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20211104OBA_R2_Information_Request_Response - Acoustic RF · MCU21/0146
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MATTHEW PALAVIDIS
VICTOR FATTORETTO
MATTHEW SHIELDS
20210208.3/0411A/R2/OB
23/09/2021
Stockwell Development Group Pty Ltd
399 Montague Road
WEST END QLD 4101
Attn: Fraser Stevenson
Noosa Residential Apartments, Hofmann Drive - Information Request Response
This letter has been drafted in response to Noosa Council Information Request (ref: MCU21/0146, dated 23
September 2021). Noosa Council comments are quoted below and are followed with the response by
Acoustic Logic Consultancy.
Noosa Council Comment
Issue
A review of the Acoustic Logic noise report dated 16 August 2021 has been undertaken. The Acoustic Logic
report does not provide adequate information to support the noise predictions prepared using noise modelling.
Further the report is confusing in the actual noise treatments necessary, with options provided for glazing – ie
if Noosa Civic Plant is acoustically treated or not. There are matters which require further clarification and on
this basis the following is requested:
Noosa Council Required Information
Item 13. Provide details on the inputs to the road to the road traffic noise modelling, including traffic flow rates,
vehicle speeds, commercial vehicle component.
Item 14. Provide validation of the traffic noise modelling to the measured road traffic noise levels.
Acoustic Logic Response
We have discussed traffic data with Noosa Council traffic specialists, and they have advised us that there is
limited information available for the existing collector roads as well as the extended Hoffmann drive. The
project traffic consultant TTM advised that the existing collector road traffic input information relies on the
current posted speeds as well as up to 5,000 vehicles per day. Based on this and considering heavy vehicle
percentage of 2%, the modelling has resulted in a noise level 1.95dB(A) higher than that measured by
Acoustic Logic. The traffic noise model is therefore considered to be conservative, however, given it falls
within the acceptable +/-2dB(A) validation range, we have not applied any corrections. Furthermore, to
obtain the 2031 predicted noise levels we are conservatively applying future traffic related noise increases
to the existing 2021 traffic scenario model.
BRISBANE ABN 98 145 324 714
Level 1 www.acousticlogic.com.au
82 Arthur Street
FORTITUDE VALLEY QLD 4006
(07) 3211 5591
The information in this document is the property of Acoustic Logic Pty Ltd 98 145 324 714 and shall be returned on demand. It is
issued on the condition that, except with our written permission, it must not be reproduced, copied or communicated to any other
party nor be used for any purpose other than that stated in particular enquiry, order or contract with which it is issued.
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In terms of future potential traffic flows we note that a traffic study by Cardno for Noosa Civic extension notes an overall peak hour increase of 42% which would result in 2,100 additional vehicles or 1.5dB(A) noise increase compared to current scenarios without considering natural traffic changes occurring. It is noted though, that the distribution of the traffic splits between surrounding roads. However, in the absence of exact data we have applied such increase to the Hoffmann Drive daily traffic rates well. In addition to the centre specific traffic increase, we note that the report indicates natural annual increase at adjacent road networks. Ernie Creek-Hoffmann Drive intersection is shown to have average annual peak hour movements decreasing, whereas the other access to Noosa Civic is predicted to have a 1.33% annual increase. Furthermore, the traffic report shows a 0.8% annual growth for Noosa population, and due to other intersection growths, adopts a 1.5% annual growth for all intersections. Based on this, our potential future traffic noise increase relies on a 1.5% annual AADT increase for Hoffmann Drive, in addition to the 42% increase due to the shopping centre, which would lead to an additional 803 vehicles in year 2031 compared to year 2021. Based on the above, our modelling of the future 2031 traffic scenario incorporated an additional 2,903 vehicles on Hoffmann Drive. This is a 60% increase compared to the 5,000 vpd used to validate the 2021 model. Such increase would result in a 1.7dB(A) additional increase in the noise levels of the validated 2021 noise model which itself predicted a 1.95dB(A) higher noise impact compared to the unattended noise monitoring values. Note, the recommendations in our previous assessment included a 3.0dB addition to the measured noise levels to obtain year 2031 noise impacts, whereas the method above predicts year 2031 to have a 3.7dB increase in noise impacts over the current measured levels. The acoustic report will be updated based on the above and shall include the additional 0.7dB increase in noise impacts. Subsequently, the acoustic treatment recommendations will be reviewed. Refer to Section 5.1 of the revised acoustic report (ref: 20210208.3/2309A/R4/JJM, dated 23 September 2021). Noosa Council Required Information Item 15. Provide tabulated noise results at residential unit facades for day/Evening and Night periods. Acoustic Logic Response The revised acoustic report presented tabulated road traffic façade noise impacts for the requested periods. Refer to Section 5.1 of the revised acoustic report. Noosa Council Required Information Item 16. Provide the required acoustic rating of façade elements to comply with road traffic noise for day/evening and night periods to comply with the Table 10 Noise Limits Acoustic Logic Response Relevant sections of the revised acoustic report presented façade construction recommendations, including acoustic ratings for glazing, walls, and roofs. Refer to Section 6 of the revised acoustic report. Noosa Council Required Information Item 17. Provide details on the inputs to the mechanical plant noise modelling including source sound power levels and operating times for all plant items considered. Acoustic Logic Response The revised acoustic report presented mechanical plant noise modelling assumptions. This includes sound power levels and operating times. Refer to Section 5.3 of the revised acoustic report. In addition to onsite mechanical plant noise, we have also reviewed the Noosa Civic plant noise impacts and provided recommendations to achieve compliance (Section 5.2). I:\Jobs\2021\20210208\20210208.3\20211104OBA_R2_Information_Request_Response.docx 2
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Noosa Council Required Information Item 18. Provide clarification of why there are no predictions provided for night time mechanical plant noise. Acoustic Logic Response Tabulated predicted day, evening, and night noise impacts from Noosa Civic operations have been presented in the revised acoustic report. The noise impacts predict compliance with Condition 5 and Condition 70 noise limits. Refer to Section 5.2 of the revised acoustic report. Noosa Council Required Information Item 19. Provide clarification as to whether the acoustic design proposed for residential units is reliant upon windows and doors to be closed at all times for internal noise criteria to be achieved. Item 20. Please advise whether mechanical ventilation/air conditioning is proposed to all noise affected units on the basis if external doors and windows have to be closed Acoustic Logic Response Where facades are required to be acoustically rated, the recommended façade treatments assume that all windows and doors are in closed position for the purposes of achieving compliance with relevant internal noise limits. Hence, mechanical ventilation/air-conditioning is required in all noise affected habitable rooms. This has been clarified with the specific affected apartments highlighted in Appendix C of the revised acoustic report Noosa Council Required Information 19. Provide clarification on whether acoustic mitigation works identified in Section 8 for the Shopping Centre will be implemented. Acoustic Logic Response Acoustic treatments identified in Section 8 for the Noosa Civic Shopping Centre shall be fully implemented as confirmed by the developer. Noise impacts from Noosa Civic to the residential development all take into consideration the acoustic treatments for the stationary plant. This has been further stated in Section 6 and Section 8 of the revised acoustic report. We trust this information is satisfactory. Please contact us should you have any further queries. Yours faithfully, Acoustic Logic Pty Ltd Omar Busaidi I:\Jobs\2021\20210208\20210208.3\20211104OBA_R2_Information_Request_Response.docx 3
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Appendix A – Revised Acoustic Report I:\Jobs\2021\20210208\20210208.3\20211104OBA_R2_Information_Request_Response.docx 4
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ACOUSTIC MATTHEW PALAVIDIS
LOG IC VICTOR FATTORETTO
MATTHEW SHIELDS
Noosa Residential Apartments, Hofmann Drive
Development Application
BRISBANE ABN 98 145 324 714
Level 1 www.acousticlogic.com.au
82 Arthur Street
FORTITUDE VALLEY QLD 4006
(07) 3211 5591
The information in this document is the property of Acoustic Logic Consultancy Pty Ltd ABN 11 068 954 343 and shall be returned
on demand. It is issued on the condition that, except with our written permission, it must not be reproduced, copied or
communicated to any other party nor be used for any purpose other than that stated in particular enquiry, order or contract with
which it is issued.
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Project ID 20210208.3
Document Title Development Application
Attention To Stockwell Development Group Pty Ltd
Revision Date Document Reference Prepared Checked By Approved
By By
0 24/02/2021 — 20210208.3/2402A/RO/JJM JJM OB
1 3/08/2021 — 20210208.3/0308A/R1/JJM JJM OB
2 11/08/2021 20210208.3/1108A/R2/JJM JJM OB
3 16/08/2021 — 20210208.3/1608A/R3/JJM JJM JJM
4 23/09/2021 — 20210208.3/2309A/R4/JJM OB TS
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TABLE OF CONTENTS
1. INTRODUCTION
2 SITE DESCRIPTION
2.1 SITE LOCATION ....
2.2 NOOSA PLAN 2020 ZONING..
3 EXISTING ACOUSTIC ENVIRONMENT...
3.1 NOISE MONITORING...................0+
3.1.1 Unattended Measurements Results
3.2 MECHANICAL PLANT AND LOADING DOCK ACTIVIES
3.2.1 Attended Measurement Results.
3.3. ROAD TRAFFIC NOISE MONITORING.
4 ASSESSMENT CRITERIA
4.1 NOOSA PLAN 2020
4.1.1 Major Centre Code...
4.1.2 Dual Occupancy and Multiple Dwelling Code..
4.2 | ENVIRONMENTAL PROTECTION ACT 1994
4.3. ENVIRONMENTAL PROTECTION (NOISE) POLICY 2019.
4.3.1 Acoustic Quality Objectives...
4.4 AS2107:2016..
4.5 NOOSA CIVIC NOISE EMISSION LIMITS ....
4.5.1 Judgement No. 765 of 2020 (3 September 2020)
45.2 Condition 70...
4.6 ADOPTED NOISE LIMITS..
5 NOISE IMPACTS AND EMISSIONS
5.1 ROAD TRAFFIC NOISE ASSESSMENT...
5.1.1 Road Traffic Model Calibration (Year 2021)..
5.1.2 Traffic Numbers — Year 2031
5.1.3 Road Traffic Noise Model Year 2031
5.1.4 Road Traffic Noise Contours
5.1.5 Facade Road Traffic Noise Impacts..
5.2 NOOSA CIVIC SHOPPPING CENTRE.....
5.2.1 Mechanical Plant Noise...
5.2.2 Loading Dock Activities
5.2.3 Compactor...
5.2.4 Compliance with Noosa Civic Noise Targets
5.3. ONSITE ACTIVITIES.
5.3.1 General Onsite Activities...
5.3.2 Preliminary Onsite Mechanical Plant Noise
6 RECOMMENDATIONS - BUILDING SHELL AND EXTERNAL GLAZING...
6.1 GLAZING
6.2 ROOF / CEILING CONSTRUCTION ....
6.3. EXTERNAL WALLS
6.4 ACOUSTIC SEALING OF WINDOW FRAMES
6.5 MECHANICAL VENTILATION
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1 INTRODUCTION
Acoustic Logic has been engaged by Stockwell Development Group Pty Ltd to conduct a noise impact
assessment for the proposed residential development to be located at Hoffman Drive, Noosaville.
