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Appendix D Acoustic Report - 14-16 Mary Street, Noosaville - Bounce Hostels 15.6.2018
Attached to the e-mail Visitor Accommodation Type 4 Conventional - 122 beds (Engineering Report, Economic Study, Geotechnical Investigation, Flood Certificate, Accoustic Report, Management Plan) MCU18/0102.msg.
Appendix D – Acoustic Report MATERIAL CHANGE OF USE TO ESTABLISH RESIDENTIAL USES - VISITOR ACCOMMODATION TYPE 4 CONVENTIONAL 14-16 Mary Street, NOOSAVILLE described as Lots 3 & 4 on RP 122928 Applicant: Bounce Hostel Noosa Pty Ltd ATF The Bounce Hostel Unit Trust Date: 15th June 2018 Unit 5, 100 Pickering Street, Enoggera 1
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Page 2
Noise Assessment Report
Visitor Accommodation
14-16 Mary Street
Noosaville
Report 1142R1-R0
21 March 2018
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Visitor Accommodation, Noosaville 1142R1-R0
Document control
Report 1142R1-R0
Version history:
Version no. Date Changed by Nature of amendment
Draft 1 15-Feb-18 JC Initial draft
Draft 2 15-Feb-18 JC Revised plans
Draft 3 21-Mar-18 JC Minor amendments
Draft 4 21-Mar-18 JC Revised plans
Revision 0 21-Mar-18 JC Final report
Contact for enquiries
Please direct any queries regarding the preparation of this document to:
Contact officer: Joseph Carroll
Director / Principal Engineer
RoadPro Acoustics
Job number: 1142
Email: [email protected]
Web: www.roadpro.net.au
© Copyright RoadPro Acoustics.
This report has been prepared for the exclusive use of the commissioning party and unless otherwise
agreed in writing by RoadPro Acoustics, no other party may copy, reproduce, distribute, make use of, or
rely on the contents of the report. No liability is accepted by RoadPro Acoustics for any use of this report,
other than for the purposes for which it was originally prepared and provided.
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Table of contents
1 Introduction .....................................................................................................1
2 Acoustic Terminology ....................................................................................2
Sound (Noise) Level .................................................................................2
“A” Weighted Sound Pressure Level - dB(A) ............................................2
Statistical Sound (Noise) Levels ...............................................................2
3 Noise Criteria ...................................................................................................3
Acoustic Quality Objectives ......................................................................3
Mechanical Plant Noise ............................................................................4
4 Background Noise ..........................................................................................5
5 Predicted Noise Levels ...................................................................................7
General Methodology ...............................................................................7
Air Conditioners ........................................................................................8
Refrigeration Plant ....................................................................................8
Vehicle Noise (Car Parks and Driveways) ................................................9
Guest Noise ............................................................................................10
6 Discussion of Results and Attenuation.......................................................10
Air Conditioners ......................................................................................10
Refrigeration Plant ..................................................................................10
Vehicle Noise ..........................................................................................10
Guest Noise ............................................................................................10
7 Conclusion and Summary of Recommendations .......................................11
Appendix A – Site Plans
Appendix B – Measured Noise Levels
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1 Introduction
RoadPro Acoustics was engaged by RG Strategic to assess potential noise
emissions from an accommodation facility at a site at 14-16 Mary Street,
Noosaville (the Site). The site location is shown in Figure 1, and proposed site
layout is shown in Figure 2. Plans are provided in Appendix A.
Figure 1: Site Location – 14-16 Mary Street, Noosaville
Figure 2: Site layout - 14-16 Mary Street, Noosaville
The Site is in the Business Centre Zone and Mary Street Precinct. The
proposal is a Consistent Use and is specifically designated for backpacker /
hostel accommodation within the Noosa Plan.
There will be no on-site entertainment or formal social events such as parties,
with the intention that guests who wish to engage in such activities can readily
do so off-site. This will be incorporated in the Operational Management Plan.
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2 Acoustic Terminology
The following is a brief explanation of the acoustic terminology used in this report.
Sound (Noise) Level
Sound or noise consists of minute fluctuations in atmospheric pressure capable of
evoking the sense of hearing. The human ear responds to changes in sound
pressure over a very wide range. The loudest sound pressure to which the human
ear responds is ten million times greater than the softest. The decibel (abbreviated
as dB) scale reduces this ratio to a more manageable size by the use of logarithms.
The symbols “L” or “LA” are commonly used to represent Sound Pressure Level.
