environmental noise assessment - orange city council...environmental noise assessment ref: 6934-1.1r...
TRANSCRIPT
SUITE 17, 808 FOREST ROAD, PEAKHURST 2210 ABN 73 107 291 494 P. 02 9046 3800 [email protected] WWW.DAYDESIGN.COM.AU
Environmental Noise Assessment
Proposed Taco Bell Restaurant 52-54 Bathurst Road, Orange, NSW
REPORT No 6934-1.1R
DATE ISSUED 13 March 2020
Prepared For: Mc Duck Properties Pty Ltd 300 Rainbow Street Coogee NSW 2034 Attention: Mr Hector Abbott
Mc Duck Properties Pty Ltd Page 2 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
Revision History
Report Date Prepared Checked Comment
Draft 09/03/2019 Alexander Mendoza Stephen Gauld By email, for client review
Final 13/03/2019 Alexander Mendoza Stephen Gauld
Document R\6934-1.1R, 22 pages plus attachments
Disclaimer
The work presented in this document was carried out in accordance with the Day Design Pty Ltd Quality Management system. Day Design is certified to ISO9001. Day Design Pty Ltd reserves all copyright of intellectual property in any or all of Day Design’s documents. No permission, license or authority is granted by Day Design to any person or organisation to use any of Day Design’s documents for any purpose without written consent of Day Design. This report has been prepared for the client identified and cannot be relied or used by any third party. Any representation, statement, opinion or advice, expressed or implied in this report is made in good faith but on the basis that Day Design is not liable (whether by reason of negligence, lack of care or otherwise) to any person for any damage or loss whatsoever which has occurred or may occur in relation to that person taking or not taking (as the case may be) action in any respect of any representation, statement, or advice referred to above. Recommendations made in this report are intended to resolve acoustical problems only. No claims of expertise in other areas are made and no liability is accepted in respect of design or construction for issues falling outside the specialist field of acoustical engineering including but not limited to structural, fire, thermal, architectural buildability, fit for purpose, waterproofing or other aspects of building construction. Supplementary professional advice should be sought in respect of these issues. The information in this document should not be reproduced, presented or reviewed except in full. Prior to passing onto a third party, the Client is to fully inform the third party of the specific brief and limitations associated with the commission.
Mc Duck Properties Pty Ltd Page 3 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
CONTENTS
CONSULTING BRIEF ...................................................................................................................................................... 5
PROJECT DESCRIPTION ............................................................................................................................................... 6
2.1 Development Description ....................................................................................................................................... 6
2.2 Site Description ........................................................................................................................................................... 6
NOISE SURVEY INSTRUMENTATION ................................................................................................................... 8
MEASURED AMBIENT NOISE LEVELS ................................................................................................................. 9
4.1 Long Term, Unattended Noise Monitoring ...................................................................................................... 9
ACCEPTABLE NOISE LEVELS ................................................................................................................................. 11
5.1 NSW Noise Policy for Industry ............................................................................................................................ 11
5.2 Intrusiveness Criteria ............................................................................................................................................. 12
5.3 Amenity Criteria ........................................................................................................................................................ 13
5.4 Sleep Disturbance ..................................................................................................................................................... 14
5.5 Project Specific Noise Emission Criteria ......................................................................................................... 14
NOISE EMISSION .......................................................................................................................................................... 15
6.1 Plant Noise Emission ............................................................................................................................................... 15
6.2 Car Park and Drive-Thru Noise Emission ....................................................................................................... 16
6.3 Drive Thru Noise Emission ................................................................................................................................... 17
CALCULATED NOISE LEVELS ................................................................................................................................. 18
7.1 Sleep Disturbance ..................................................................................................................................................... 19
NOISE CONTROL RECOMMENDATIONS............................................................................................................ 21
NOISE IMPACT STATEMENT .................................................................................................................................. 22
Mc Duck Properties Pty Ltd Page 4 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
TABLES
Table 1 Noise Sensitive Receptors .................................................................................................................................. 6
Table 2 Noise Instrumentation......................................................................................................................................... 8
Table 3 Ambient Noise Levels ......................................................................................................................................... 10
Table 4 Amenity Criteria ................................................................................................................................................... 13
Table 5 Schedule of Mechanical Plant Sound Power Levels ............................................................................... 15
Table 6 Sound Power Levels of Car Park Noise ....................................................................................................... 16
Table 7 Sound Power Levels of Drive-Thru Speaker Box .................................................................................... 17
Table 8 Calculated Leq, 15 minute Noise Levels at Receptor Locations .................................................................. 18
Table 9 Calculated Leq, 15 minute Noise Levels at Non-Residential Receptor Locations (R5-R6) .............. 19
Table 10 Calculated Lmax Noise Levels at Residential Receptor Locations – R1-R2 .................................... 19
Table 11 Calculated Lmax Noise Levels at Residential Receptor Locations – R3-R4 .................................... 20
Mc Duck Properties Pty Ltd Page 5 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
CONSULTINGBRIEF
Day Design Pty Ltd was engaged by McDuck Properties Pty Ltd to carry out an environmental noise impact assessment for a proposed Taco Bell restaurant to be constructed at 52-54 Bathurst Road, Orange, NSW.