The site is impacted by road traffic noise from the local road network. Facade acoustic design requirements
mitigate road traffic noise whilst also considering noise impact from Noosa Civic Shopping Centre Northeast
of the development.
This report has been updated to address items raised in Noosa Council Information Request (ref:
MCU21/0146, dated 23 September 2021). General recommendations for mechanical plant and other major
noise sources associated with the development have also been provided.
2 _ SITE DESCRIPTION
The site of the proposed development is situated amongst undeveloped bushland adjacent to Noosa Civic
Centre.
2.1 SITE LOCATION
The properties in the vicinity of the development are the following:
e Northeast: Noosa Civic Shopping Centre (Commercial/Retail)
e West: Commercial/Retail developments along Rene Street.
e Southwest: A residential complex located at 60 Hofmann Drive, Noosaville; consisting of five
standalone residential buildings.
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La Proposed Site Residential
La Commercial/Retail
Figure 1 — Site Location and Nearest Noise Sensitive Receptors
2.2 NOOSA PLAN 2020 ZONING
Secon |
Geushowoomieuccinc
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The subject site is in a Major Centre Zone with the surrounding properties within the following Noosa
Plan 2020 zones:
¢ Land strip bounding the site to the north, northeast, and east — Environmental Management
and Conservation Zone.
« Noosa Civic Shopping Centre (northeast) — Major Centre Zone.
« 36-40 Hofmann Drive (northwest) — Major Centre Zone.
¢ 81 and 85 Hofmann Drive (west) Low Impact Industry Zone and Environmental Management
and Conservation Zone.
e Residential Complex at 60 Hofmann Drive (southwest) - High Density Residential.
3 EXISTING ACOUSTIC ENVIRONMENT
The existing background conditions include Road traffic noise from Hofmann drive, mechanical
plant/loading dock bay from Noosa Civic Centre, and environmental noise from surrounding undeveloped
bushland.
3.1 NOISE MONITORING
Environmental noise monitoring was conducted on two occasions to capture road traffic and mechanical
plant/loading bay impact from Noosa Civic Centre. The monitoring results can be seen in the table below
with corresponding map of monitoring locations as seen below. In addition attended measurements were
conducted in Noosa Civic and on Hofmann Drive as illustrated on the map.
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Unattended
Attended
Figure 2 —- Noise Meas.:rement Locations
3.1.1. Unattended Measurements Results
Table 1 -NGARA Measurement Summary
Date Average Acoustic Descriptor, dB(A)
Leq Loo Lio Li
D* | EF N* | D* E* | N* D* | E* |N* | D* | EX | N*
20/11/19 59 48 | 48 57 45 | 42 60 |50 /50 | 61 | 53 | 53
21/11/19 57 52 50 55 50 | 45 59 |54 |51 [61 | 56 | 54
22/11/19 58 48 | 48 56 44 | 43 59 |50 |49 |61 | 53 | 53
23/11/19 58 52 | 48 56 46 | 43 59 |54 |49 |60 | 56 | 53
24/11/19 58 45 49 56 42 | 43 59 |46 |50 |60 | 48 | 54
25/11/19 59 49 50 57 45 | 46 60 |50 |/51 |62 | 53 | 54
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Date Average Acoustic Descriptor, dB(A)
Leq Loo Lio Li
D* E* N* D* E* N* D* E* N* | D* E* N*
26/11/19 59 48 48 57 46 | 44 60 |50 |50 | 62 52 54
27/11/19 59 57 61 63
AVERAGE 58 49 49 56 45 | 44 60 |50 | 50 | 61 53 | 54
* D- Day (7:00-18:00), E- Evening (18:00 — 22:00), N-Night (22:00-7:00)
Table 2 -Rion NL42 Measurement Summary
Date Average Acoustic Descriptor, dB(A)
Leq Loo Lio Li
D* E* N* D* E* N* D* | EF N* | D* | E* N*
20/11/19 54 48 44 51 46 37 56 50 | 46 66 56 59
21/11/19 52 49 44 49 46 36 53 50 | 46 66 59 61
22/11/19 52 49 44 49 46 36 53 50 | 45 66 60 61
23/11/19 52 48 44 49 46 35 54 |49 | 46 66 58 60
24/11/19 53 48 43 49 45 36 56 50 | 45 67 58 61
25/11/19 52 49 43 49 46 37 54 51 45 66 61 61
26/11/19 57 51 44 52 47 37 59 54 | 46 70 59 60
27/11/19 54 51 56 67
AVERAGE 53 49 44 50 46 36 55 51 46 |67 | 59 | 60
* D- Day (7:00-18:00), E- Evening (18:00 — 22:00), N-Night (22:00-7:00)
3.2 MECHANICAL PLANT AND LOADING DOCK ACTIVIES
Additional measurements were used to determine impacts to the proposed development from road traffic
noise on Hofmann drive, and Noosa Civic mechanical plant noise and standard loading bay activities.
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3.2.1. Attended Measurement Results
Table 3 -Loading Dock Activity, Attended Measurements
Noise Source Acoustic Descriptor, dB(A)
Leg Lax Lpeak
Mechanical plant @ 25 metres 57 62 78
Reversing signal from trolley collection truck 69 76 83
Mechanical plant noise through exhaust/grille @ | 71 73 85
1 metre away
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Table 4 - Mechanical Plant, Attended Measurements
Location’ Height Noise Source Distance from Acoustic Descriptor, dB(A)
Noise Source L L
Leq 10 90
1 1.2 metres | Mechanical Plant Deck 1m 72 74 71
above roof
2 1.2 metres | Exhaust Fan Im 81 81 80
above roof
3 1.2 metres | Plant Room 1m 84 84 83
above roof
4 1.2 metres | Mechanical Plant Deck 1m 69 69 68
above roof
5 1.2 metres | Mechanical Plant Deck 1m 71 72 70
above roof
6 1.2 metres | Mechanical Plant Deck Im 72 72 71
above roof
7 1.2. metres | Rear Exhaust Fan Im 81 82 79
above roof
8 1.2 metres | Mechanical Plant Decks, 55m 54 54 52
above
ground Rear Exhaust Fan
9 1.2. metres | Mechanical Plant Deck 1m 75 76 73
above roof
10 1.2 metres | Mechanical Plant Deck 5m 57 59 55
above roof
11 1.2 metres | Plant Room, 58m 56 57 55
above roof
Front Exhaust Fan
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3.3 ROAD TRAFFIC NOISE MONITORING
Additional road traffic monitoring was conducted between 2 March and 9 March 2021. The logger location
was chosen to measure road traffic noise level from Hoffman drive. The measured noise levels are presented
in Table 5 below.
Table 5 -Unattended Road Traffic Noise Monitoring - 2021
Date Average Acoustic Descriptor, dB(A)
Leq Loo Lio
pt | EF n* |p* | E* nx |p* [|e |N* | 18Hr
2/3/2021 59 |51 |40 |49 |42 |37 |e2 [52 | 40 | |
3/3/2021 60 |51 [46 [51 |4a [a1 [63 |52 |47 [59
4/3/2021 61 |53 [47 [50 |44 |42 [65 |s56 |48 [60
5/3/2021 59 50 45 48 42 40 62 52 45 57
6/3/2021 56 |51 [45 |46 |43 |39 |eo |52 | 44
7/3/2021 54 |48 [44 [aa [43 |38 [58 [49 | 4a
8/3/2021 59 |51 |46 |50 |43 |40 |e2 [51 |46 |57
9/3/2021 58 “8 |
AVERAGE 58 (51 [45 [48 /|43 |39 {oz [52 |45 |59
* D- Day (7:00-18:00), E- Evening (18:00 — 22:00), N-Night (22:00-7:00),
Road traffic noise measurements were also conducted during the monitoring period at different locations
on Hoffman drive. Refer to figure below presents the measurement locations.
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Location 1
Figure 3 — Noise Measurement Locations — 2021
Refer to Table 6 for attended road traffic noise monitoring results.
Table 6 -Attended Road Traffic Noise Monitoring - 2021
Location Acoustic Descriptor, dB(A)
Leq Lio Loo
1 68 71 54
2* 51 52 48
3 62 65 53
*No road traffic recorded due to road closure/construction; results indicate background noise
conditions at site.
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4 ASSESSMENT CRITERIA
4.1 NOOSA PLAN 2020
The Major Centre Code applies to the proposed residential development. The Performance and Acceptable
Outcomes of the code relating to noise are presented in Table 7.
4.1.1 Major Centre Code
Table 7 - Major Centre Code Criteria for Assessment
Performance Outcomes Acceptable Outcomes
Building Design and Streetscape
Mechanical plant, equipment and AO31.1
storage
Mechanical plant, equipment and storage areas, including
PO31 vents and exhausts, are not visible from any street or
public space.
Mechanical plant and equipment (including
air conditioning equipment) and storage
areas are designed and located to:
AO31.2
a) avoid adverse visual impacts when
viewed from the street and | Mechanical plant, equipment and storage areas are:
adjoining properties; and
a) located more than 2 metres from any property
b) visually integrate with the building boundary;
design.
b) where located at ground level, screened by
fencing 1.5 metres in height or dense vegetation
of at least 1.5 metres in width incorporating
grouped trees and shrubs with a maximum
separation distance of 1 metre measured from the
centre of the tree or shrub;
c) re visually integrated into the line and plane of the
building and roof design and do not project
beyond the height or width of the building when
viewed from the street and adjoining properties;
d) fully enclosed or screened where above ground
level such that they are not visible from the street
frontages nor adjoining premises; and
e) are acoustically screened from any adjoining
sensitive land use.
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Performance Outcomes
Acceptable Outcomes
Mixed use development
PO36
Where residential development is proposed
it is provided for in mixed use buildings with
small dwellings, where such activities are
ancillary to and support the predominant
business functions of the zone
A036
Development provides for one or more of the following
residential activities, in the form of small dwellings only
and accommodated in a mixed-use building format:
a) one caretaker's accommodation unit;
b) dwelling unit (e.g. shop top housing);
c) dual occupancies;
d) multiple dwellings.
PO39
Mixed-use buildings are designed and
operated to ensure:
a) business uses manage potential
impact on residents, including
impacts associated with:
i) visual and acoustic privacy;
ii) safety and security; and
iii) lighting.
b) residential uses do not limit the
business opportunities of the site.
PO39.1
Dwellings are designed to incorporate suitable noise
attenuation and privacy measures to reduce amenity
impacts from business uses.
