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Acoustic Report · MCU15/0122
Attached to the e-mail MCU15/0122 Development Application- Acoustic report Email 4 of 5.
Proposed Medical Centre, Noosaville
Table 2 Logger Noise Measurement Results
Measured Ambient Sound Levels, dB
Day Evening Night
LA10 LA90 Ʌ LA10 LA90 Ʌ LA10 LA90 Ʌ
1-Sep-15 56 40 46 32 50 32
2-Sep-15 56 39 45 31 50 29
3-Sep-15 58 46 45 28 50 30
4-Sep-15 57 43 47 32 50 31
5-Sep-15 56 40 48 33 49 32
6-Sep-15 55 39 45 30 50 31
7-Sep-15 57 39 44 29 50 30
8-Sep-15 58 46
Average 55 39 44 29 49 29
Notes: Ʌ The LA90 is the lowest 10th percentile of the LA90(15-minute) measurements for the
respective time period.
Note that the daytime noise levels are dominated by road traffic noise from
Goodchap Street. Therefore, it is considered to be appropriate to reduce the LA90
measured during the day by 3 dB(A) for assessment purposes at residences on
the western side of Goodchap Street due to the further distance of these
residences from the noise source.
The daytime LA90 for assessment purposes for residences on the western side of
Goodchap Street is therefore: 39 dB(A) – 3 dB(A) = 36 dB(A).
4 Predicted Noise Levels and Attenuation
4.1 Vehicle Noise
4.1.1 Carpark Noise
Previous noise measurements carried out by RoadPro Acoustics of vehicles
driving in car parks have shown noise levels in the order of 60-65 dB(A) at a
distance of 10 m are produced.
The lower level carpark is enclosed, preventing noise emissions from impacting
on residences in Val Crescent. The wall material for the carpark will be minimum
Rw 25, and the roof material (where this function isn’t served by the soffit) will be
colourbond steel sheeting.
The nearest residence to the north of the site (on the opposite side of Goodchap
Street) will be approximately 20 m from the driveway ramp on that side of the
development. The resultant short-term noise levels from vehicles on the site would
be approximately 55-60 dB(A) without any additional noise attenuation. The
LAeq,1 hr will be lower than this level depending on how frequently vehicles use the
ramp, however it is uncertain by how much. A minimum 1 m high acoustic barrier
has been designed to run along the northern edge of the carpark and ramp,
accompanied by acoustically absorptive surface treatment on the inside of the
barrier and on the building wall adjacent to the driveway. This will ensure
effectiveness of the barrier by reducing noise reflections, as well as reducing the
noise that generally emanates from the site.
www.roadpro.net.au 5 November 2015 Page 5 of 8
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