The scope of work is as follows:
Inspect the site and environs
Measure the background noise levels at critical locations and times
Establish acceptable noise level criterion
Quantify noise emissions from the restaurant
Calculate the level of noise emission, taking into account building envelope transmission loss, screen walls and distance attenuation
Prepare a site plan identifying the development and nearby noise sensitive locations
Provide recommendations for noise control (if necessary)
Prepare an Environmental Noise Impact Report.
Mc Duck Properties Pty Ltd Page 6 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
PROJECTDESCRIPTION
2.1 DevelopmentDescription
Mc Duck Properties Pty Ltd proposes to construct a new Taco Bell restaurant with a drive-thru and car park at 52-54 Bathurst Road, Orange, NSW.
Car parking will be provided for 25 vehicles (3 dedicated for staff). Entry and exit locations are located via driveways on Eyles Street and Bathurst Road.
The proposed operating hours are as follows:
10 am - 10 pm Sunday to Thursday, and
10 am - 11 pm Friday and Saturday.
2.2 SiteDescription
The site is on land zoned as B6 – EnterpriseCorridor under the Orange Local Environmental Plan 2011.
The site is located on the western side of Bathurst Road which forms part of the Mitchell Highway, a Classified Road under the Roads Act 1993. This section of road carries heavy traffic volumes, including heavy vehicles.
The nearest residential premises are located on adjacent blocks to the west and south. To the east, on the opposite side of Bathurst Road, is Memory Park, a public recreation area. To the southeast, on the opposite side of Eyles Street is a BP Truckstop.
The nearest noise sensitive receptors to the property, in various directions, are shown in Figure 1 and as follows in Table 1.
Table1 NoiseSensitiveReceptors
ReceptorandType AddressDirectionfrom
site
R1 – Residential 23 Eyles Street South
R2 – Residential 88 McLachlan Street West
R3 – Residential 94 McLachlan Street West
R4 – Residential 50 Bathurst Road West
R5 – Passive Recreation Memory Park East
R6 – Commercial 56-60 Bathurst Road Southeast
Receptor locations are considered representative of all adjacent receptor locations in the immediate area. Compliance at these locations ensures compliance at all other nearby receptors.
Mc Duck Properties Pty Ltd Page 7 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
Figure1–LocationPlan;52‐54BathurstRoad,Orange,NSW
R4
R1
R6
R5
Subject Site R2
R3
A
B
Mc Duck Properties Pty Ltd Page 8 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
NOISESURVEYINSTRUMENTATION
Noise level measurements and analysis were made with instrumentation as follows in Table 2:
Table2 NoiseInstrumentation
Description ModelNo. SerialNo.
Infobyte Noise Logger
Condenser Microphone 0.5” diameter
iM4
MK 250
107
107
Infobyte Noise Logger
Condenser Microphone 0.5” diameter
iM4
MK 250
121
6595
An environmental noise logger is used to continuously monitor ambient noise levels and provide information on the statistical distribution of noise during an extended period of time. The Infobyte Noise Monitor iM4 is a Type 1/Type 2 (#107/#121) precision environmental noise monitor meeting all the applicable requirements of AS1259 for an integrating-averaging sound level meter.
All instrument systems had been laboratory calibrated using instrumentation traceable to Australian National Standards and certified within the last two years thus conforming to Australian Standards. The measurement system was also field calibrated prior to and after noise surveys. Calibration drift was found to be less than 1 dB for long term measurements. No adjustments for instrument drift during the measurement period were warranted.