AO39.2
The residential component of the development provides
for:
a) separate identifiable residential entries from
entrances for other building uses;
b) clearly defined and safe pedestrian access to
dwelling units and accommodation units that are
appropriately lit, visible to others and directly
accessible to units from areas likely to be used at
night; and
c) security measures such that building users do not
have access to areas that are intended for the
exclusive use or residents of, and visitors to,
residential accommodation;
d) windows, balconies, terraces of each dwelling are
screened up to a minimum height of 1.7 metres
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Performance Outcomes
Acceptable Outcomes
from the finished floor level where overlooking a
habitable room or private open space of another
dwelling within 9 metres; and
e) screening may incorporate solid translucent
screens, shutters, perforated panels or trellises
which have a maximum of 50% openings.
AO39.2
Dwellings provide:
a) clearly identify private residential space by using
features such as low walls, changes in surface
texture or other landscape treatments; and
b) private open space or an open balcony directly
accessible from a habitable room with:
i) a minimum area of 9m?,
ii) a minimum dimension of 2.5 metres; and
iii) is clear of any utilities such as gas, water
tanks and air conditioning units.
Safety and Amenity
Vehicle loading and waste
PO50
Vehicle loading / unloading and waste
storage and collection areas do not
significantly impact on the visual or acoustic
amenity of the area or sensitive land uses.
AO50
Vehicle loading/unloading, waste storage/collection and
external storage areas are enclosed within a service yard
or courtyard and located to the rear or under the building
and not located along any frontage to a public street or
space.
High Density Residential Precinct
PO79
AOQ79.1
facilities
swimming pools, spas and sports courts are:
Communal outdoor recreational including
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Performance Outcomes
Acceptable Outcomes
Development, including mechanical plant,
vehicle manoeuvring and
outdoor recreation uses:
communal
a)
setback at least 12 metres from the boundary of
land in a residential zone and screened by a 5
metre wide buffer densely planted with trees and
a) donot have an adverse effect on the
amenity enjoyed by users of
adjacent or nearby premises
through emission of noise, light,
fumes or smoke;
b) do not
disturbance to local fauna through
light or smoke emissions.
cause unreasonable
shrubs including species from 1 metre to 8 metres
in height; or
b) located internally to the arrangement of buildings
on the site; and
c) not used between the hours of 9:00pm and
6:30am the following day
AO79.3
Mechanical plant is:
a) located at least 2 metres from side or rear
property boundary;
b) where located at ground level, screened by
fencing 1.5 metres in height or dense vegetation
of at least 1.5 metres in width incorporating
grouped trees and = shrubs
separation distance of 1 metre measured from the
centre of the plant;
with maximum
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.
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4.1.2
The Dual Occupancy and Multiple Dwelling Code applies to the proposed residential development. The
Dual Occupancy and Multiple Dwelling Code
Performance and Acceptable Outcomes of the code relating to noise are presented in Table 8.
Table 8 - Dual Occupancy and Multiple Dwelling Code Criteria for Assessment
Performance Outcomes
Acceptable Outcomes
Safety and Amenity
POS
Development is designed to minimise noise
carrying between dwelling units or
accommodation units by locating noise
sensitive spaces such as bedrooms away
from noise generating areas of the
development, such as car parking areas or
mechanical plant and equipment or
recreational facilities.
AOS
Bedroom windows are at least 3 metres away from
shared driveways, car parking areas, mechanical plant,
refuse and recycling areas, vents and exhausts.
PO6
Where dwellings form part of a mixed use
development, the development provides
residents with reasonable privacy and
security.
AO6.1
Clearly identifiable entry areas for the residents of, and
visitors to, multiple dwellings are provided separately
from entrances for other site users and provide for safe
entry from streets, car parking areas and servicing areas.
AO6.2
Clearly marked, safe and secure parking areas are
provided for residents and visitors which are separate
from parking areas provided for other site users.
AO6.3
Security measures are installed such that site users do
not have access to areas that are intended for the
exclusive use of residents of, and visitors to, dwellings.
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Performance Outcomes
Acceptable Outcomes
AO6.4
Dwellings are designed to incorporate suitable noise
attenuation and privacy measures to reduce amenity
impacts from business uses.
AO6.5
Windows, balconies and terraces of each dwelling are
screened where overlooking a habitable room or private
open space of another dwelling within 9 metres.
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4.2 ENVIRONMENTAL PROTECTION ACT 1994
The following relevant noise limits would apply:
A4OT Pumps:
e« Between 10pm-7am: no audible noise
e Between 7am and 7pm: 5dB(A) above background level;
e Between 7pm and 10pm: 3dB(A) above background level.
440U Air-conditioning equipment:
¢ Between 10pm and 7am: 3dB(A) above background level;
e¢ From 7am to 10pm: 5dB(A) above background level.
440V Refrigeration Equipment
e Between 10pm and 7am: 3dB(A) above background level;
¢ From 7am to 10pm: 5dB(A) above background level.
4.3. ENVIRONMENTAL PROTECTION (NOISE) POLICY 2019
4.3.1 Acoustic Quality Objectives
The Queensland Environmental Protection (noise) Policy 2019 specifies indoor and outdoor acoustic quality
objectives for residences and are presented in Table 9 below.
Table 9 - Environmental Protection (noise) Policy 2019 Acoustic Quality Objectives
Acoustic quality objectives (measured at
Sensitive Time of day the receptor) dB(A) Environmental
Receptor value
LAegq, adj, Thr LAio, adj, 1hr LA, adj, 1hr
Residence (for Daytime and 50 55 65 Health and
outdoors) evening wellbeing
Daytime and 35 40 45 Health and
evening wellbeing
Residence (for Health and
indoors) ing, i
Night-time 30 35 40 wellbeing, in
relation to the
ability to sleep
4.4 AS2107:2016
Australian and New Zealand Standard AS/NZS 2107:2016 ‘Recommended design sound levels and
reverberation times for building interiors’ (later referenced as AS2107) lists recommended indoor noise levels
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based on the space use. Given that the applicable Noosa Shire planning codes do not list the indoor noise
targets for the residential development itself, we have adopted the following design targets:
e Living Areas: 30-40 dBA Leqt
¢ Sleeping areas (night time) 30-35 dBALegt.
4.5 NOOSA CIVIC NOISE EMISSION LIMITS
Noise emanating from Noosa Civic Shopping Centre and impacting the proposed residential development
is subject to a judgement by the Planning and Environment Court Judgement No. 765 of 2020, dated 3
September 2020). In addition, condition 70 of the original DA approval for Noosa Civic contained noise limits
relating to air-conditioning noise. The limits are indicated for information as compliance with the limits are
the responsibility of the Noosa Civic Shopping Centre.
4.5.1 Judgement No. 765 of 2020 (3 September 2020)
5. Prepare and submit to Council of approval with an Operational Works application a revised acoustic
report which includes measures to mitigate noise generate from the shopping centre operations and
equipment, including deliveries, truck movements and rubbish collection. This report should consider
attenuation at the noise source as well as a noise barrier along the shared boundary of Lots 19 and
21. All measures to mitigate noise must be implemented prior the submission of the subdivision plan
to Council.
¢ Noise attenuation is required to achieve the following acoustic quality for potential residential uses
of Lots 17-19. The measurement location must include receivers being placed at the closest point to
the future residential and office buildings.
Criteria (measured at the receptor) dB(A)
Sensitive receptor Time of Day LAeq,adj, Thr! LAl adj Th?
Daytime and evening
(habitable spaces) 35 45
Dwelling (indoors)
Night-time (sleeping 30 40
areas)
‘Acoustic descriptor/noise target for continuous noise sources (eg. Mechanical plant).
Acoustic descriptor/noise target for transient impacts arising from loading dock activities (e.g. truck
movements, reversing alarms, compactor, trolley etc.)
4.5.2 Condition 70
The original DA for the shopping centre included condition 70 below regarding air-conditioning equipment.
70. An occupier of premises where there is air-conditioning equipment must not use or allow the use of the
equipment —
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a) before 7am or after 10pm on any day if it maker noise or causes noise to be made of more than the higher
of the following —
0) 40 dB(A);
ii) 3 dB(A) above the background noise level
b) from 7am to 7pm on any day if it maker noise or causes noise to be made of more than the lower of either
of the following:
i) 50 dB(A)
ii) 5 dB(A) above the background noise level
©) from 7pm to 10pm on any day if it makes noise or causes noise to be made of more than 3 db(A) above the
background noise level.
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4.6 ADOPTED NOISE LIMITS
Based on the relevant applicable criteria for the Noosa Residential Apartments, Hofmann Drive reviewed in
previous sections, the summary of proposed noise criteria related to the site is listed below in Table 10.
Table 10 - Noise Objectives
Noise Source
Receiver
Noise Objective
Surrounding
Onsite Residential
EPP 2019 - Shopping Centre Activities (based on Judgement
No.765)'
- Day and Evening (7am — 10pm): habitable spaces < 35 dB(A)
Laeq.adj,thr
- Night (10pm — 7am): sleeping areas < 30 dB(A) Laeqadj,thr
Noise
AS2107:2016 — Road Traffic Noise
- Day and Evening (7am — 10pm): habitable spaces < 40 dB(A)
Laeq,adj,15hr
- Night (10pm - 7am): sleeping areas < 35 dB(A) Laegadj ahr
Mechanical Plant - Background Creep (L90+0 dB(A))
- Day and Evening (7am — 6pm): < 48 dB(A)Lso + 0
New Surrounding - Evening (6pm — 10pm): < 43 dB(A) Leo + 0
Development Sensitive - Night (10pm —- 7am): < 39 dB(A) Loo + 0
Receivers
Traffic Generation — Acoustic Quality Objectives
- Day and Evening: 50dB(A)Leg,agj.thr
- Night: 45dB(A)Legadj,thr
Noosa Civic air-
conditioning
plant
Onsite Residential
Condition 70 of Noosa Civic’
- Day and Evening (7am — 7pm): < 50 dB(A) Laeqadj,12hr
- Evening (7pm - 10pm): < 48 dB(A) Laeqadj3hr
- Night (10pm — 7am): < 40 dB(A) Lacqadjshr
Note 1: as previously requested by the Council, compliance with the noise limit is the responsibility of the
shopping centre and no facade upgrades are therefore considered, i.e. standard construction provisions
apply to address the shopping centre noise.
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5 NOISE IMPACTS AND EMISSIONS
The proposed development is impacted by the following noise sources:
¢ Road traffic noise from Hofmann Drive.
¢ Mechanical plant noise from Noosa Civic Shopping Centre.
e Truck activities from Noosa Civic Shopping Centre loading dock.