“A” Weighted Sound Pressure Level - dB(A)
The overall level of a sound is usually expressed in terms of dB(A), which is
measured using a sound level meter with an “A-weighting” filter. This is an
electronic filter having a frequency response corresponding approximately to that
of human hearing.
People’s hearing is most sensitive to sounds at mid frequencies (500 Hz to
4000 Hz), and less sensitive at lower and higher frequencies. Thus, the level of a
sound in dB(A) is a good measure of the loudness of that sound. Different sources
having the same dB(A) level generally sound about equally as loud.
A change of 1 dB(A) or 2 dB(A) in the level of a sound is difficult for most people
to detect, whilst a 3 dB(A) to 5 dB(A) change corresponds to small but noticeable
change in loudness. A 10 dB(A) change corresponds to an approximate doubling
or halving in loudness. The table below shows examples of typical noise levels
Table 1: Typical Noise Levels
Sound Pressure Typical Source Subjective
Level (dB(A)) Evaluation
130 Threshold of pain Intolerable
120 Heavy rock concert Extremely
110 Grinding on steel noisy
100 Loud car horn at 3 m Very noisy
90 Construction site with pneumatic hammering
80 Curbside of busy street Loud
70 Loud radio or television
60 Department store Moderate to
50 General Office quiet
40 Inside private office Quiet to very
30 Inside bedroom quiet
20 Unoccupied recording studio Almost silent
Statistical Sound (Noise) Levels
Sounds that vary in level over time, such as road traffic noise and most community
noise, are commonly described in terms of the statistical exceedance levels LAN,
where LAN is the A-weighted sound pressure level exceeded by N% of a given
measurement period. For example, the LA1 is the noise level exceeded for 1% of
the time, LA10 the noise exceeded for 10% of the time, and so on.
Of particular relevance are:
LA1 The noise level exceeded for 1% of the 15 minute interval.
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LA10 The noise level exceed for 10% of the 15 minute interval. This is commonly
referred to as the average maximum noise level.
LA90 The noise level exceeded for 90% of the sample period. This noise level is
described as the average minimum background sound level (in the absence of
the source under consideration), or simply the background level
LAeq is the A-weighted equivalent continuous sound pressure level (basically the
average sound level). It is defined as the steady sound level that contains the
same amount of acoustical energy as a given time-varying sound.
When dealing with numerous days of statistical noise data a method is required to
determine the noise descriptors that are representative of a monitoring location for
a particular time of day. The method of statistical accumulation provides an
appropriate method of determining these noise descriptors.
This method accumulates each value for the days of monitoring and produces an
estimate of the “repeatable minimum” LA90 noise level over the daytime and night-
time measurement periods, as required by the Department of Environment and
Heritage Protection. In addition, the method produces mean or “average” levels
that are representative of the other descriptors that can be expected on a typical
day at each particular site.
3 Noise Criteria
Acoustic Quality Objectives
The Noosa Plan (Part 11 – Noosaville Locality Plant, Division 17) provides the
following with respect to amenit:
The Environmental Protection (Noise) Policy 2008 is designed to achieve the
object of the Environmental Protection Act 1994. Relevant extracts are as follows:
“The environmental values to be enhanced or protected under this policy are—
…the qualities of the acoustic environment that are conducive to protecting the amenity of the
community”
and
“…To the extent that it is reasonable to do so, noise from an activity must not be—
…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 addition to the general aims and criteria for time-varying noise emissions,
Acoustic Qualify Objectives are specified for residences as shown in Table 2.
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Table 2: Environmental Protection (Noise) Policy 2008 Acoustic Quality Objectives
Sensitive Time of Acoustic quality objectives (measured Environmental
receptor day at the receptor) dB(A) value
LAeq,adj,1hr LA10,adj,1hr LA1,adj,1hr
Dwelling Daytime 50 55 65 Health and
(for and evening wellbeing
outdoors)
Dwelling Daytime 35 40 45 Health and
(for indoors) and evening wellbeing
Nighttime 30 35 40 health and
wellbeing, in
relation to the
ability to sleep
Mechanical Plant Noise
The Environmental Protection Act 1994 specifies criteria for pumps and air
conditioning plant as follows:
440T Pumps
(1) This section applies to premises at or for which there is a pump.
(2) An occupier of the premises must not use, or permit the use of, the pump on
any day—
(a) before 7a.m, if it makes an audible noise; or
(b) from 7a.m. to 7p.m, if it makes a noise of more than 5dB(A) above the
background level; or
(c) from 7p.m. to 10p.m, if it makes a noise of more than 3dB(A) above the
background level; or
(d) after 10p.m, if it makes an audible noise.