Mc Duck Properties Pty Ltd Page 9 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
MEASUREDAMBIENTNOISELEVELS
4.1 LongTerm,UnattendedNoiseMonitoring
In order to assess the severity of a possible environmental noise problem in a residential area it is necessary to measure the ambient background noise level at the times and locations of worst possible annoyance. The lower the background noise level, the more perceptible the intrusive noise becomes and the more potentially annoying.
The ambient L90 background noise level is a statistical measure of the sound pressure level that is exceeded for 90% of the measuring period (typically 15 minutes).
The Rating Background Level (RBL) is defined by the NSW EPA as the median value of the (lower) tenth percentile of L90 ambient background noise levels for day, evening or night periods, measured over a number of days during the proposed days and times of operation.
Two environmental noise loggers were placed on site along the west boundary from Tuesday 25 February to Tuesday 3 March 2020 to determine the Rating Background Level in the area. Their locations are shown on Figure 1 below as Location ‘A’ and Location ‘B’.
While placing noise loggers, the author noted that the residential dwelling at ‘R4’ was elevated above the ground level of the subject site. East and south facing windows of this dwelling had clear line of sight to Bathurst Road and the BP Truckstop above the existing fence.
The author also observed that the west boundary fence was comprised of sections of Colorbond fence (‘R3’ & ‘R4’), chain link fence and a timber paling fence in a poor state of repair. As such, the receptors to the west of the subject site (along McLachlan Street) have little shielding from road traffic noise from Bathurst Road and vehicle movements from the BP Truckstop.
The fence on the southern boundary of the site (‘R1’) was noted to comprise a 1.8 metre Colorbond fence in reasonable state of repair. However, the east façade is fully exposed to road traffic noise from Bathurst Road and vehicle movements from the BP Truckstop.
Mc Duck Properties Pty Ltd Page 10 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
The measured noise levels are presented in the attached Appendix A and also in Table 3 below.
Table3 AmbientNoiseLevels
NoiseMeasurementLocation
TimePeriodAmbientLeqNoiseLevel
RatingBackgroundLevel
Location ‘A’ –
52-54 Bathurst Rd,
Orange
Day (7 am – 6 pm) 57 dBA 48 dBA
Evening (6 pm – 10 pm) 56 dBA 45 dBA
Early Night (10 pm – 11 pm) 54 dBA 42 dBA
Night (12 am – 7 am) 53 dBA 33 dBA
Location ‘B’ –
25 Eyles St,
Orange
Day (7 am – 6 pm) 56 dBA 48 dBA
Evening (6 pm – 10 pm) 57 dBA 48 dBA
Early Night (10 pm – 11 pm) 54 dBA 46 dBA
Night (12 am – 7 am) 52 dBA 37 dBA
Meteorological conditions during the testing typically consisted of clear skies with temperature of 6°C to 30°C. Atmospheric conditions were generally ideal for noise monitoring, therefore noise measurements were considered reliable and typical for the receptor area.
Mc Duck Properties Pty Ltd Page 11 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
ACCEPTABLENOISELEVELS
5.1 NSWNoisePolicyforIndustry
The Environment Protection Authority (EPA) published their NSW Noise Policy for Industry (NPI) in October 2017. The NPI is specifically aimed at assessing noise from industrial noise sources scheduled under the Protection of the Environment Operations Act 1997 (POEO, 1997).
The proposed restaurant is not a ‘scheduled premises’ under the Protection of the Environment Operations Act 1997 as it is not required to hold a licence under that Act for operations at the site.
The appropriate regulatory authority (Council) may, by notice in writing given to such a person, prohibit the person from causing, permitting or allowing:
(a) any specified activity to be carried on at the premises, or
(b) any specified article to be used or operated at the premises,
or both, in such a manner as to cause the emission from the premises, at all times or on specified days, or between specified times on all days or on specified days, of noise that, when measured at any specified point (whether within or outside the premises,) is in excess of a specified level.
The NPI provides a useful framework to assess noise emission from non-scheduled premises, whether that premises produces intrusive or non-intrusive noise.
While the NPI is not strictly applicable to this site, as the site is not scheduled, in the absence of other relevant standards the limits set out in the NSW Noise Policy for Industry will be used as a guide in determining whether the level of noise is considered intrusive or not.