5.1 ROAD TRAFFIC NOISE ASSESSMENT
5.1.1. Road Traffic Model Calibration (Year 2021)
Noosa Council traffic specialists have advised that there is limited information available for the existing
collector roads as well as the future Hoffman Drive extension. We note the following regarding the
calibration of 2021 road model:
e = The traffic consultant for the project (TTM Consulting) have advised ALC that the existing collector
road traffic information input relies on the currently posted speeds as well as up to 5,000 vehicles
per day (AADT). Our model calibration at the long term traffic noise monitoring location is based
on this information and heavy vehicle percentage of 2%;
e Posted speed limit of 50 km/h has been used in the road traffic noise model calculations.
The SoundPLAN model was calibrated based on the above numbers and the unattended road traffic noise
monitoring. The road traffic model calibration numbers are presented in Table 11.
Table 11 - Road traffic noise modelling calibration - Year 2021
Noise Level Lio, ish, dB(A)
Road Correction’
Measured Model Difference
Hoffman Drive 58.6 60.5 1.95 0
Note No correction was added to the model as the difference is within the acceptable 2dB(A) difference
validation range
Based on the above, we note that the traffic noise model is conservative when compared against the
measured value.
5.1.2 Traffic Numbers — Year 2031
The future (year 2031) traffic numbers have been based on Noosa Civic Expansion Traffic Impact Assessment
prepared by Cardno which noted an overall peak hour increase of 42% for Noosa Civic extension which
could result in 2,100 addition vehicles and a subsequent 1.5dB(A) noise increase compared to the 2021
model. Note, the distribution of traffic splits between surrounding roads. However, in the absence of exact
data we have applied such increase to the Hofmann Drive daily traffic rates as well.
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Furthermore, the Cardno Traffic Report presented a 0.8% annual growth for Noosa population, and due to
other intersection growths adopted a 1.5% annual growth for all intersection. Based on this, the future traffic
noise assessment (year 2031) increase relies on the following:
¢ A1.5% annual AADT increase for Hofmann Drive.
e An additional 42% increase due to the Noosa Civic expansion.
The numbers used in the assessment (year 2031) are provided in Table 12.
Table 12 - Hofmann Drive Traffic Volumes
Hofmann Drive
Road AADT Annual Increase Due to Predicted‘ | % Heavy
Speed Limit 2021 Growth* Noosa Civic AADT Vehicles
Expansion Compared 2031
to Year 2021°
50 km/h 5,000 1.5% 42% 7,903 2.0%
e Note“ Resulting in predicted addition of 803 vehicles in 2031 when compared to year 2021.
* Note®) This increase leads to additional 2,100 vehicles, or 1.5dB(A) noise increase.
e Note With the annual growth and extension increases combined, total additional 2,903 vehicles in
year 2031 is predicted compared to year 2021. This results in overall 60% traffic increase compared
to the 2021 traffic numbers used in acoustic modelling. Such increase would result in 1.7dB(A) noise
increase.
Based on the above information, 1.95dB(A) conservative year 2021 calibration model + 1.7dB(A) traffic flow
increase related noise change predicted for year 2031 would lead to 3.65dB(A) higher value in year 2031
than that monitored in year 2021.
5.1.3. Road Traffic Noise Model Year 2031
The SoundPLAN™ future road traffic noise model was based on CORTN modelling compared against the
measured noise levels presented in Table 5 and using the traffic volumes in Table 12. The results are
presented in Table 13.
Table 13 - Road traffic noise modelling calibration - Year 2031
Noise Level Lio, ishr dB(A)
Road Correction
Measured (2021) Model (2021) Model (2031)
Hoffman Drive 58.6 60.5 62.2 0
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5.1.4 Road Traffic Noise Contours
Road traffic noise was modelled using SoundPLAN™; the 2031 grid noise maps are presented in Figure 4 to
Figure 6.
Noosa Residential
Predicted Road Traffic
Noise Levels (Year 2031}
Level 1
Prepared by: 08
bate: 10/2021
Noise Level
Lyo 4enr
indo
# ACOUSTIC
LOGIC
Figure 4 - Predicted 2031 Road Traffic Noise Levels (Day L.
eq 11hr) — Level 1
Noosa Residential
Predicted Road Traffic
Noise Levels (Year 2031}
Level 2
Prepared by: 08
bate: 10/2021
Noise Level
Lio ash
nas)
J ACOUSTIC
# LOGIC
Figure 5 — Predicted 2031 Road Traffic Noise Levels (Day Leg 11nr) — Level 2
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Noosa Residential
Predicted Road Traffic
Noise Levels (Year 2031}
Level 3
Prepared by: 08
bate: 10/2021
Noise Level
Lyo ashe
ind)
J ACOUSTIC
' LOGIC
Figure 6 — Predicted 2031 Road Traffic Noise Levels (Day Leg 11nr) —- Level 3
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5.1.5 Fagade Road Traffic Noise Impacts
Tabulated road traffic noise impacts predicted at the residential unit facades are presented in Table 14.
Refer to Appendix B for unit numbering.
Table 14 - Road Traffic Fagade Noise Impacts — 2031
Building | Unit | Room | Floor L10(18h) Leq,Day | Leq.Evening Leg, Night
dB(A) dB(A) dB(A) dB(A)
A 1 bed 1 Level 1 46 45 38 32
A 1 bed 2 Level 1 57 56 49 43
A 1 living Level 1 37 36 29 23
A 2 bed1 | Level1 46 45 38 32
A 2 living Level 1 37 36 29 23
A 3 bed 1 Level 1 39 38 31 25
A 3 living Level 1 38 37 30 24
A 4 bed 1 Level 1 45 44 37 31
A 4 bed2 | Level1 37 36 29 23
A 4 living Level 1 37 36 29 23
A 5 bed 1 Level 1 45 44 37 31
A 5 living Level 1 37 36 29 23
A 6 bed 1 Level 1 38 37 30 24
A 6 bed 2 Level 1 45 44 37 31
A 6 bed3 | Level1 52 51 44 38
A 6 living Level 1 40 39 32 26
A 7 bed 1 Level 1 63 62 55 49
A 7 living Level 1 58 57 50 44
A 8 bed 1 Level 1 63 62 55 49
A 8 living Level 1 59 58 51 45
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Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
A 9 bed 1 Level 1 63 62 55 49
A 9 living Level 1 61 60 53 47
A 10 bed 1 Level 1 62 61 54 48
A 10 living Level 1 61 60 53 47
A 11 bed 1 Level 1 62 61 54 48
A 11 living Level 1 61 60 53 47
A 12 bed 1 Level 1 63 62 55 49
A 12 bed 2 Level 1 56 55 48 42
A 12 living Level 1 61 60 53 47
A 1 bed 1 Level 2 48 47 40 34
A 1 bed 2 Level 2 59 58 51 45
A 1 living Level 2 40 39 32 26
A 2 bed 1 Level 2 48 47 40 34
A 2 living Level 2 40 39 32 26
A 3 bed 1 Level 2 42 41 34 28
A 3 living Level 2 41 40 33 27
A 4 bed 1 Level 2 47 46 39 33
A 4 bed 2 Level 2 39 38 31 25
A 4 living Level 2 40 39 32 26
A 5 bed1 | Level 2 47 46 39 33
A 5 living Level 2 40 39 32 26
A 6 bed 1 Level 2 41 40 33 27
A 6 bed 2 Level 2 47 46 39 33
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Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
A 6 bed 3 Level 2 54 53 46 40
A 6 living Level 2 42 41 34 28
A 7 bed 1 Level 2 65 64 57 51
A 7 living Level 2 60 59 52 46
A 8 bed 1 Level 2 64 63 56 50
A 8 living Level 2 60 59 52 46
A 9 bed 1 Level 2 64 63 56 50
A 9 living Level 2 62 61 54 48
A 10 bed 1 Level 2 63 62 55 49
A 10 living Level 2 63 62 55 49
A 11 bed 1 Level 2 63 62 55 49
A 11 living Level 2 62 61 54 48
A 12 bed 1 Level 2 65 64 57 51
A 12 bed 2 Level 2 58 57 50 44
A 12 living Level 2 62 61 54 48
A 1 bed 1 Level 3 50 49 42 36
A 1 bed 2 Level 3 59 58 51 45
A 1 living Level 3 45 44 37 31
A 2 bed 1 Level 3 50 49 42 36
A 2 living Level 3 45 44 37 31
A 3 bed 1 Level 3 46 45 38 32
A 3 living Level 3 45 44 37 31
A 4 bed 1 Level 3 49 48 41 35
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Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
A 4 bed 2 Level 3 44 43 36 30
A 4 living Level 3 45 44 37 31
