ch 16.3,
Mc Graw-Hill Inc, 1991. Noise duration was assumed to be continuous over the period
• Outdoor dining was predicted from the outdoor dining area. The noise duration was assumed to be
continuous during the assessment time period. The sound level includes allowance for low-level
background amplified music.
• Noise attenuation provided by intervening building structures where applicable, with the following
attenuation values applied:
- 15dB where a structure blocks direct line of sight between the receiver and noise source.
• Noise attenuation of 7dB through an open window at a receiver was applied for internal predictions for
offsite receivers.
• It is noted that between 15 and 20dB could be expected to be achieved through a closed window or
door with standard construction, however upgraded construction to achieve a minimum noise
attenuation of 25dB has been recommended for onsite receivers.
• As events in the outdoor entertainment area will be infrequent, these have been assessed separately
from noise sources associated with the daily operation. The assessment is shown in section 6.5
• Noise source locations are shown in Figure 6.
- 1: Deliveries, Truck movements, Waste collection
- 2: Car door closure, Car engine start
- A: Car pass by
- B: Car and Truck Pass by
Site: Eenie Creek Road, Noosaville 21
Reference: 22BRA0078 R01_2
Page 23
Figure 6: Noise Source Locations
Civic plaza zone for infrequent
entertainment events
Civic plaza spine which
includes outdoor dining
Site: Eenie Creek Road, Noosaville 22
Reference: 22BRA0078 R01_2
Page 24
6.4 Predicted Onsite Noise Levels at Receivers
The predicted noise levels from typical onsite activities are based on the noise sources presented in Table 11
and the assumptions outlined in Section 6.3. Calculations are included in Appendix C.
6.4.1 Acoustic Quality Objectives (EPP)
Table 12 presents the predicted acoustic quality objective noise levels at the nearest offsite sensitive
receivers. The criteria for day/evening periods is specified in the table heading, with the night time indoor
criteria shown in brackets.
Table 12: Acoustic Quality Objective Predictions – Offsite Receivers
Predicted Noise Level, dB(A)
Noise Source L Aeq, 1hr L A10, 1 hr L A1, 1hr
Outdoors Indoors Outdoors Indoors Outdoors Indoors
Receiver
Day & Day & Eve / Day & Day & Eve / Day & Day & Eve
Criteria Evening Night Evening Night Evening / Night
50 35 / (30) 55 40 / (35) 65 45 / (40)
Car door close 22 15 24 17 30 23
Car pass-by 21 14 27 20 27 20
Car engine start 21 14 23 16 23 16
Truck pass-by 18 11 20 13 21 14
Delivery (non-refrigerated) 20 13 23 16 28 21
1
Delivery (refrigerated) 25 18 26 19 26 19
Roller door operation <10 <10 <10 <10 12 <10
Waste collection 28 21 29 22 40 33
Conversation 13 <10 16 <10 20 13
Outdoor dining 22 15 25 18 27 20
Car door close 11 <10 13 <10 19 12
Car pass-by 32 25 38 31 38 31
Car engine start <10 <10 11 <10 11 <10
Truck pass-by 25 18 27 20 28 21
Delivery (non-refrigerated) 12 <10 15 <10 20 13
2
Delivery (refrigerated) 17 10 18 11 18 11
Roller door operation <10 <10 <10 <10 <10 <10
Waste collection 20 13 21 14 32 25
Conversation <10 <10 <10 <10 12 <10
Outdoor dining 13 <10 16 <10 18 11
Notes: Day & Evening 7am-10pm, Night 10pm-7am.
All noise sources are predicted to comply at offsite receiver locations at all times.
Table 13 presents the predicted acoustic quality objective noise levels at the nearest onsite sensitive
receivers. The criteria for day/evening periods is specified in the table heading, with the night time indoor
Site: Eenie Creek Road, Noosaville 23
Reference: 22BRA0078 R01_2
Page 25
criteria shown in brackets. Predicted noise levels that exceed criteria are shown in ‘bold and underlined’
font.