Mc Duck Properties Pty Ltd Page 12 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
5.2 IntrusivenessCriteria
The EPA states in Section 2.3 of its NSW Noise Policy for Industry that the Leq level of noise intrusion from broad-band industrial noise sources may be up to 5 dB above the L90 background noise level at the receptor without being considered intrusive.
The L90 Rating Background Level at Location ‘A’ was 48 dBA in the day, 45 dBA in the evening and 42 dBA during the early night.
Location ‘A’ is considered representative of residential premises with facades exposed to Bathurst Road.
The acceptable Leq noise intrusiveness criteria for these receptor locations is:
(48 + 5 =) 53 dBAduring the day;
(45 + 5 =) 50 dBAin the evening; and
(42 + 5 =) 47 dBAduring the early night.
The L90 Rating Background Level at Location ‘B’ was 48 dBA in the day, 48 dBA in the evening and 46 dBA during the early night.
Location ‘B’ is considered representative of the noise levels at facades of residential receptor locations with partial exposure to road traffic noise from Bathurst Road and from vehicle movements from the BP Truckstop.
The acceptable Leq noise intrusiveness criteria for these receptor locations is:
(48 + 5 =) 53 dBAduring the day;
(48 + 5 =) 53 dBAin the evening; and
(46 + 5 =) 51 dBAduring the early night.
Mc Duck Properties Pty Ltd Page 13 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
5.3 AmenityCriteria
Depending on the type of area in which the noise is being made, there is a certain reasonable expectancy for noise amenity. The NSW NPIprovides a schedule of recommended Leq industrial noise levels that under normal circumstances should not be exceeded. If successive developments occur near a residential area, each one allowing a criterion of background noise level plus 5 dB, the ambient noise level will gradually creep higher.
The recommended Leq noise levels below in Table 4 are taken from Section 2.4, Table 2.2 of the NPI.
Table4 AmenityCriteria
TypeofReceiver NoiseAmenityArea TimeofDay
RecommendedLeqNoiseLevel,
dBA
Residence Urban1
Day 60
Evening 50
Night 45
Commercial premises All When in use 65
Passive Recreation Area All When in use 50
The LAeq is determined over a 15-minute period for the project intrusiveness noise level and over an assessment period (day, evening and night) for the project amenity noise level. This leads to the situation where, because of the different averaging periods, the same numerical value does not necessarily represent the same amount of noise heard by a person for different time periods. To standardise the time periods for the intrusiveness and amenity noise levels, the NPI assumes that the LAeq,15minwill be taken to be equal to the LAeq,period+3decibels(dB).
Compliance with the amenity criteria will limit ambient noise creep. Wherever the existing Leq noise level from industrial noise sources approaches or exceeds the amenity criteria at a critical receptor location, the intrusive Leq noise from the noise source in question must be reduced to a level that may be as much as 10 dB below the existing Leq industrial noise level.
The acceptable Leq amenity criteria for this area is:
(60 – 5 + 3 dB =) 58 dBAduring the day;
(50 – 5 + 3 dB =) 48 dBAin the evening; and
(45 – 5 + 3 dB =) 43 dBAat night.
1 Receiver category determined in accordance with Table 2.3 of the NPI.
Mc Duck Properties Pty Ltd Page 14 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
5.4 SleepDisturbance
The Noise Policy for Industry provides the following guidance (NPI, Section 2.5) for setting appropriate trigger levels for sleep disturbance:
‘Sleepdisturbanceisconsideredtobebothawakeningsanddisturbancetosleepstages.Wherethesubjectdevelopment/premisesnight‐timenoiselevelsataresidentiallocationexceed:
LAeq,15min40dB(A)ortheprevailingRBLplus5dB,whicheveristhegreater,and/or
LAFmax52dB(A)ortheprevailingRBLplus15dB,whicheveristhegreater,
adetailedmaximumnoiseleveleventassessmentshouldbeundertaken.’
It is proposed that the restaurant will operate up to 11 pm, on Friday and Saturday night. Vehicles may use the drive-thru facility during the early night period. We have considered the potential for sleep disturbance upon residents in adjacent residential dwellings from various noise producing facets of the operation.