A 5 bed 1 Level 3 49 48 41 35
A 5 living Level 3 45 44 37 31
A 6 bed 1 Level 3 45 44 37 31
A 6 bed2 | Level 3 49 48 41 35
A 6 bed 3 Level 3 55 54 47 41
A 6 living Level 3 46 45 38 32
A 7 bed1 | Level 3 65 64 57 51
A 7 living Level 3 61 60 53 47
A 8 bed 1 Level 3 65 64 57 51
A 8 living Level 3 61 60 53 47
A 9 bed1 | Level 3 65 64 57 51
A 9 living Level 3 63 62 55 49
A 10 bed 1 Level 3 63 62 55 49
A 10 living Level 3 63 62 55 49
A 11 bed1 | Level 3 64 63 56 50
A 11 living Level 3 63 62 55 49
A 12 bed 1 Level 3 65 64 57 51
A 12 bed1 | Level 3 58 57 50 44
A 12 living Level 3 63 62 55 49
B 1 bed 1 Level 1 37 36 29 23
B 1 bed 2 Level 1 42 41 34 28
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Aÿ Tÿ CDEÿBÿ HDIDJÿBÿ MRÿ MBÿ UKÿ KTÿ
Aÿ Tÿ JOIOPQÿ HDIDJÿBÿ MBÿ MSÿ UGÿ KLÿ
Aÿ Nÿ CDEÿBÿ HDIDJÿBÿ MGÿ MRÿ UUÿ KNÿ
Aÿ Nÿ JOIOPQÿ HDIDJÿBÿ MBÿ MSÿ UGÿ KLÿ
Aÿ BSÿ CDEÿBÿ HDIDJÿBÿ MGÿ MRÿ UUÿ KNÿ
Aÿ BSÿ JOIOPQÿ HDIDJÿBÿ UNÿ UTÿ UBÿ KUÿ
ÿ
12345673898 3898 989 3898 989 3898 98 445 5 5 ÿ ÿ
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[OCR of page images]
Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
B 1 bed 3 Level 1 47 46 39 33
B 1 living Level 1 37 36 29 23
B 2 bed 1 Level 1 44 43 36 30
B 2 bed2 | Level1 37 36 29 23
B 2 living Level 1 37 36 29 23
B 3 bed1 | Level1 39 38 31 25
B 3 living Level 1 37 36 29 23
B 4 bed 1 Level 1 43 42 35 29
B 4 living Level 1 37 36 29 23
B 5 bed 1 Level 1 52 51 44 38
B 5 bed 2 Level 1 57 56 49 43
B 5 living Level 1 38 37 30 24
B 6 bed 1 Level 1 63 62 55 49
B 6 bed2 | Level1 56 55 48 42
B 6 living Level 1 61 60 53 47
B 7 bed 1 Level 1 62 61 54 48
B 7 living Level 1 61 60 53 47
B 8 bed 1 Level 1 62 61 54 48
B 8 living Level 1 61 60 53 47
B 9 bed 1 Level 1 63 62 55 49
B 9 living Level 1 61 60 53 47
B 10 bed 1 Level 1 63 62 55 49
B 10 living Level 1 59 58 51 45
I;Mobs\2021\202 10208\20210208.3\20210923JJMA_R4_Development_Application_.docx
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Aÿ Bÿ CDEÿMÿ GDHDIÿJÿ KNÿ KRÿ KBÿ MPÿ
Aÿ Bÿ ISHSTUÿ GDHDIÿJÿ KLÿ MNÿ MJÿ JOÿ
Aÿ Jÿ CDEÿBÿ GDHDIÿJÿ KOÿ KPÿ MRÿ MJÿ
Aÿ Jÿ CDEÿJÿ GDHDIÿJÿ MNÿ MRÿ MBÿ JPÿ
Aÿ Jÿ ISHSTUÿ GDHDIÿJÿ KLÿ MNÿ MJÿ JOÿ
Aÿ Mÿ CDEÿBÿ GDHDIÿJÿ KJÿ KBÿ MKÿ JRÿ
Aÿ Mÿ ISHSTUÿ GDHDIÿJÿ KLÿ MNÿ MJÿ JOÿ
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Aÿ Pÿ CDEÿJÿ GDHDIÿJÿ PNÿ PRÿ PBÿ KPÿ
Aÿ Pÿ ISHSTUÿ GDHDIÿJÿ KBÿ KLÿ MMÿ JQÿ
Aÿ Oÿ CDEÿBÿ GDHDIÿJÿ OPÿ OKÿ PQÿ PBÿ
Aÿ Oÿ CDEÿJÿ GDHDIÿJÿ PRÿ PQÿ PLÿ KKÿ
Aÿ Oÿ ISHSTUÿ GDHDIÿJÿ OJÿ OBÿ PKÿ KRÿ
Aÿ Qÿ CDEÿBÿ GDHDIÿJÿ OMÿ OJÿ PPÿ KNÿ
Aÿ Qÿ ISHSTUÿ GDHDIÿJÿ OMÿ OJÿ PPÿ KNÿ
Aÿ Rÿ CDEÿBÿ GDHDIÿJÿ OMÿ OJÿ PPÿ KNÿ
Aÿ Rÿ ISHSTUÿ GDHDIÿJÿ OMÿ OJÿ PPÿ KNÿ
Aÿ Nÿ CDEÿBÿ GDHDIÿJÿ OPÿ OKÿ PQÿ PBÿ
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ÿ
12345673898 3898 989 3898 989 3898 98 445 5 5 ÿ ÿ
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[OCR of page images]
Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
B 1 bed 1 Level 2 40 39 32 26
B 1 bed 2 Level 2 45 44 37 31
B 1 bed 3 Level 2 49 48 41 35
B 1 living Level 2 40 39 32 26
B 2 bed 1 Level 2 46 45 38 32
B 2 bed2 | Level 2 39 38 31 25
B 2 living Level 2 40 39 32 26
B 3 bed 1 Level 2 42 41 34 28
B 3 living Level 2 40 39 32 26
B 4 bed 1 Level 2 45 44 37 31
B 4 living Level 2 39 38 31 25
B 5 bed 1 Level 2 55 54 47 41
B 5 bed2 | Level 2 59 58 51 45
B 5 living Level 2 41 40 33 27
B 6 bed 1 Level 2 65 64 57 51
B 6 bed2 | Level 2 58 57 50 44
B 6 living Level 2 62 61 54 48
B 7 bed 1 Level 2 63 62 55 49
B 7 living Level 2 63 62 55 49
B 8 bed1 | Level 2 63 62 55 49
B 8 living Level 2 63 62 55 49
B 9 bed 1 Level 2 65 64 57 51
B 9 living Level 2 62 61 54 48
I;Mobs\2021\202 10208\20210208.3\20210923JJMA_R4_Development_Application_.docx
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Bÿ Lÿ EFGÿCÿ IFJFKÿUÿ OVÿ OPÿ ODÿ UOÿ
Bÿ Lÿ EFGÿLÿ IFJFKÿUÿ OOÿ OUÿ UMÿ UDÿ
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Bÿ Nÿ KQJQRSÿ IFJFKÿUÿ ONÿ OOÿ UPÿ UCÿ
Bÿ Mÿ EFGÿCÿ IFJFKÿUÿ MNÿ MOÿ NPÿ NCÿ
Bÿ Mÿ EFGÿLÿ IFJFKÿUÿ NTÿ NVÿ NCÿ ONÿ
Bÿ Mÿ KQJQRSÿ IFJFKÿUÿ MUÿ MLÿ NNÿ OTÿ
Bÿ Pÿ EFGÿCÿ IFJFKÿUÿ MOÿ MUÿ NMÿ NDÿ
Bÿ Pÿ KQJQRSÿ IFJFKÿUÿ MUÿ MLÿ NNÿ OTÿ
Bÿ Vÿ EFGÿCÿ IFJFKÿUÿ MOÿ MUÿ NMÿ NDÿ
Bÿ Vÿ KQJQRSÿ IFJFKÿUÿ MUÿ MLÿ NNÿ OTÿ
ÿ
12345673898 3898 989 3898 989 3898 98 445 5 5 ÿ !ÿ
ÿ
[OCR of page images]
Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
B 10 bed 1 Level 2 65 64 57 51
B 10 living Level 2 60 59 52 46
B 1 bed 1 Level 3 45 44 37 31
B 1 bed 2 Level 3 47 46 39 33
B 1 bed 3 Level 3 51 50 43 37
B 1 living Level 3 45 44 37 31
B 2 bed 1 Level 3 48 47 40 34
B 2 bed 2 Level 3 44 43 36 30
B 2 living Level 3 45 44 37 31
B 3 bed 1 Level 3 46 45 38 32
B 3 living Level 3 45 44 37 31
B 4 bed 1 Level 3 48 47 40 34
B 4 living Level 3 45 44 37 31
B 5 bed 1 Level 3 56 55 48 42
B 5 bed 2 Level 3 59 58 51 45
B 5 living Level 3 45 44 37 31
B 6 bed 1 Level 3 65 64 57 51
B 6 bed 2 Level 3 59 58 51 45
B 6 living Level 3 63 62 55 49
B 7 bed1 | Level 3 64 63 56 50
B 7 living Level 3 63 62 55 49
B 8 bed 1 Level 3 64 63 56 50
B 8 living Level 3 63 62 55 49
I;Mobs\2021\202 10208\20210208.3\20210923JJMA_R4_Development_Application_.docx
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Bÿ Cÿ DEFÿHÿ IEJEKÿLÿ MNÿ MOÿ NPÿ NHÿ
Bÿ Cÿ KQJQRSÿ IEJEKÿLÿ MLÿ MTÿ NNÿ OCÿ
Bÿ HUÿ DEFÿHÿ IEJEKÿLÿ MNÿ MOÿ NPÿ NHÿ
Bÿ HUÿ KQJQRSÿ IEJEKÿLÿ MHÿ MUÿ NLÿ OPÿ
Vÿ Hÿ DEFÿHÿ IEJEKÿHÿ NHÿ NUÿ OLÿ LPÿ
Vÿ Hÿ KQJQRSÿ IEJEKÿHÿ OPÿ OMÿ LCÿ LLÿ
Vÿ Tÿ DEFÿHÿ IEJEKÿHÿ OCÿ OWÿ OHÿ LNÿ
Vÿ Tÿ KQJQRSÿ IEJEKÿHÿ NUÿ OCÿ OTÿ LMÿ
Vÿ Lÿ DEFÿHÿ IEJEKÿHÿ OWÿ OPÿ OUÿ LOÿ
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Vÿ Oÿ DEFÿHÿ IEJEKÿHÿ OWÿ OPÿ OUÿ LOÿ
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Vÿ Oÿ DEFÿLÿ IEJEKÿHÿ LNÿ LOÿ TPÿ THÿ
Vÿ Oÿ KQJQRSÿ IEJEKÿHÿ OLÿ OTÿ LNÿ TCÿ
Vÿ Nÿ DEFÿHÿ IEJEKÿHÿ OLÿ OTÿ LNÿ TCÿ
Vÿ Nÿ DEFÿTÿ IEJEKÿHÿ NHÿ NUÿ OLÿ LPÿ
Vÿ Nÿ DEFÿLÿ IEJEKÿHÿ LPÿ LMÿ TCÿ TLÿ
Vÿ Nÿ KQJQRSÿ IEJEKÿHÿ NUÿ OCÿ OTÿ LMÿ
Vÿ Mÿ DEFÿHÿ IEJEKÿHÿ NLÿ NTÿ ONÿ LCÿ
Vÿ Mÿ DEFÿTÿ IEJEKÿHÿ NUÿ OCÿ OTÿ LMÿ
Vÿ Mÿ KQJQRSÿ IEJEKÿHÿ OMÿ ONÿ LWÿ LTÿ
Vÿ Pÿ DEFÿHÿ IEJEKÿHÿ NLÿ NTÿ ONÿ LCÿ
Vÿ Pÿ DEFÿTÿ IEJEKÿHÿ NHÿ NUÿ OLÿ LPÿ
ÿ
12345673898 3898 989 3898 989 3898 98 445 5 5 ÿ !ÿ
ÿ
[OCR of page images]
Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
B 9 bed 1 Level 3 65 64 57 51
B 9 living Level 3 63 62 55 49
B 10 bed 1 Level 3 65 64 57 51
B 10 living Level 3 61 60 53 47
Cc 1 bed 1 Level 1 51 50 43 37
Cc 1 living Level 1 47 46 39 33
c 2 bed 1 Level 1 49 48 41 35
Cc 2 living Level 1 50 49 42 36
C 3 bed 1 Level 1 48 47 40 34
Cc 3 living Level 1 43 42 35 29
Cc 4 bed 1 Level 1 48 47 40 34
Cc 4 bed 2 Level 1 47 46 39 33
Cc 4 bed 3 Level 1 35 34 27 21
c 4 living Level 1 43 42 35 29
c 5 bed 1 Level 1 43 42 35 29
Cc 5 bed2 | Level1 51 50 43 37
Cc 5 bed 3 Level 1 37 36 29 23
Cc 5 living Level 1 50 49 42 36
Cc 6 bed 1 Level 1 53 52 45 39
c 6 bed2 | Level1 50 49 42 36
Cc 6 living Level 1 46 45 38 32
c 7 bed 1 Level 1 53 52 45 39
c 7 bed 2 Level 1 51 50 43 37
I;Mobs\2021\202 10208\20210208.3\20210923JJMA_R4_Development_Application_.docx
36
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ÿ
342567ÿ 19:;<=>ÿ 19:;?@9'$'(ÿ 19:;A$(6+ÿ
"#$%&$'(ÿ *'$+ÿ ,--.ÿ /%--0ÿ 12&"4 87ÿ &"487ÿ &"487ÿ &"487ÿ
Bÿ Cÿ DEFEGHÿ IJFJDÿLÿ MNÿ MOÿ PQÿ PRÿ
Bÿ Qÿ SJTÿLÿ IJFJDÿLÿ OMÿ OPÿ MNÿ MUÿ
Bÿ Qÿ DEFEGHÿ IJFJDÿLÿ MQÿ MCÿ MUÿ PMÿ
Bÿ Vÿ SJTÿLÿ IJFJDÿLÿ OOÿ OMÿ MCÿ MLÿ
Bÿ Vÿ DEFEGHÿ IJFJDÿLÿ OPÿ ORÿ MOÿ PVÿ
Bÿ LUÿ SJTÿLÿ IJFJDÿLÿ OVÿ OQÿ OLÿ MOÿ
Bÿ LUÿ SJTÿRÿ IJFJDÿLÿ OVÿ OQÿ OLÿ MOÿ
Bÿ LUÿ DEFEGHÿ IJFJDÿLÿ MQÿ MCÿ MUÿ PMÿ
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Bÿ Pÿ SJTÿLÿ IJFJDÿRÿ OUÿ MVÿ MRÿ PNÿ
Bÿ Pÿ DEFEGHÿ IJFJDÿRÿ MOÿ MMÿ PCÿ PLÿ