Table 13: Acoustic Quality Objective Predictions – Onsite Receivers
Predicted Noise Level, dB(A)
Noise Source L Aeq, 1hr L A10, 1 hr L A1, 1hr
Outdoors Indoors Outdoors Indoors Outdoors Indoors
Receiver
Day & Day & Eve / Day & Day & Eve / Day & Day & Eve
Criteria Evening Night Evening Night Evening / Night
50 35 / (30) 55 40 / (35) 65 45 / (40)
Car door close 56 31* 58 33 64 39
Car pass-by 57 32* 63 38* 63 38
Car engine start 55 30 57* 32 57 32
Truck pass-by 56 31* 58* 33 59 34
Delivery (non-refrigerated) 38 13 41 16 46 21
A
Delivery (refrigerated) 43 18 44 19 44 19
Roller door operation 17 <10 26 <10 28 <10
Waste collection 45 20 46 21 57 32
Conversation 47 22 50 25 54 29
Outdoor dining 57 32* 60 35 62 37
Car door close 56 31* 58* 33 64 39
Car pass-by 55 30 61 36* 61 36
Car engine start 55 30 57 32 57 32
Truck pass-by 50 25 52 27 53 28
Delivery (non-refrigerated) 23 <10 26 <10 31 <10
B
Delivery (refrigerated) 28 <10 29 <10 29 <10
Roller door operation <10 <10 13 <10 15 <10
Waste collection 30 <10 31 <10 42 17
Conversation 47 22 50 25 54 29
Outdoor dining 57 32 60 35 62 37
Car door close 56 31* 58* 33 64 39
Car pass-by 55 30 61 36* 61 36
Car engine start 55 30 57* 32 57 32
Truck pass-by 50 25 52 27 53 28
Delivery (non-refrigerated) 33 <10 26 <10 31 <10
C
Delivery (refrigerated) 38 13 29 <10 29 <10
Roller door operation 14 <10 13 <10 15 <10
Waste collection 40 15 31 <10 42 17
Conversation 47 22 50 25 54 29
Outdoor dining 45 20 60 35 62 37
*A 1-3dB exceedance of criteria is considered a ‘marginal compliance’ as a 1-3dB change in noise level is typically not
discernible to the human ear in an environmental setting
Site: Eenie Creek Road, Noosaville 24
Reference: 22BRA0078 R01_2
Page 26
Notes: Day & Evening 7am-10pm, Night 10pm-7am. Predicted noise levels that exceed criteria are shown in ‘bold and
underlined’ font.
For the onsite receivers, due to the close proximity of vehicle movements and outdoor dining to the onsite
receiver facades, exceedances at the external façades are observed. The recommendation is to provide the
dwellings with façade treatment to achieve a minimum total noise reduction of 25 to allow the onsite
residential dwellings to achieve the recommended internal noise criteria with facades closed.
Refer to Section 7 for recommended noise mitigation measures.
6.4.2 Background Creep (EPP)
Table 14 presents the predicted background creep noise levels at the nearest sensitive receivers. Background
creep applies to offsite receivers.
Table 14: Background Creep Predictions – Offsite Receivers
Predicted Complies with Criteria?