(3) Subsection (2)(a), (c) and (d) do not apply to a noise made at an educational
institution, that is not more than 5dB(A) above the background level.
(4) In this section— Pump —
(a) means an electrical, mechanical or pneumatic pump; and
Examples — liquid pump, air pump, heat pump
(b) includes a swimming pool pump and a spa blower.
Under this definition, “pump” includes refrigeration plant.
440U Air-conditioning equipment
(1) This section applies to premises at or for which there is air-conditioning
equipment.
(2) An occupier of the premises must not use, or permit the use of, the equipment
on any day—
(a) before 7a.m, if it makes a noise of more than 3dB(A) above the
background level; or
(b) from 7a.m. to 10p.m, if it makes a noise of more than 5dB(A) above the
background level; or
(c) after 10p.m, if it makes a noise of more than 3dB(A) above the
background level.
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These criteria are applicable for noise impacting on, and produced by, the
proposed development.
440V Refrigeration equipment
(1) This section applies to a person who is—
(a) an occupier of premises at or for which there is plant or equipment for
refrigeration (refrigeration equipment); or
(b) an owner of refrigeration equipment that is on or in a vehicle, other than
a vehicle used or to be used on a railway.
(2) The person must not use, or permit the use of, the refrigeration equipment on
any day—
(a) before 7a.m, if it makes a noise of more than 3dB(A) above the
background level; or
(b) from 7a.m. to 10p.m, if it makes a noise of more than 5dB(A) above the
background level; or
(c) after 10p.m, if it makes a noise of more than 3dB(A) above the
background level.
(3) In this section—
vehicle includes a trailer.
4 Background Noise
Noise measurements were carried out at the site from Wednesday 24th January
2018 to Thursday 1st February 2018 at the locations shown in Figure 3 and Figure
4. The locations were selected as being representative of background noise levels
for the nearest sensitive receivers.
The measurements were carried out using Rion NL-21 sound level meters
recording sound levels at 15-minute intervals, with the microphone at a height of
approximately 1.2 m. The instruments were checked for calibration prior to and
post-measurement using a 94 dB acoustic signal at 1000 Hz, and drift in
calibration remained within ±0.5 dB.
Weather conditions for the duration of the survey were sourced from the Noosa
Bureau of Meteorology station, and were generally suitable for noise monitoring
throughout the measurement period.
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Figure 3: Noise Logger Locations - 14-16 Mary Street, Noosaville
Figure 4: Noise Loggers
Ambient noise at the Site consisted of intermittent traffic noise from Mary St.
A summary of the logged data over the week is provided in Table 3 and . The full
dataset of the measurements and weather is provided as charts in Appendix B.
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Visitor Accommodation, Noosaville 1142R1-RO Table 3: Logger Noise Measurement Results (northern boundary), dB(A) Date Laso(oay) Lasorevey —_Laaoinight) __Laeaioay) Lreatéve) —Lreainight) —_Larovoay) Larotevey —__Laxounight) Wednesday-24-Jan-18 34.6 29.9 57.6 53.2 44.6 42.7 Thursday-25-Jan-18 43.4 35.8 33.7 50.6 57.9 52.3 50.4 45.5 42.3 Friday-26-Jan-18 39.9 36.0 31.9 50.3 58.6 54.0 48.4 45.7 46.0 Saturday-27-Jan-18 43.9 38.1 33.8 51.9 58.6 55.5 51.5 47.7 47.2 Sunday-28-Jan-18 44.2 37.6 34.3 $2.1 58.7 55.4 51.6 49.4 47.2 Monday-29-Jan-18 46.9 38.4 37.3 55.9 59.6 56.3 54.3 49.7 48.0 Tuesday-30-Jan-18 46.3 33.5 31.9 55.4 60.4 54.3 53.0 46.0 42.6 Wednesday-31-Jan-18 40.3 39.0 32.3 51.6 59.2 58.2 49.8 50.0 54.1 Overall 41 35 32. 