Bÿ Mÿ SJTÿLÿ IJFJDÿRÿ MVÿ MQÿ MLÿ POÿ
Bÿ Mÿ SJTÿRÿ IJFJDÿRÿ MVÿ MQÿ MLÿ POÿ
Bÿ Mÿ SJTÿPÿ IJFJDÿRÿ PQÿ PCÿ PUÿ RMÿ
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Bÿ Oÿ SJTÿRÿ IJFJDÿRÿ ORÿ OLÿ MMÿ PQÿ
Bÿ Oÿ SJTÿPÿ IJFJDÿRÿ MUÿ PVÿ PRÿ RNÿ
Bÿ Oÿ DEFEGHÿ IJFJDÿRÿ OLÿ OUÿ MPÿ PCÿ
Bÿ Nÿ SJTÿLÿ IJFJDÿRÿ OMÿ OPÿ MNÿ MUÿ
ÿ
12345673898 3898 989 3898 989 3898 98 445 5 5 ÿ !ÿ
ÿ
[OCR of page images]
Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
Cc 7 living Level 1 46 45 38 32
c 8 bed1 | Level1 54 53 46 40
c 8 living Level 1 48 47 40 34
Cc 9 bed 1 Level 1 55 54 47 41
Cc 9 living Level 1 53 52 45 39
c 10 bed1 | Level1 59 58 51 45
c 10 bed 2 Level 1 59 58 51 45
Cc 10 living Level 1 48 47 40 34
c 1 bed1 | Level 2 53 52 45 39
Cc 1 living Level 2 49 48 41 35
Cc 2 bed 1 Level 2 51 50 43 37
Cc 2 living Level 2 52 51 44 38
c 3 bed1 | Level 2 50 49 42 36
c 3 living Level 2 45 44 37 31
c 4 bed 1 Level 2 49 48 41 35
Cc 4 bed 2 Level 2 49 48 41 35
Cc 4 bed 3 Level 2 38 37 30 24
Cc 4 living Level 2 44 43 36 30
Cc 5 bed 1 Level 2 45 44 37 31
c 5 bed2 | Level 2 52 51 44 38
Cc 5 bed 3 Level 2 40 39 32 26
C 5 living Level 2 51 50 43 37
Cc 6 bed 1 Level 2 54 53 46 40
I;Mobs\2021\202 10208\20210208.3\20210923JJMA_R4_Development_Application_.docx
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Aÿ Pÿ CDEÿLÿ HDIDJÿGÿ KKÿ KNÿ NPÿ NLÿ
Aÿ Pÿ CDEÿGÿ HDIDJÿGÿ KGÿ KLÿ NNÿ OUÿ
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Aÿ Uÿ CDEÿLÿ HDIDJÿGÿ KBÿ KKÿ NUÿ NGÿ
Aÿ Uÿ JQIQRSÿ HDIDJÿGÿ NTÿ NUÿ NLÿ OKÿ
Aÿ Tÿ CDEÿLÿ HDIDJÿGÿ KBÿ KKÿ NUÿ NGÿ
Aÿ Tÿ JQIQRSÿ HDIDJÿGÿ KNÿ KOÿ NBÿ NMÿ
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ÿ
12345673898 3898 989 3898 989 3898 98 445 5 5 ÿ ÿ
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[OCR of page images]
Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
Cc 6 bed 2 Level 2 51 50 43 37
Cc 6 living Level 2 47 46 39 33
c 7 bed 1 Level 2 55 54 47 41
c 7 bed 2 Level 2 52 51 44 38
Cc 7 living Level 2 47 46 39 33
c 8 bed1 | Level 2 56 55 48 42
Cc 8 living Level 2 49 48 41 35
Cc 9 bed 1 Level 2 56 55 48 42
Cc 9 living Level 2 54 53 46 40
c 10 bed 1 Level 2 61 60 53 47
c 10 bed2 | Level 2 61 60 53 47
Cc 10 living Level 2 50 49 42 36
c 1 bed1 | Level 3 54 53 46 40
c 1 living Level 3 51 50 43 37
c 2 bed 1 Level 3 52 51 44 38
Cc 2 living Level 3 53 52 45 39
Cc 3 bed 1 Level 3 52 51 44 38
Cc 3 living Level 3 48 47 40 34
Cc 4 bed 1 Level 3 51 50 43 37
c 4 bed2 | Level 3 50 49 42 36
c 4 bed 3 Level 3 43 42 35 29
C 4 living Level 3 47 46 39 33
Cc 5 bed 1 Level 3 47 46 39 33
I;Mobs\2021\202 10208\20210208.3\20210923JJMA_R4_Development_Application_.docx
38
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Building | Unit | Room | Floor L10(18h) | Lea.Day | Leq.Evening | Leq.Night
dB(A) dB(A) dB(A) dB(A)
Cc 5 bed 2 Level 3 53 52 45 39
Cc 5 bed 3 Level 3 44 43 36 30
c 5 living Level 3 52 51 44 38
c 6 bed 1 Level 3 55 54 47 41
Cc 6 bed 2 Level 3 52 51 44 38
Cc 6 living Level 3 49 48 41 35
c 7 bed 1 Level 3 55 54 47 41
Cc 7 bed 2 Level 3 53 52 45 39
Cc 7 living Level 3 49 48 41 35
c 8 bed 1 Level 3 56 55 48 42
Cc 8 living Level 3 50 49 42 36
Cc 9 bed 1 Level 3 57 56 49 43
Cc 9 living Level 3 55 54 47 41
c 10 bed 1 Level 3 61 60 53 47
Cc 10 bed 2 Level 3 61 60 53 47
Cc 10 living Level 3 51 50 43 37
Facade requirements based on these tabulated values are presented in Section 6.
5.2 NOOSA CIVIC SHOPPPING CENTRE
Analysis of noise impacts from Noosa Civic Shopping Centre were conducted based on the following
assumptions:
« Mechanical plant noise source levels based on the attended measurements in Table 4 with
additional controls listed below, which limit the noise impacts.
e The following operational conditions regarding the site mechanical plant:
o ALC has been advised that the chillers are switched off at 9pm, hence they have been
considered not to be operational during the night time period.
o The condenser units are considered to be operational prior to 7am.
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¢ Commonly used allowance to have 10-15dB noise reduction across facade with partially opened
windows for ventilation to determine the impacts internally. Additional noise reduction will be
achieved, given the residential buildings are likely recommended to have acoustically rated
windows with additional provision for ventilation to allow external windows to be closed. We
note that the basis of judgement is Environmental Protection (Noise) Policy 2019 Acoustic
Quality Objectives which indicates a 20dB difference between outdoor and indoor acoustic
quality objectives which would lead to higher outdoor noise allowances in comparison to our
assessment;
e The residential development site ground level on Lots 17-19 are 4.62metres below the loading
dock level as advised by the developer;
¢ The loading dock locations presented in Figure 7 below;
Lb1
Woolworths
Residential lots (Lots 17-19)
Noosa Civic Loading Docks
Figure 7 - Loading Dock Locations
e Loading Dock 1 (Woolworths) is the only loading dock with refrigerated trucks operational and
it is assumed that the refrigeration units are not able to be turned off;
« Loading Dock 2 is used by light vehicles;
e Loading Docks 3-5 are used by regular trucks;
e Loading Docks 2-5 do not have refrigeration trucks and therefore, no idling is allowed with the
exception of a short time pick-up/drop off (less than 10minutes) within the loading dock;
e Rear loading dock operational hours
o Monday - Saturday: 5am to 9pm
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o Sunday: 8am to 6pm
Vehicles are limited to a speed of 10km/h in the loading dock;
Refrigeration truck idle time of 15 minutes while unloading and this idling was assumed to only
occur in the loading dock, and not along the boundaries or at the entrance to the loading docks.
The refrigeration trucks, therefore, must not enter the site prior to loading to wait for their turn.
Such restrictions should be included if not yet followed (e.g. signs installed at the entry and
along the boundaries of the shopping centre loading docks);
No Idling time for all other trucks including rubbish collection trucks, and such restrictions
should be included if not yet followed (e.g. signs installed at the entry and along the boundaries
of the shopping centre loading docks);
Mechanical plant adjacent and within loading docks is not operational between 9pm and 7am
Monday — Saturday, and 6pm and 8am on Sunday;
Kitchen exhaust fans are not operational between 9pm and 7am Monday — Saturday, and 6pm
and 8am on Sunday;
Compactor operational hours:
o Monday — Wednesday, and Friday — Sunday: 8am to 6pm
o Thursday: 8am to 9pm
No trolley collection between 10pm and 7am;
The following sound power levels:
o Roof condenser units sound power levels 79-93 dB(A) Leg, based on onsite
measurements at Noosa Civic;
o Kitchen exhaust fans sound power levels 98dB(A) and 99dB(A) Leg, based on onsite
measurements at Noosa Civic;
o Loading dock truck sound power level 101dB(A) Lmax at a height of 3m above the ground
level, obtained from onsite measurements at Noosa Civic and similar equipment
previously assessed by ALC;
o Refrigeration truck sound power level of 95dB(A) Leq at a height of 3m above the ground
level, obtained from measurements of similar equipment previously assessed by ALC;
o Compactor sound power level of 100dB(A) Lmax, obtained from measurements of similar
equipment previously assessed by ALC; and
o Light vehicles sound power level of 86dB(A) Leg, obtained from measurements of similar
equipment previously assessed by ALC.