External Noise Day Evening Night Operation Night
Receiver Noise Source
Level, L Aeq (7am–6pm) (6pm–10pm) (10pm–2am) (10pm–7am)
dB(A) 66dB(A) 45dB(A) 36dB(A) 34dB(A)
Car door close 22 ✓ ✓ ✓ ✓
Car pass-by 21 ✓ ✓ ✓ ✓
Car engine start 21 ✓ ✓ ✓ ✓
Truck pass-by 19 ✓ ✓ ✓ ✓
Delivery (non-refrigerated) 21 ✓ ✓ ✓ ✓
1
Delivery (refrigerated) 26 ✓ ✓ ✓ ✓
Roller door operation <10 ✓ ✓ ✓ ✓
Waste collection 28 ✓ ✓ ✓ ✓
Conversation 13 ✓ ✓ ✓ N/A
Outdoor dining 22 ✓ ✓ ✓ N/A
Day Evening Night Operation Night
(7am–6pm) (6pm–10pm) (10pm–2am) (10pm–7am)
54dB(A) 42dB(A) 36dB(A) 34dB(A)
Car door close 11 ✓ ✓ ✓ ✓
Car pass-by 32 ✓ ✓ ✓ ✓
Car engine start <10 ✓ ✓ ✓ ✓
Truck pass-by 26 ✓ ✓ ✓ ✓
Delivery (non-refrigerated) 13 ✓ ✓ ✓ ✓
2
Delivery (refrigerated) 18 ✓ ✓ ✓ ✓
Roller door operation <10 ✓ ✓ ✓ ✓
Waste collection 20 ✓ ✓ ✓ ✓
Conversation <10 ✓ ✓ ✓ N/A
Outdoor dining 13 ✓ ✓ ✓ N/A
All noise sources are predicted to comply at offsite receiver location at all times.
Site: Eenie Creek Road, Noosaville 25
Reference: 22BRA0078 R01_2
Page 27
6.5 Outdoor Entertainment Area Noise Emissions
The proposed outdoor entertainment area is intended to operate on an infrequent basis and therefore has
been assessed separately to the noise sources associated with daily operation. The events will likely be
events associated with the onsite retail, dining and entertainment, and are not going to be loud rock
concerts or dance music DJs etc.
The entertainment area may include noise emissions from patrons and amplified sound/music. A noise
assessment in SoundPLAN v9.0 was conducted for a typical event based on the following parameters:
• For Day and Evening operation (7am – 10pm), 2 speakers both operating at a maximum Sound Pressure
Level of 100dB(A) @1m.
• For Night Time operation (10pm – 2am), 2 speakers both operating at a maximum Sound Pressure Level
of 90dB(A) @1m.
• Four crowds of 75 patrons per crowd (300 patrons total).
- Outdoor crowd noise level predictions was calculated with the Hayne et al 2011 Crowd Prediction
Noise method.
• Assumed crowd and speaker source heights of 1.5m
• Noise source locations are shown in Figure 7
- 1: Speaker
- 2: Crowd of 75 people.
Figure 7: Noise Source Locations – Outdoor Entertainment Area
2 2
2 2
1 1
Site: Eenie Creek Road, Noosaville 26
Reference: 22BRA0078 R01_2
Page 28
Table 15 presents the predicted acoustic quality objective noise levels at the nearest offsite sensitive
receivers. The criteria for day/evening periods are specified in the table heading, with the night time indoor
criteria shown in brackets.
Table 15: Acoustic Quality Objective (Leq) Predictions – Offsite Receivers
Predicted Noise Level, dB(A)
Noise Source L Aeq, 1hr
Outdoors Indoors
Receiver
Day &
Day & Eve / Night
Criteria Evening
35 / (30)
50
1 Outdoor Entertainment Area 39 32 / (23)
2 Outdoor Entertainment Area 40 33 / (30)
Notes: Day & Evening 7am-10pm, Night 10pm-7am.
Crowd noise sources are predicted to comply at offsite receiver locations at all times.
The predicted acoustic quality objective noise levels for the onsite receivers were calculated and the
SoundPLAN results are shown in Appendix D. To achieve the internal noise levels the recommendation is to
provide the dwellings with façade treatment to achieve a minimum total noise reduction of 25dB with
facades closed. Refer to Section 7 for recommended noise mitigation measures.
Table 16 presents the predicted background creep noise levels at the nearest sensitive receivers. Background
creep applies to offsite receivers.
Table 16: Background Creep Predictions – Offsite Receivers
Predicted External Complies with Criteria?
Noise Level, Day Evening Night Operation
Receiver Noise Source
Day & Eve / Night (7am–6pm) (6pm–10pm) (10pm–2am)
L Aeq dB(A) 66dB(A) 45dB(A) 36dB(A)
Outdoor ✓ ✓ ✓
1 39 / 30
Entertainment Area
Day Evening Night Operation
(7am–6pm) (6pm–10pm) (10pm–2am)
54dB(A) 42dB(A) 36dB(A)
Outdoor ✓ ✓ ✓*
2 40 / 37*
Entertainment Area
*A 1dB exceedance of criteria is considered a ‘marginal compliance’ as a 1-3dB change in noise level is typically not
discernible to the human ear in an environmental setting.