5.5 ProjectSpecificNoiseEmissionCriteria
With consideration to the aforementioned documents and policies, the acceptable Leq noise criteria for ‘R4’ and other residential premises facing Bathurst Road, is therefore:
53 dBAduring the day;
48 dBAin the evening;
43 dBAduring the early night;
57 dBA Lmax trigger noise level for sleep disturbance (at nearest affected façade).
With consideration to the aforementioned documents and policies, the acceptable Leq noise criteria for ‘R1’ – ‘R3’ and other residential premises facing Eyles Street and within rear yards of residential premises facing McLachlan Street, is therefore:
53 dBAduring the day;
48 dBAin the evening;
43 dBAduring the early night.;
61 dBA Lmax trigger noise level for sleep disturbance (at nearest affected façade).
These criteria are to be assessed at the most affected point on or within the residential property boundary during the day, evening and night respectively.
Mc Duck Properties Pty Ltd Page 15 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
NOISEEMISSION
The main sources of noise from these premises will be traffic and the mechanical plant which will include air conditioning condensers and exhaust fans, some of which may operate continuously while the restaurant is operating during trading hours.
6.1 PlantNoiseEmission
Specific items of plant have yet to be finalised, however, for the purposes of this assessment, we have assumed an equipment list used in previous Environmental Noise Assessments typically installed in similar restaurant fitouts prepared by Day Design. A schedule of the sound power levels and the item of plant those levels are based on, is shown in Table 5.
Table5 ScheduleofMechanicalPlantSoundPowerLevels
Description dBASoundPowerLevels(dB)
atOctaveBandCentreFrequencies(Hz)
63 125 250 500 1k 2k 4k 8k
Toilet Exhaust Fantech – TD-250/100
53 50 59 51 52 48 44 36 28
Kitchen Exhaust Fantech - CGD354M-MM
72 79 77 73 70 61 63 62 52
Kitchen Make-up Fantech - PCD454
73 72 74 74 72 68 62 60 51
Wash Up Exhaust Fantech - CE192V
67 68 69 69 66 59 58 56 49
Outdoor AC Condenser Unit
Mitsubishi PUHY-P1000YNW-A 75 97 78 76 74 68 65 62 57
Knowing the sound power level of a noise source (see above Table 5), the sound pressure level (as measured with a sound level meter) can be calculated at a remote location using suitable formulae to account for distance losses, sound barriers, etc.
Mc Duck Properties Pty Ltd Page 16 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
6.2 CarParkandDrive‐ThruNoiseEmission
Car parking will be provided for 25 cars. A loading bay is also provided on the south side of the building for deliveries.
The NSW Roads and Traffic Authority Published the ‘GuidetoTrafficGeneratingDevelopments’ in 2002 and provides estimates for traffic generation for various development situations, including fast food restaurants such as McDonalds and KFC. For KFC restaurants, The Guide advises an average evening peak hour vehicle trip rate of 100 vehicles per hour.
For the purposes of this noise assessment, we have conservatively assumed a trip rate of 25 passenger vehicle trips within any given 15 minute noise assessment period, equivalent to a typical KFC restaurant.
Day Design has had the opportunity to measure the noise level from a range of vehicles travelling at various speeds. Average LAE and Lmax sound power level for vehicles travelling at 10km/h has been determined from these measurements.
The LAE and Lmax sound power levels for vehicle movements within the carpark used in this noise assessment are shown in Table 6.
Table6 SoundPowerLevelsofCarParkNoise
Description dBA
SoundPowerLevels(dB)atOctaveBandCentreFrequencies(Hz)
63 125 250 500 1k 2k 4k 8k
Car drive by at 10km/h – LAE 82 86 82 78 77 78 73 70 64
Car doors closing – Lmax 92 98 92 90 88 88 83 80 76
Truck manoeuvring – LAE 98 102 99 94 96 96 92 88 83
Truck manoeuvring – Lmax 101 113 102 98 95 97 94 92 96
Mc Duck Properties Pty Ltd Page 17 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
6.3 DriveThruNoiseEmission
Day Design has previously measured the noise levels generated by speaker boxes at other similar restaurants with drive-thru ordering facilities.
The LAE and Lmax sound power levels of noise from a typical speaker box are shown in Table 7 below.