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5.2.1. Mechanical Plant Noise
Mechanical noise impacts from the nearby Noosa Civic Centre were measured with the results presented in
Table 4. Utilising the measurements, mechanical plant noise was modelled using SoundPLAN™. The facade
noise maps are presented in Figure 8 to Figure 10.
Noosa Civic
Predicted Facade Noise Impacts
aearseneeees
ACOUSTIC
LOGIC
Figure 8 - Predicted Mechanical Plant Noise Levels Leg - view 1
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Noosa Civic
TEN)
Qrreaseses
Sorreaaeeses
ACOUSTIC
LOGIC
Noosa Civic
Tn
grresseses
aearseneeees
ACOUSTIC
LOGIC
Figure 10 — Predicted Mechanical Plant Noise Levels L., — view 3
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5.2.2 Loading Dock Activities
Loading Dock activities noise at Noosa Civic Shopping Centre was modelled using SoundPLAN™. The facade
noise maps are presented in Figure 11 to Figure 13.
Note an acoustic barrier along the loading dock as recommended in the Acoustic Logic Report for
Noosa Civic (ref: 20191414.3/0607A/R7/OB), dated 6 July 2021) was assumed.
The acoustic barrier location is marked up in Figure 16.
Noosa Civic
Loading Dock Vehicle Idling
Predicted Facade Noise Impacts
Prepared ty. OB
‘ate 19108/2001
Noise Level
ms
sesstegeuyss
ACOUSTIC
Loaic
Figure 11- Loading Dock Vehicle Idling Noise Levels (Leq)
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Noosa Civic
Loading Dock Vehicle Movements
Predicted Facade Noise Impacts
Prepared ty. OB
‘ate 19108/2001
Noise Level
sesstegeuyss
ACOUSTIC
Loaic
Figure 12- Loading Dock Movement Noise Levels (Leq)
Noosa Civic
Loading Dock Vehicle Movements
Predicted Facade Noise Impacts
Prepared ty. OB
‘ate 19108/2001
Noise Level
nds)
ageesaessees
ACOUSTIC
Loaic
Figure 13- Loading Dock Movement Noise Levels (Lmax)
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5.2.3. Compactor
Compactor noise at Noosa Civic Shopping Centre was modelled using SoundPLAN™. The facade noise map
is presented in Figure 14.
Note an acoustic barrier along the loading dock as recommended in the Acoustic Logic Report for
Noosa Civic (ref: 20191414.3/0607A/R7/OB), dated 6 July 2021) was assumed.
The acoustic barrier location is marked up in Figure 16.
Noosa Civic
Compactor
Predicted Facade Noise Impacts
Prepared by: 08
Date 19)08/2001
Noise Level
ax
intB)
_f ACOUSTIC
LOGIC
Figure 14- Compactor Noise Levels (Lmax)
5.2.4 Compliance with Noosa Civic Noise Targets
The predicted noise impacts based on the SoundPLAN™ modelling conducted were compared against the
Noosa Civic noise criteria in Section 4.5. The noise levels are presented in Table 15 and Table 16. We note
that the values are indicative and informative only as compliance with noise impact limits is the responsibility
of the Noosa Civic shopping centre and not the residential development. No fagade upgrades for the
residential development to address Noosa Civic shopping centre are provided and all requirements to
achieve compliance with Noosa Civic noise emission limit are presented in a separate report.
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Table 15 — Predicted Continuous Noise Impacts with Optimised Acoustic Barrier
lian
. Internal Noise seus Compliance Comp tance
Noise . Criteria Laeg, adj, . with
Source Time Level Leg, adj thr with Condition
dB(A)" ‘wr Condition 5 >
70
Mechanical Day 33 < 35 Yes Yes
Plant Evening 33 <35 Yes Yes
Noise Night 25 < 30 Yes Yes
Loading Day 15 <35 Yes N/A
Dock Evening 15 < 35 Yes N/A
Movement | Night 15 < 30 Yes N/A
Loading Day 25 < 35 Yes N/A
Dock .
Vehicle Evening 25 <35 Yes N/A
Idling Night 25 < 30 Yes N/A
Note?: Assumed 10-15dB noise reduction across facade with partially opened windows for ventilation.
Note*: Condition 70 is not applicable to all mechanical plant and is only considered for air-conditioning
equipment noise.
Table 16 — Predicted Transient Noise Impacts with Optimised Acoustic Barrier
: . ogo Compliance
Noise . Internal Noise Level Lamax Criteria . Pp" wpe
Time 1 with Condition
Source dB(A) Lat, adj, thr 5
Loading Day 37 <45 N/A
Dock Evening 37 <45 N/A
Movement Night 37 < 40 N/A
Day 37 <45 N/A
Compactor Evening 37 <45 N/A
Night N/A N/A N/A
Note: Assumed 10-15dB noise reduction across facade with partially opened windows for ventilation.
Compliance is predicted for mechanical plant, loading dock vehicle movements, loading dock vehicle idling,
and compactor noise for all time periods.
Based on the above predictions, the following is noted for mechanical plant noise:
1) Night time period: compliance is predicted for the night time period based on the following
conditions:
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a. The chillers are switched off at 9pm and shall not be operational during the night time
period.
b. The operational conditions of other plant are as listed in Section 6.2.
We note that the values are indicative and informative only as compliance with noise impact limits is the
responsibility of the Noosa Civic shopping centre and not the residential development. No facade upgrades
for the residential development to address Noosa Civic shopping centre are provided and all requirements
to achieve compliance with Noosa Civic noise emission limit are presented in a separate report.
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5.3. ONSITE ACTIVITIES
5.3.1 General Onsite Activities
Assessment of the general noise activities onsite to the nearest sensitive receivers has been carried out with
the results presented in the following sections.
Note the noise impacts consider building screening, distance attenuation, and barrier attenuation.
Additionally source noise levels included correction due to tonality and impulsiveness as per Australian
Standard AS1055: 2018.
The following table indicates predictions of noise emissions from the site operations.
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The closest residential receiver is as follows:
1) Residential development at 60 Hofmann Drive.
The acoustic amenity Leq outdoor noise levels are presented in Table 17.
Table 17 Acoustic Quality Objectives Outdoor Noise Levels (Laeq,inr), Receiver 1: 60 Hofmann Drive
: Single
Activity cane Event No. Events per hour Distance Noise Impacts Laeg, thr Outdoor Noise Compliance
Duration
Laeg,agj (seconds) | Day | Evening | Night (m) Day | Evening | Night Day Evening | Night
Criteria 50 50 45
Car Door Closure (Basement) 83 2 40 20 8 40 8 5 1 Yes Yes Yes
Car Engine Start (Basement) 82 2 40 20 8 40 7 4 0 Yes Yes Yes
Car on Ramp (Ground Level) 82 10 40 20 8 45 31 28 24 Yes Yes Yes
Car Passby 84 8 40 20 8 40 33 30 26 Yes Yes Yes
Swimming Pool (Ground Level) 82 900 4 4 0 75 37 37 0 Yes Yes Yes
Total 40 39 29 Yes Yes Yes
Based on the noise impacts presented in Table 17, general noise from the site is predicted to comply with the nominated noise criteria at the closest sensitive receivers.
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5.3.2 Preliminary Onsite Mechanical Plant Noise
A preliminary assessment of the mechanical plant onsite to the nearest sensitive receivers has been carried out
with the results presented in the following sections.
Note the noise impacts consider building screening, distance attenuation, and barrier attenuation. Additionally
source noise levels included correction due to tonality and impulsiveness as per Australian Standard AS1055: 2018.
The assessment was based on the following assumptions:
e Each unit has a single condenser unit;
e The condenser unit has a sound power level of SWL 63dB(A) Leq;
e The mechanical plants are located in the plant rooms shown in the attached plans;
e The plant rooms are fully enclosed with minimum Rw50 walls, and only one side of the plant room is
open for ventilation.
Table 18 - Predicted Mechanical Plant Noise Impacts at Receiver 1: 60 Hofmann Drive
Building No. Single Predicted Criteria Compliance
Condenser condenser Noise (Night)
Units unit SWL Impacts
Leq dB(A)
A 36 30 dB(A) Yes
B 36 68 dB(A) 30 dB(A) Yes
39 dB(A)
C 30 29 dB(A) Yes
Total 96 - 35 dB(A) Yes
Based on the noise impacts presented in Table 18, mechanical plant noise from the site is predicted to comply
with the nominated noise criteria at the closest sensitive receivers.
Note, the mechanical plant noise assessment and predicted noise is preliminary only and shall be reviewed
at a the building approval stage once details of the plant are available once all plant is selected and the
detailed design of all plant is carried out.
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6 RECOMMENDATIONS - BUILDING SHELL AND EXTERNAL GLAZING
Impact from shopping center and loading dock areas have been addressed in a previous noise impact assessment
report (ref: 20191414.3/0607A/R7/OB), dated 6 July 2021). The recommendations in this report are based on the
assumption that the Shopping center achieves compliance as per Mediation Judgement. Further, AL has been
advised by Stockwell that loading dock impacts will be treated utilizing Acoustic Barriers and operational controls
measures as listed in the abovementioned report. On that basis, no fagade upgrades to address Noosa Civic
shopping Centre have been adopted.
6.1. GLAZING
The glazing systems should be selected and installed to meet the noise criteria presented in this report.
Minimum requirements are presented to satisfy only the acoustic requirements for the facade and glazing based
on the current assessment methods. Where other requirements for the fagade and glazing are specified elsewhere
in the glazing specification, the glazing shall be selected to meet all requirements and may result in increased
glass thicknesses over those specified in the acoustic specification but shall in no cases fall below the minimum
thicknesses and requirements set out in this specification.
The design of the window mullions, perimeter seals of openable and fixed glazing, and the installation of the
windows/doors in the building openings shall be selected so that the completed system reduces internal noise
levels to at or below the requirements in the abovementioned report and in any case shall meet or exceed the
minimum acceptable glazing requirements nominated below.
Thicker glazing may be required for structural, safety or other purposes. Where required to use thicker glazing
than that scheduled, this will also be acoustically acceptable.
It is recommended that only window systems having test results indicating compliance with the required ratings
obtained in a certified laboratory be used. The submitted glazing system acoustic performance and thickness
deviations from the requirements in this brief are to be approved by the acoustic consultant.
Refer to Appendix A for Glazing types.
The glazing types and markups are satisfactory and applicable on the condition that the acoustic treatments in
section 8 are fully implemented to achieve compliance with the Mediation Judgement No. 765 of 2020
(dated 3 September 2020),
Table 19 —- Minimum Installed Glazing Requirements
Glazin Examples of Typical Minimum Minimum Acoustic Performance
9 Glazing Thickness (all must be complied with)
Type A 10.38mm laminated glass Rw35 and Table 20
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Glazin Examples of Typical Minimum Minimum Acoustic Performance
9 Glazing Thickness (all must be complied with)
Type B 6.38mm laminated glass Rw32 and Table 20
Type C 4mm float Rw24 and Table 20
In addition to comply with the above, glazing suites are to achieve the following installed minimum transmission
loss values (glazing and frame).