Crowd noise sources are predicted to comply or marginally comply with the background creep criteria at
offsite receiver locations at all times.
Site: Eenie Creek Road, Noosaville 27
Reference: 22BRA0078 R01_2
Page 29
Figure 8 and Figure 9 present the noise contour maps for the noise impacts due to the outdoor
entertainment area for Day / Evening time and night time respectively.
Figure 8: Outdoor Entertainment Area – Noise Contour Plot – Day and Evening time assumptions
Receiver 1
Noise
Sources
Receiver 2
Onsite
Receivers
Site: Eenie Creek Road, Noosaville 28
Reference: 22BRA0078 R01_2
Page 30
Figure 9: Outdoor Entertainment Area – Noise Contour Plot – Night time assumptions
Receiver 1
Noise
Sources
Receiver 2
Onsite
Receivers
Site: Eenie Creek Road, Noosaville 29
Reference: 22BRA0078 R01_2
Page 31
7 Recommendations
Compliance with the criteria outlined in Section 5 is predicted to be achieved based on the inclusion of the
recommendations outlined below.
7.1 Onsite Residential Building Attenuation
It is recommended all onsite residential dwellings are constructed to achieve a total noise reduction of at
least 25dB. Details regarding sound reduction requirements for habitable rooms are presented in Table 17.
Table 17: Recommended Residential Building Attenuation
Required Sound Reduction Rating (Rw) for Habitable Rooms
Glazing* Glazing* External Roof and Entry Doors
> 1.8m 2 ≤ 1.8m 2 Walls Ceiling
Rw 27 Rw 24 Rw 35 Rw 35 Rw 28
*Glazing area refers to total glazing area in a room, not the area of a single window / sliding door.
Based on sound reduction requirements for 25dB reduction from Queensland Development Code MP4.4, Schedule 1
7.2 Management Strategies
The following management strategies are recommended:
a. Operating hours to be limited to 7am – 2am.
b. Amplified music for restaurants to be limited to background music only.
c. For the outdoor entertainment area:
i. Speakers to be located within the southern section of the entertainment area to remove direct
line of sight between speakers and onsite receiver facades.
Figure 10: Recommended Speaker Location
Recommended
Speaker Location
Onsite receivers
Site: Eenie Creek Road, Noosaville 30
Reference: 22BRA0078 R01_2
Page 32
ii. Day and Evening operation (7am – 10pm), 2 speakers both operating at a maximum Sound
Pressure Level of 100dB(A) @1m.
iii. Night-time operation (10pm – 2am), 2 speakers both operating at a maximum Sound Pressure
Level of 90dB(A) @1m.
d. Any speed humps should be bitumen, concrete (as part of the slab) or rubber, not metal.
e. Any grates or other protective covers in the car parking area should be rigidly fixed in position to
eliminate clanging and be maintained.
7.3 Mechanical Plant Noise
Because detailed plant selections are not available at this stage, it is not possible to carry out a detailed
examination of the noise control measures that may be required to achieve the noise targets for mechanical
plant.
To comply with AO79 it is recommended all mechanical plant is acoustically screened from nearby sensitive
receivers.
A mechanical plant noise assessment should be conducted by a suitably qualified acoustic consultant once
plant selections are finalised.