Table7 SoundPowerLevelsofDrive‐ThruSpeakerBox
Description dBA
SoundPowerLevels(dB)atOctaveBandCentreFrequencies(Hz)
63 125 250 500 1k 2k 4k 8k
Speaker Box - LAE 72 78 76 69 70 68 65 56 53
Speaker Box - Lmax 84 86 85 79 82 79 77 66 69
Mc Duck Properties Pty Ltd Page 18 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
CALCULATEDNOISELEVELS
Noise levels have been calculated at the nearest receptor locations surrounding the subject site. We have assumed that all items of mechanical plant listed in Table 5 are operating continuously and simultaneously. We have assumed that supply and exhaust fans are located on the roof of the restaurant building with outdoor air conditioning condenser units located in the plant area at ground floor level.
We have included noise attenuation for rooftop plant from a 1 metre high parapet wall on the perimeter of the building. The plant area is assumed to be constructed in accordance with the recommendations provided in Section 8.
We have also assumed a traffic flow rate of up to 25 vehicles entering or leaving the site within any given 15 minute period during operating hours (10 am – 11 pm). We have conservatively assumed that within this 15 minute period, 5 vehicles will enter/leave the carpark areas from the Eyles Street and Bathurst Road driveways and 15 vehicles within the drive-thru driveway, travelling at 10km/h.
We have assumed that the recommendations for fences on boundaries and drive-thru areas have been constructed in accordance with the recommendations provided in Section 8.
We have assumed that all items of plant have sound power levels at or below those specified in Table 5.
We have conservatively assumed that the speaker box will be active for a total of 3 minutes within any given 15 minute assessment period with the remaining period comprising customers talking or not in use as customer vehicles are waiting or moving through the queue.
For nearby residential receptors the noise levels have been assessed at ground floor level at the nearest/most affected façade.
With the aforementioned assumptions, cumulative noise levels at each residential receptor location is as calculated in Table 8 in comparison with the most stringent early night time noise criterion relevant to the operation, established in Section 5. Compliance with the early night criterion ensures compliance at all other times during the day and evening periods.
Table8 CalculatedLeq,15minuteNoiseLevelsatReceptorLocations
ReceptorLocationCalculatedLeq,15minute
NoiseLevelAcceptableLeq,15minute
NoiseLevelCompliance
‘R1’ – Residential 40 dBA 43 dBA Yes
‘R2’ – Residential 37 dBA 43 dBA Yes
‘R3’ – Residential 40 dBA 43 dBA Yes
‘R4’ – Residential 39 dBA 43 dBA Yes
Mc Duck Properties Pty Ltd Page 19 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
With the aforementioned assumptions, cumulative noise levels at each non-residential receptor location (‘R5’ and ‘R6’) is as calculated in Table 9 in comparison with the NPI Amenity criterion applicable for each receptor type, as established in Section 5.
Table9 CalculatedLeq,15minuteNoiseLevelsatNon‐ResidentialReceptorLocations(R5‐R6)
ReceptorLocationCalculatedLeq,15minute
NoiseLevelAcceptableLeq,15minute
NoiseLevelCompliance
‘R5’ – Passive Recreation Area
35 dBA 50 dBA Yes
‘R6’ – Commercial 38 dBA 65 dBA Yes
7.1 SleepDisturbance
With the aforementioned assumptions, Lmax noise levels from various noise producing facets of the restaurant is as calculated at each residential receptor location in Tables 10 and 11 in comparison with the NPI sleep disturbance criterion.