Table 20 — Minimum Glazing Requirements
Glazing Minimum installed transmission loss, dB
Type 63Hz 125Hz | 250Hz | 500Hz | 1kHz 2kHz | 4kHz 8Khz
Type A 22 27 31 34 36 37 49 52
Type B 19 22 24 30 36 33 38 42
Type C 17 20 23 26 29 28 26 38
All external windows and doors listed are required to be fitted with Q-lon type acoustic seals. (Mohair Seals are
unacceptable).
Where glazing is required to achieve a nominated acoustic performance the perimeter of the window frame shall
be acoustically sealed into the window opening so there is no leakage of noise between the window frame and
the building opening. The sealing method selected shall take into account and allow for any movement of the
window frame relative to the building opening and so that the acoustic performance is maintained.
IMobs\2021\202 10208\202 10208.3\20210923JJMA_R4_Development_Application_.docx 53
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6.2 ROOF / CEILING CONSTRUCTION
The recommended roof/ceiling constructions for pitched roof is shown in Figure 2 below. Penetrations in all
ceilings (such as for light fittings etc.) must be acoustically treated and sealed gap free with a flexible sealant. The
ceiling sheet minimum requirements are presented in Table 21
Steel sheet roof with Anticon 145
Trus:
\ below \,
V rN
Min 250mm
75mm thick Glass wool insulation Air gap
- Figure 12 - Roof/ceiling constructions \
Ceiling sheet
Table 21 - External Lightweight Roof Constructions
A ic Rati
Space coustic Rating Internal Lining Truss System External Lining
1x 10mm plasterboard Minimum of
(additional 10mm 250mm truss
Level 3 Pitched plasterboard required to with 75mm Sheet Metal Roof
Roof Rw 47 address Noosa Civic thick 11kg/m3 | with Anticon 145
mechanical plant noise as glasswool below
is with limited treatment insulation in
applied at source) cavity
6.3 EXTERNAL WALLS
External walls are of concrete/masonry of acoustic rating Rw50 and will not require acoustic upgrading. Alternative
construction details may be suitable but must be submitted to Acoustic Logic for review and approval.
6.4 ACOUSTIC SEALING OF WINDOW FRAMES
Where glazing is required to achieve a nominated acoustic performance the perimeter of the window frame shall
be acoustically sealed into the window opening so there is no leakage of noise between the window frame and
the building opening. The sealing method selected shall take into account and allow for any movement of the
window frame relative to the building opening and so that the acoustic performance is maintained.
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7 RECOMMENDATIONS - NOISE EMISSIONS
7.1 MECHANICAL PLANT
The preliminary review of mechanical plant indicates compliance at the closest noise sensitive receivers. However,
the mechanical plant associated with the development has not been selected and therefore, detailed assessment
is required prior to BA phase of the project. The selection of plant and acoustic treatment added to the plant must
ensure that noise emission limits at sensitive sites achieve compliance with the noise emission limits.
Table 22 - Plant Noise Emission Limits
Location Equipment Noise Emission Limit dB(A)!
(7am- (7pm- (10pm-7am)
7pm) 10pm)
Sensitive Surrounding Receiver Pumps 55 49 36
Air-conditioning 55 51 39
equipment
'Noise emission limits were based on ambient noise levels in Table 2 of the unattended noise monitoring
conducted closest to the site and noise sensitive receivers. The noise limits are applicable at current residential
buildings outside of the development site. Generally, own development will be targeting AS2107:2016 indoor
noise levels.
7.2. OTHER NOISE SOURCES
Other noise sources with any significance are anticipated to include site generated traffic and waste collection.
Waste collection is not anticipated to generate adverse impact onto surrounding developments, given that
collection times would align with the collection times at the adjacent existing residential sites.
Traffic generation from the proposed development is not anticipated to generate adverse impact onto the
adjacent existing residential receivers given that Hofmann Drive will be extended, thus generating higher traffic
noise compared to the proposed development.
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8 NOOSA CIVIC SHOPPING CENTRE MECHANICAL PLANT - ACOUSTIC TREATMENTS
The required acoustic treatments to the mechanical plant servicing Noosa Civic Shopping Centre summarised
below:
8.1. MECHANICAL PLANT OPERATING HOURS:
a. The chillers in the mechanical plant room are switched off at 99m and shall not be operational during the
night time period (location 7);
b. Previous assessment included recommendation for condenser units to either be operational with reduced
capacity to lower the noise emissions by 5dB(A) or are switched off during the night time period. Due to
the operation hours of the shopping centre, this assumption has been now excluded and we expect the
condensers to operate prior to 7am;
c. Mechanical plant adjacent and within loading docks is not operational between 9pm and 7am Monday —
Saturday, and 6pm and 8am on Sunday (location 7 and adjacent to loading docks); and
d. Kitchen exhaust fans are not operational between 9pm and 7am Monday — Saturday, and 6pm and 8am
on Sunday.
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8.2. STATIONARY PLANT TREATMENTS
The following acoustic treatment for the Noosa Civic stationary plant shall be fully implemented:
e Solid, gap-free acoustic barriers with a minimum surface density of 12kg/m2 as marked up below
(yellow line);
¢ Acoustimax panels (75mm thick ) in lieu of the standard louvers indicated in the figure below (red
line); and
e Solid gap-free acoustic barriers for the rooftop exhaust fans using 75mm thick Acoustimax panels
(purple line).
=== Acoustimax panels (75mm thick) replacing current standard louvers
Acoustic barrier to height 500mm above top of plant
ees Acoustimax panels (75mm thick) to height 500mm above top of plant
Figure 15- Mechanical Plant Acoustic Barriers
An acoustic barrier along the loading dock as recommended in the Acoustic Logic Report for Noosa Civic
(ref: 20191414.3/0607A/R7/OB), dated 6 July 2021) was assumed.
The assumed acoustic barrier of height 2-4 metres above the loading dock pad level and with a minimum surface
density of 12kg/m? or higher. The acoustic barrier location is marked up in Figure 16.
Compliance with noise limits is the responsibility of the shopping centre. The predictions in this report are based
on the mechanical plant operating as is.
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— Acoustic barrier 2.0 metre high above loading dock ground levell
=mmss==== Acoustic barrier 3.0 metre high above loading dock ground levell
w=me=== Acoustic barrier 4.0 metre high above loading dock ground level
Figure 16 — Proposed Optimised Acoustic Barrier Location
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59
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9 CONCLUSION
A noise impact assessment was conducted for the proposed residential development on Hoffman Drive, Noosa.
As part of the assessment unattended road traffic and ambient noise monitoring was conducted to determine the
acoustic environment in the area. Recommendations are provided in Section 6 to address traffic noise impacts.
Noise activities from Noosa Civic Shopping Centre were considered and impacts were predicted using
SoundPLAN™ computer modelling. Provided the recommendations section 0 and section 7 of this report are
implemented, compliance is predicted with the adopted noise limits in Section 4.6. We note that the values are
indicative and informative only as compliance with noise impact limits is the responsibility of the Noosa Civic
shopping centre and not the residential development. No facade upgrades for the residential development to
address Noosa Civic shopping centre are provided and all requirements to achieve compliance with Noosa Civic
noise emission limit are presented in a separate report.
Noise emissions associated with the development site have been addressed in Section 7. Mechanical plant
selection may differ and therefore, detailed assessment is required prior to BA phase of the project. The selection
of plant and acoustic treatment added to the plant must ensure that noise emission limits at sensitive sites achieve
compliance with the noise emission limits.
We trust this information is satisfactory. Please contact us should you have any further queries.
Yours faithfully,
a
WiltMteg—
Acoustic Logic Pty Ltd
Justin McCartney
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20225
Project No:
Date:
Scale: 1: 200@ A3
Plaza Level, Mosaic
826 Ann St
Fortitude Valley QLD 4006
T +61 7 3253 9900
[email protected]
These designs and plans are the copyright of MODE DESIGN Corp, Pty Ltd and cannot be reproduced without written
permission
HOFMANN DRIVE,
NOOSA
DEVELOPMENT APPROVAL
Do not scale off this drawing
Drawn / Check: AuChecker
DAI
Page 67
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Type A Glazing
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Fortitude Valley QLD 4006 rawn eck: Au
T3617 3283 9900 sTockweur = DEVELOPMENT APPROVAL DATI2
[email protected]
These designs and plans are the copyright of MODE DESIGN Corp, Pty Ltd and cannot be reproduced without written Donot scale off this drawing
permission
Page 68
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Project No: 20225
Plaza Level, Mosaic HOFMANN DRIVE, Date: _
826 Ann St i NOOSA ~ Scale: / check 13 200@ As
rawn }eCK: u
DEVELOPMENT APPROVAL
° oO DA113
Fortitude Valley QLD 4006
T +617 3253 9900 STOCKWELL
[email protected]
These designs and plans are the copyright of MODE DESIGN Corp, Pty Ltd and cannot be reproduced without written
permission
Do not scale off this drawing
Page 69
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nn NOOSA " A
Fortitude Valley QLD 4006 Drawn / Check: AuChecker
T2617 3253 9900 sTockweu = DEVELOPMENT APPROVAL DAI21
[email protected]
These designs and plans are the copyright of MODE DESIGN Corp. Pty Ltd and cannot be reproduced without written Do not scale off this drawing
permission
Page 71
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vA Project No: 20225
Beannst i NOOsANN DRIVE, Seale: 1:200@ A3
nn NOOSA ‘ A
Fortitude Valley QLD 4006 Drawn / Check: AuChecker
T2617 3253 9900 sTockweu = DEVELOPMENT APPROVAL DAI23
[email protected]
These designs and plans are the copyright of MODE DESIGN Corp, Pty Ltd and cannot be reproduced without written
permission
Do not scale off this drawing
Page 73
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Be Ange Valley QLD 4006 : DEVELOPMENT APPROVAL Drawn / Check: Aachecker
T +617 3253 9900 STOCKWELL DA124
[email protected]
“These designs and plans are the copyright of MODE DESIGN Corp. Pty Ltd and cannot be reproduced without writen Dont scale of this Grawing
permission
Page 74
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Project No: 20225
Date:
HOFMANN DRIVE, Scale: 1: 200@ A3
a NOOSA Drawn / Check: AuChecker
DEVELOPMENT APPROVAL
Fortitude Valley QLD 4006
T +61 7 3253 9900
[email protected]
These designs and plans are the copyright of MODE DESIGN Corp, Pty Ltd and cannot be reproduced without written
permission
Do not scale off this drawing
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Page 75
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