53 59 55 $1 47 47 Table 4: Logger Noise Measurement Results (eastern boundary), dB(A) Date Lasoiay) Lasotevey —__Lasoinight) _Laea(oay) Lreatéve) ——Lneainich) —_Larojoay) Lasorevey —_Laroqnight) Wednesday-24-Jan-18 34.7 28.7 59.0 55.1 47.4 47.4 Thursday-25-Jan-18 41.5 35.0 32.8 53.1 59.3 54.4 52.7 45.5 44.0 Friday-26-Jan-18 39.4 45.7 30.9 52.6 59.9 55.8 52.4 48.9 47.7 Saturday-27-Jan-18 42.0 36.5 31.8 54.0 59.8 57.1 54.2 48.1 49.0 Sunday-28-Jan-18 43.2 35.9 32.5 54.9 59.7 56.6 58.0 50.9 47.9 Monday-29-Jan-18 44.7 36.3 36.3 60.7 60.9 57.6 52.4 47.9 47.5 Tuesday-30-Jan-18 43.9 31.2 29.9 55.2 61.8 56.0 53.2 45.2 41.6 Wednesday-31-Jan-18 40.8 37.3 31.0 53.0 60.8 59.3 50.9 50.6 53.0 Overall 41 35 30 56 60 57 53 48 48 The following background noise levels are therefore adopted for the Site: Day 41 dB(A) Evening 35 dB(A) Night 30 dB(A) The background creep criteria for general noise such as vehicles and guests are therefore: Day Laeg,adi(t hour) $ 46 dB(A) Evening Laeg.adi(1 hour) $ 40 dB(A) Night Laeg,adj(1 hour) $ 35 dB(A) 5 Predicted Noise Levels 5.1 General Methodology The nearest potentially affected receivers to the Site and access are residences at 12 Mary Street and 4 — 10 Ann Street, shown in Figure 5. The premises at 18 Mary Street is a commercial use. www. roadpro.net.au 21 March 2018 Page 7 of 11
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Figure 5: Nearest potentially affected receivers to the Site
Noise levels were calculated using the inverse square law for geometric spreading,
and Maekawa’s equations for barrier insertion loss.
Most of the surrounding properties are 2-storey residential buildings.
Air Conditioners
The general criteria in Section 3.2 and the measured ambient noise levels in
Section 4 provide site-specific criteria for noise from air conditioners as shown in
Table 5.
Table 5: Site-Specific Criteria for Air Conditioning Plant
Period General Criterion LA90 Site-Specific
Criterion
Day (7 am-6 pm) ≤ background LA90 + 5dB(A) 30 dB 41 + 5 = 46 dB(A)
Evening (6 pm-10 pm) ≤ background LA90 + 5dB(A) 28 dB 35 + 5 = 40 dB(A)
Night (10 pm-6 am) ≤ background LA90 + 3dB(A) 27 dB 30 + 3 = 33 dB(A)
Air conditioning plant hasn’t been specified for the Site at this stage. However,
given the short distances to the Site boundaries from the Accommodation
Pavilions, it is recommended that external condenser units are located within the
undercover carpark.
Refrigeration Plant
The general criteria in Section 3.2 and the measured ambient noise levels in
Section 4 provide site-specific criteria for noise from refrigeration plant as shown
in Table 6.
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Table 6: Site-Specific Criteria for Refrigeration Plant
Period General Criterion Measured Site-Specific
LA90 Criterion
7 am-10 pm ≤ background LA90 + 5dB(A) 28 dB 35 + 5 = 40 dB(A)
10 pm-7 am ≤ background LA90 + 3dB(A) 27 dB 30 + 3 = 33 dB(A)
There is no fixed refrigeration equipment associated with the proposal at this
stage.
Vehicle Noise (Car Parks and Driveways)
Vehicle noise is generally described in two components for driveways and
carparks. The first is from the vehicles being driven to / from carparks, and the
second is from engine starts and car door closures. The latter generally produces
higher short-duration LAMax noise events. The former tends to be relatively low in
sound level, but can be of significantly greater duration, thereby influencing the
overall LAeq sound level.
Use of the carpark is expected to be generally limited to between 8:00 am and
8:00 pm due to the nature of the accommodation on offer and subsequent low
private vehicle usage1, therefore only the daytime and evening criteria are
applicable.
Noise from vehicles on the driveway was modelled as a moving point source,
assuming 10 vehicles in a 1-hour period and using a sound power spectrum for
light diesel engines at low speeds2, shown in Table 7.
Table 7: Light Diesel Sound Power Spectrum
1/1 Octave Band Centre Frequency (Hz)
63 125 250 500 1000 2000 4000 8000
LwA 65 67 74 82 80 78 77 66
Noise from car door closures and engine starts is not expected to produce noise
at the adjoining residence due to the carpark being in a basement and therefore
enclosed.
The noise levels expected from vehicle noise at the nearest residence are shown
in Table 8.