Site: Eenie Creek Road, Noosaville 31
Reference: 22BRA0078 R01_2
Page 33
8 Conclusion TTM was engaged by Stockwell Development Group Pty Ltd to undertake an environmental noise assessment of the Noosa Civic Village Mixed Use Development of Noosa Civic Shopping Centre located at Eenie Creek Road, Noosaville. The assessment was based on the Noosa Council Planning Scheme (Noosa Plan 2020). Compliance with the Noosa Council Planning Scheme is predicted to be achieved based on the implementation of the recommendations outlined in Section 7 of this report. Site: Eenie Creek Road, Noosaville 32 Reference: 22BRA0078 R01_2
Page 34
Appendix A Development Plans Site: Eenie Creek Road, Noosaville 33 Reference: 22BRA0078 R01_2
Page 35
ttm NVHON@G -LN3INdOT3A30 3SN G3XIM OVTIA JIAID VSOON PEs th ae Site: Eenie Creek Road, Noosaville Reference: 22BRA0078 RO1_2 HT 34
Page 36
ttm NVHONG cL waeay NV id LNBM3S¥E 2037 C70 eEESCON By e800 suas Ez AN3WdO73A30 3S 3x0 SOVTIA SIAID VSOON oes Bees 35 Site: Eenie Creek Road, Noosaville Reference: 22BRA0078 RO1_2
Page 37
ttm NVHONa NV 3NO TEAST OSS NOUVORSSY INGMOTSNSO om a 205% C10 emrescON By ¥9819 ane gz AN3WdO73A30 3SN G3XIN SOVTIHA SIAID VSOON SSS 36 Site: Eenie Creek Road, Noosaville Reference: 22BRA0078 RO1_2
Page 38
ert | epee: NVHON& Corsa i 4AN3WdO73A30 3SN G3XIM SOVTIA JIAID VSOON — 37 Site: Eenie Creek Road, Noosaville Reference: 22BRA0078 RO1_2
Page 39
Appendix B Unattended Noise Monitoring
Graphs
Site: Eenie Creek Road, Noosaville 38
Reference: 22BRA0078 R01_2
Page 40
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Page 47
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46
Time
Site: Eenie Creek Road, Noosaville
Reference: 22BRA0078 RO1_2
Page 48
Appendix C EPP Calculations Site: Eenie Creek Road, Noosaville 47 Reference: 22BRA0078 R01_2
Page 49
Calculations – Leq
Distance to Receivers
Noise Source Duration Leq Events Leq period R1 R2 RA RB RC
1 hour Offsite North Offsite West Resi North Resi South Resi East
Car door close 2 75 1397 74 400 260 8 8 8
Car pass-by 6 69 1397 73 385 105 6 8 8
Car engine start 3 72 1397 73 400 260 8 8 8
Truck pass-by / manoeuvring 20 80 18 70 385 175 5 10 10
Deliver (non refridgerated) 60 80 9 72 395 170 50 50 90
Deliver (refridgerated) 60 85 9 77 395 170 50 50 90
Opening / closing industrial roller5door 69 18 53 405 170 60 50 90
Waste collection 40 93 4 79 395 170 50 50 90
Conversation 60 65 60 65 385 170 8 8 8
Outdoor dining 60 75 60 75 435 230 8 8 30
Noise level after Distance loss
Car door close 22 26 56 56 56
Car pass-by 21 32 57 55 55
Car engine start 21 24 55 55 55
Truck pass-by / manoeuvring 18 25 56 50 50
Deliver (non refridgerated) 20 27 38 38 33
Deliver (refridgerated) 25 32 43 43 38
Opening / closing industrial roller door 1 8 17 19 14
Waste collection 28 35 45 45 40
Conversation 13 20 47 47 47
Outdoor dining 22 28 57 57 45
Shielding losses (building, barrier etc)
Car door close 0 15 0 0 0
Car pass-by 0 0 0 0 0
Car engine start 0 15 0 0 0
