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Response to Information Request 5-7 Rufous Street Peregian Beach - Attachment D MCU13/0092
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important and most demanding requirement. Research has determined that the maximum noise
level inside a bedroom or sleeping area due to short duration transient events should not exceed
4SdBA LAmax for nil sleep disturbances9. This value corresponds to the World Health Organization
(WHO)guideline internal LAmax noise level of 4SdBA for transient noise events in order to prevent
sleep disturbancelO.
By historical convention, the sleep criteria are applied only during the "normal"sleep period which
extends from lOpm to 7am.
To convert the criterion for sleep disturbance from a limit measured inside a bedroom to an
outdoor limit, adjustments between SdBA and lOdBA are suggested by various authorities to
account for fa ade attenuation provided by a normal, naturally-ventilated dwelling. This results in
an outdoor noise limit ranging from SOdBA to SSdBA (LAmax)’
Table 4: LAm.x Noise Criteria for car park noise emissions at residences
Transient Noise Criteria,
Time Period
LAm.x,.dj (dBA)
Day (7am to 6pm) 69
Evening (6pm to lOpm) 65
Night (lOpm to 7am) 50 to 55 (sleep disturbance)
It can be seen in Table 4 that the most stringent noise limits are during the night-time period.
7.2 Limits for service and delivery vehicle noise
Loading activities involving noise from vehicle refrigeration plant and engine idling can be
characterised as being intermittent or quasi-continuous in nature. However, activities such as
vehicle reversing (i.e. reverse beeping nOise), starting of vehicle engine, vehicle door slamming,
vehicle acceleration, dropping of boxes (stock) onto the floor, etc. can be characterised as being
transient in nature.
Therefore, the appropriate measurement parameters to quantify noise events associated with
loading activities would be LAmax (for transient noise events) and LAeq (for intermittent or quasi-
continuous noise events). The applicable noise limit for the LAmax noise descriptor would be those
presented in Table 4 derived for carparking.
The LAeq noise limits for the residences near the proposed shopping centre development site due
to refrigerated truck noise (i.e. from refrigeration plant on trucks loading / unloading at the site)
are determined based on the comparison of like parameters methodology (details regarding this
9
Bullen, R., Hede, A. & Williams, T. (1996),’Sleep Disturbance Due to Environmental Noise: A Proposed Assessment
Index’, Acoustics Australia, vol. 24(3), pp. 91-96. This paper was previously referenced in the Users Guide to
Queensland’s Environmental Protection (Noise)Policy 1997.
Berglund, B., Lindvall, T., Schwela, D. (1999)’World Health Organization: Guidelines for Community Noise’, pp. 44-
10
46.
@ Renzo Tonin Ron Rumble Proposed Shopping Centre, Rufous Street, Peregian
Noise Impact Assessment
Q9554-01F02 (Rev 3) Peregian Shopping Centre.doc Multi Span Australia Group Pty Ltd
5 August 2013 Page 13
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