Table 8: Predicted Vehicle Noise Levels
Receiver LAeq(1 hour), dB LAmax, dB
12 Mary Street 41 64
The predicted noise impact levels indicate that:
• The LAeq(1 hour) will achieve the external noise criteria for the daytime and
internal noise criterion for the daytime and evening periods when allowing
for a 7 dB(A) reduction (free-field) through open windows.
• The LAMax (as proxy for the LA1(1 hour)) noise levels will achieve the external
noise criterion for the daytime and evening. The internal LA1 may be
exceeded, however this should be considered in the context of the
residence with respect to existing road traffic noise exposure.
1 Boune Plan of Management
2 Emanuel Hammer, Sebastian Egger, Tina Saurer and Erik Bühlmann, 23rd International
Congress on Sound and Vibration (July 2016) “Traffic Noise Modelling at Lower Speeds”
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Guest Noise
A “worst case” scenario for guest noise was calculated assuming guests
congregated in 3 groups of 5 in the pool / relaxation area. The sound power levels
for the LAeq and statistical noise indices was estimated using the formulae
developed by Hayne et al3 for small to medium crowds.
Due to the nature of the area and potential distribution of people within it, sound
levels at the nearest receivers were calculated by assuming an even distribution
of the total sound power around the perimeter of the area, and that sound through
the apertures between buildings would be dominant over any that may go over the
buildings. Noise levels were then calculated assuming each aperture acted as a
point source.
The predicted noise levels from guests in the pool / relaxation area are shown in
Table 9.
Table 9: Predicted guest noise levels for 30 people in the courtyard
Receiver LAeq(1 hour), dB LA10(1 hour), dB LA1(1 hour), dB
12 Mary Street 35 38 41
4 Ann Street 35 38 41
6 Ann Street 34 37 40
8 Ann Street 33 36 39
10 Anne Street 35 38 41
The predicted noise levels from guests achieve the Acoustic Quality Objectives
and Background Creep criteria during all time periods.
6 Discussion of Results and Attenuation
Air Conditioners
There is no air-conditioning plant designated for the site at this stage. The
measured background noise levels and established criteria for air-conditioning
plant provide criteria for any potential future installations.
Refrigeration Plant
There is no fixed refrigeration plant at the venue. The measured background noise
levels provide criteria for any potential future installations.
Vehicle Noise
Vehicle noise produced on the driveway is not expected to cause a noise nuisance
during the late evening or night time due to the negligible expected use of the
driveway.
Noise from the driveway is also considered unlikely to subjectively emerge from
the ambient existing road traffic noise from Mary Street during the daytime and
evening.
Guest Noise
Guest noise from the pool / relaxation area will achieve all Acoustic Quality
Objectives and Background Creep criteria.
3 Prediction of Noise from Small to Medium Sized Crowds M.J. Hayne (1), J.C. Taylor (1),
R.H. Rumble (1) and D.J. Mee (2) Proceedings of ACOUSTICS 2011
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7 Conclusion and Summary of Recommendations
RoadPro Acoustics was engaged by RG Strategic to assess potential noise
emissions from a proposed accommodation facility at 14-16 Mary Street,
Noosaville.
Noise criteria for mechanical plant have been established, and these should be
referred to during the detailed design stage of the project to ensure external
condenser units are appropriately sited and/or treated.
Vehicle noise from the driveway is not expected to cause a noise nuisance due to
limited hours of usage, and existing exposure to road traffic noise at the nearest
residence.
Guest noise from the pool / relaxation area is not expected to cause a noise
nuisance.
It is the view of RoadPro Acoustics that with inclusion of the above
recommendations, the Site is suitable for the proposed use with respect to acoustic
amenity.