Truck pass-by / manoeuvring 0 0 0 0 0
Deliver (non refridgerated) 0 15 0 15 0
Deliver (refridgerated) 0 15 0 15 0
Opening / closing industrial roller door 0 15 0 15 0
Waste collection 0 15 0 15 0
Conversation 0 15 0 0 0
Outdoor dining 0 15 0 0 0
Noise Level at Receiver R1 R2 RA RB RC
Car door close 22 11 56 56 56
Car pass-by 21 32 57 55 55
Car engine start 21 9 55 55 55
Truck pass-by / manoeuvring 18 25 56 50 50
Deliver (non refridgerated) 20 12 38 23 33
Deliver (refridgerated) 25 17 43 28 38
Opening / closing industrial roller door 1 -7 17 4 14
Waste collection 28 20 45 30 40
Conversation 13 5 47 47 47
Outdoor dining 22 13 57 57 45
Site: Eenie Creek Road, Noosaville 48
Reference: 22BRA0078 R01_2
Page 50
Calculation – L1
Receiver Duration L1 Events L1 period R1 R2 RA RB RC
1 hour Offsite North Offsite East Resi North Resi South Resi East
Car door close 2 83 1397 82 400 260 8 8 8
Car pass-by 6 75 1397 79 385 105 6 8 8
Car engine start 3 74 1397 75 400 260 8 8 8
Truck pass-by / manoeuvring 20 83 18 73 385 175 5 10 10
Deliver (non refridgerated) 60 88 9 80 395 170 50 50 90
Deliver (refridgerated) 60 86 9 78 395 170 50 50 90
Opening / closing industrial roller
5 door 80 18 64 405 170 60 50 90
Waste collection 40 105 4 91 395 170 50 50 90
Conversation 60 72 60 72 385 170 8 8 8
Outdoor dining 60 80 60 80 435 230 8 8 30
Noise level after Distance loss
Car door close 30 34 64 64 64
Car pass-by 27 38 63 61 61
Car engine start 23 26 57 57 57
Truck pass-by / manoeuvring 21 28 59 53 53
Deliver (non refridgerated) 28 35 46 46 41
Deliver (refridgerated) 26 33 44 44 39
Opening / closing industrial roller door 12 19 28 30 25
Waste collection 40 47 57 57 52
Conversation 20 27 54 54 54
Outdoor dining 27 33 62 62 50
Shielding losses (building, barrier etc)
Car door close 0 15 0 0 0
Car pass-by 0 0 0 0 0
Car engine start 0 15 0 0 0
Truck pass-by / manoeuvring 0 0 0 0 0
Deliver (non refridgerated) 0 15 0 15 15
Deliver (refridgerated) 0 15 0 15 15
Opening / closing industrial roller door 0 15 0 15 15
Waste collection 0 15 0 15 15
Conversation 0 15 0 0 0
Outdoor dining 0 15 0 0 0
Noise Level at Receiver R1 R2 R3 RB RC
Car door close 30 19 64 64 64
Car pass-by 27 38 63 61 61
Car engine start 23 11 57 57 57
Truck pass-by / manoeuvring 21 28 59 53 53
Deliver (non refridgerated) 28 20 46 31 26
Deliver (refridgerated) 26 18 44 29 24
Opening / closing industrial roller door 12 4 28 15 10
Waste collection 40 32 57 42 37
Conversation 20 12 54 54 54
Outdoor dining 27 18 62 62 50
Site: Eenie Creek Road, Noosaville 49
Reference: 22BRA0078 R01_2
Page 51
Calculation – Background Creep
Distance to Receivers
Noise Source Duration Leq Events Leq period R1 R2
15 minutes 15 minutes Offsite North Offsite West
Car door close 2 75 350 74 400 260
Car pass-by 6 69 350 73 385 105
Car engine start 3 72 350 73 400 260
Truck pass-by / manoeuvring 20 80 5 70 385 175
Deliver (non refridgerated) 60 80 3 73 395 170
Deliver (refridgerated) 60 85 3 78 395 170
Opening / closing industrial roller5door 69 5 53 405 170
Waste collection 40 93 1 79 395 170
Conversation 60 65 15 65 385 170
Outdoor dining 60 75 15 75 435 230
Noise level after Distance loss
Car door close 22 26
Car pass-by 21 32
Car engine start 21 24
Truck pass-by / manoeuvring 19 26
Deliver (non refridgerated) 21 28
Deliver (refridgerated) 26 33
Opening / closing industrial roller door 1 9
Waste collection 28 35
Conversation 13 20
Outdoor dining 22 28
Shielding losses (building, barrier etc)
Car door close 0 15
Car pass-by 0 0
Car engine start 0 15
Truck pass-by / manoeuvring 0 0
Deliver (non refridgerated) 0 15
Deliver (refridgerated) 0 15
Opening / closing industrial roller door 0 15
Waste collection 0 15
Conversation 0 15
Outdoor dining 0 15
Noise Level at Receiver R1 R2
Car door close 22 11
Car pass-by 21 32
Car engine start 21 9
Truck pass-by / manoeuvring 19 26
Deliver (non refridgerated) 21 13
Deliver (refridgerated) 26 18
Opening / closing industrial roller door 1 -6
Waste collection 28 20
Conversation 13 5
Outdoor dining 22 13
Site: Eenie Creek Road, Noosaville 50
Reference: 22BRA0078 R01_2
Page 52
Appendix D SoundPLAN Results Site: Eenie Creek Road, Noosaville 51 Reference: 22BRA0078 R01_2
Page 53
ttm Noosa Civic Expansion, Eenie Creek Road, Noosaville Assessed receiver levels "Impact Assessement - Amplified Music, Crowd.sit" 2 Receiver Usage Fl Leg dB(A) Al RS 1.FL 31.1 2.FL 31.1 A2 RS 1.FL 31.3 2.FL 31.3 A3 RS 1.FL 31.9 2.FL 32.4 A4 RS 1.FL 52.1 2.FL 50.8 B1 RS 1.FL 57.6 2.FL 59.7 B2 RS 1.FL 52.2 2.FL 52.8 B3 RS 1.FL 34.3 2.FL 34.6 B4 RS 1.FL 35.4 2.FL 39.4 BS RS 1.FL 474 2.FL 50.4 B6 RS 1.FL 48.4 2.FL 51.6 B7 RS 1.FL 45.4 2.FL 45.8 c1 RS 1.FL 39.8 2.FL 39.9 c2 RS GF 29.4 1.FL 29.4 2.FL 29.4 c3 RS GF 32.0 1.FL 32.0 2.FL 36.7 C4 RS GF 31.9 1.FL 32.3 2.FL 33.6 Receiver 1 (offsite) RS GF 38.8 Receiver 2 (offsite) RS GF 39.9 TTM Consulting Pty Ltd SOUNSFLAN 8. Site: Eenie Creek Road, No Reference: 22BRA0078 RO1_2 52
Page 54
ttm Assessed receiver levels Noosa Civic Expansion, Eenie Creek Road, Noosaville "Impact Assessement - Amplified Music, Crowd NIGHT.sit" 2 Receiver FI Dir Leq GB(A) Al 1.FL N 23.2 2.FL 23.2 A2 1.FL E 23.7 2.FL 23.6 A3 1.FL SE 26.1 2.FL 28.3 AA 1.FL Sw 50.4 2.FL 49.9 Bi 1.FL NW 50.0 2.FL 53.3 B2 1.FL NE $1.6 2.FL 52.1 B3 1.FL SE 28.0 2.FL 29.2 B4 1.FL SE 27.3 2.FL 31.0 BS 1.FL Sw 37.5 2.FL 40.4 B6 1.FL NW 39.3 2.FL 42.2 B7 1.FL NW 36.2 2.FL 38.0 c1 1.FL NE 39.4 2.FL 39.6 c2 GF SE 214 1.FL 214 2.FL 214 c3 GF Sw 23.2 1.FL 23.2 2.FL 27.2 c4 GF NW 25.9 1.FL 27.5 2.FL 29.5 Receiver 1 (offsite) GF 29.6 Receiver 2 (offsite) GF 36.9 TTM Consulting Pty Ltd SouncPLAN 2.0 Site: Eenie Creek Road, Reference: 22BRA00 53
Page 55
ttm Receiver Locations Receiver C eo ake e Receiver A 54 Site: Eenie Creek Road, Noosaville Reference: 22BRA0078 RO1_2
Used in these records
Appendix G- Environmental Noise Assessment.pdfRelated documentApplication case desk ↗
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