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Visitor Accommodation, Noosaville 1142R1-R0 Appendix A – Proposal Plans www.roadpro.net.au 21 March 2018
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Visitor Accommodation, Noosaville
1142R1-RO
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21 March 2018
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Visitor Accommodation, Noosaville 1142R1-RO i BOUNCE NOOSA a 16 MARY STREET aan NOOSAVILLE QLD 4566 VOUNCE € Fugiang Investments Pty Ltd Erawing Tithe BUILDING SECTIONS 18001 pala www. roadpro.net.au 21 March 2018
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Visitor Accommodation, Noosaville 1142R1-R0 Appendix B – Measured Ambient Noise Levels www.roadpro.net.au 21 March 2018
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Visitor Accommodation, Noosaville 1142R1-RO Ambient Noise Levels 14-16 Mary St, Noosavill (northern boundary) - Friday 26 January 2018 80 . \ N A . \\ is MA 4 IN OE I io PW WW VY MS a “lyf ee ey % wlth A 35 30 25 0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00 Ambient Noise Levels 14-16 Mary St, Noosavill (northern boundary) - Saturday 27 January 2018 —l1 —L1i9 —L90 —L " h ( . hy “lA : Nia rh AN if 30 www.roadpro.net.au 21 March 2018
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Visitor Accommodation, Noosaville 1142R1-RO Ambient Noise Levels 14-16 Mary St, Noosavill (northern boundary) - Sunday 28 January 2018 2 _—, Pa ann cf ‘ \ ~=4 — C Ambient Noise Levels —l1 —110 —190 —Ler 14-16 Mary St, Noosavill (northern boundary) - Monday 29 January 2018 iN I\ | i it L\ A \a hy | | A Ica | A OL WAKA PN N | aA Ng eS "2g NT b\w Nee i \ www. roadpro.net.au 21 March 2018
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Visitor Accommodation, Noosaville 1142R1-RO 80 Ambient Noise Levels 14-16 Mary St, Noosavill (northern boundary) - Thursday 1 February 2018 —1 —110 —190 —=Leq 75 70 65 60 55 50 Sound Level (dBA) 45 35 30 25 0:00 2:00 6:00 8:00 10:00 12:00 Time of Day 14:00 16:00 18:00 20:00 22:00 0:00 80 Ambient Noise Levels 14-16 Mary St, Noosaville (eastern boundary) - Wednesday 24 January 2018 ——l1 ——110 ——190 —Leq 75 70 65 60 55 50 Sound Level (dBA) 45 35 30 25 0:00 2:00 4:00 6:00 8:00 10:00 12:00 Time of Day 14:00 16:00 18:00 20:00 22:00 0:00 www. roadpro.net.au 21 March 2018
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Visitor Accommodation, Noosaville 1142R1-RO Ambient Noise Levels 14-16 Mary St, Noosaville (eastern boundary) - Thursday 25 January 2018 —u —110 —190 ——u \ | \ | \\W AA NLA NAN Al We | AW SAAS) Vaal Ambient Noise Levels 14-16 Mary St, Noosaville (eastern boundary) - Friday 26 January 2018 ——l1 —110 ——190 — te \ | A \ pA MW \ pth ed 7 \Aan. seals SW KAN Md \ MeN YW EVEN NI oA pee Vy aX ve AV NEW a www. roadpro.net.au 21 March 2018
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Ambient Noise Levels aville (eastern boundary) - Saturday 27 Janua ry 2018 14-16 Mary St, Noos: LAA oY ON —— SS IM \ _—— e 6» Ss ® fs ® &© » Gg 8 Gg we 2 FC FF 8 BB Bb 8B F< FF HH BR A Ambient Noise Levels ville (eastern boundary) - Sunday 28 Janua ry 2018 14-16 Mary St, Noosa | wr Sy WAN pw A e © oc ® sg: w»® @ 2 © 8 FS F&F Bb & 3. 8 8 8 &
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Ambient Noise Levels aville (eastern boundary) - Mo ry 2018 nday 29 Janua 14-16 Mary St, Noos WA nw WWI an JV") —SEE= OS \ A WAL \ | Vat \ aL e@ © 2c 8» 2 #® gg 8 ¢ 8% gg BF es sS RF 8 8B 8B 8B F FF HB BB A Qu Ambient Noise Levels ville (eastern boundary) - Tuesday 30 Janu ary 2018 14-16 Mary St, Noosa’ WA \ YY we — SS > > < ~ 3 ie i a = | ee = = | 7a aa ___ ~~ eo 6» cs » gs » 2 © 9g wv Gg Be ee CS 8§ 8 8B 8B B FF FF SB B A
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Visitor Accommodation, Noosaville 1142R1-RO Ambient Noise Levels 14-16 Mary St, Noosaville (eastern boundary) - Wednesday 31 January 2018 ——l1 —11i0 ——190 —Leq \ IN \\ y \\ A \ i) AW Na /\ NAMPA Ma NO MIENN es aR RZ | NN vd | nf) | VY WARN AI! W\n pw ee SS sound Level (dBA) a a a Time of Day Ambient Noise Levels 14-16 Mary St, Noosaville (eastern boundary) - Thursday 1 February 2018 — SSS www.roadpro.net.au 21 March 2018