Table10 CalculatedLmaxNoiseLevelsatResidentialReceptorLocations–R1‐R2
NoiseEventCalculatedLmaxNoise
LevelAcceptableLmaxNoise
LevelCompliance
‘R1’–23EylesStreet
Vehicles – Eyles St Up to 56 dBA
61 dBA
Yes
Vehicles – Bathurst Rd Up to 42 dBA Yes
Vehicles – In Drive-Thru
Up to 53 dBA Yes
Speaker Boxes Up to 48 dBA Yes
‘R2’–88McLachlanStreet
Vehicles – Eyles St Up to 40 dBA
61 dBA
Yes
Vehicles – Bathurst Rd Up to 32 dBA Yes
Vehicles – In Drive-Thru Up to 52 dBA Yes
Speaker Boxes Up to 44 dBA Yes
Mc Duck Properties Pty Ltd Page 20 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
Table11 CalculatedLmaxNoiseLevelsatResidentialReceptorLocations–R3‐R4
NoiseEventCalculatedLmaxNoise
LevelAcceptableLmaxNoise
LevelCompliance
‘R3’–94McLachlanStreet
Vehicles – Eyles St Up to 38 dBA
61 dBA
Yes
Vehicles – Bathurst Rd Up to 36 dBA Yes
Vehicles – In Drive-Thru Up to 55 dBA Yes
Speaker Boxes Up to 42 dBA Yes
‘R4’–50BathurstRoad
Vehicles – Eyles St Up to 55 dBA
57 dBA
Yes
Vehicles – Bathurst Rd Up to 31 dBA Yes
Vehicles – In Drive-Thru Up to 55 dBA Yes
Speaker Boxes Up to 36 dBA Yes
Mc Duck Properties Pty Ltd Page 21 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
NOISECONTROLRECOMMENDATIONS
In order to meet the most stringent early night time noise criterion at the nearest residential receptor locations, we recommend that the following be incorporated into the design of the new restaurant:
AcousticFences/Barriers
Acoustic fences should be constructed along the west boundary of the site extending approximately 35 metres from the northern most point to the north building line. This section of fence shall be constructed to a minimum height of 2.4 metres above the ground level of the drive-thru driveway, as shown in Appendix B.
Acoustic fences shall be constructed for the remainder of the west boundary and the southern boundary to a minimum height of 1,8 metres above the ground level of the drive-thru driveway, as shown in Appendix B.
The plant area should be constructed from an acoustically opaque material, such as Colorbond, lapped and capped timber, masonry etc, to a height of either 1.8 metres above ground level of the plant area or at least 600 mm above the tallest item of plant (whichever is the greater).
The level of noise attenuation from a fence (or barrier) is dependent on the difference between the length of the noise transmission path over the fence in comparison with the direct path length from source to receiver. The higher the fence, the greater path length difference and therefore, better noise reduction performance. The level of noise passing through a barrier or fence, is typically negligible compared to the residual noise travelling over a fence to the receiver location.
As such, the material the fence is constructed from is less critical than the overall height of the fence and that there are no holes or gaps between panels or between the ground and underside of the fence where noise can leak through. Acoustic fences may be constructed from any solid material such as Colorbond sheet, lapped and capped timber, masonry, fibre cement, glass or any combination of these materials.
MechanicalPlantSelection
The total sound power level of plant installed within the plant area should be no greater than 76 dBA.
The total sound power of all rooftop plant shall not exceed 85 dBA.
SpeakerBox
The total sound power level of the speaker boxes shall not exceed 73 dBA.
ManagementControls
Truck deliveries to the site shall be scheduled to occur during day time hours only (7 am – 6 pm).
Mc Duck Properties Pty Ltd Page 22 of 22
Environmental Noise Assessment
Ref: 6934-1.1R 13-Mar-20
NOISEIMPACTSTATEMENT
Day Design Pty Ltd was engaged by Mc Duck Properties Pty Ltd to carry out an environmental noise impact assessment for a proposed Taco Bell restaurant to be constructed at 52-54 Bathurst Road, Orange, NSW.
Measurements and calculations show that, provided the recommended noise controls outlined in Section 8 of this report are implemented into the design, the level of noise emitted by the proposed Taco Bell restaurant will meet the requirements of the NSW Environment Protection Authority, as detailed in Section 5 of this report.
AlexanderMendoza, MDesSc (Audio & Acoustics), MAAS
Acoustic Consultant
for and on behalf of Day Design Pty Ltd
AAACMEMBERSHIPDay Design Pty Ltd is a member company of the Association of Australasian Acoustical Consultants, and the work herein reported has been performed in accordance with the terms of membership.
Attachments: Appendix A – Ambient Noise Survey Appendix B – Acoustic Fence Heights Appendix C – Architectural Drawings AC108-1 to 4 – Glossary of Acoustical Terms
AMBIENT NOISE SURVEY 6934‐1Appendix A1
DAY DESIGN PTY LTD
20
30
40
50
60
70
80
00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00
Noise Lev
el (d
BA)
Time (hh:mm)
L10 Leq L90
Tuesday, 25 February 2020
Wednesday, 26 February 2020
Thursday, 27 February 2020
Friday, 28 February 2020
Saturday, 29 February 2020
Sunday, 1 March 2020
Monday, 2 March 2020
Located at 52-54 Bathurst Road, Orange, NSWTuesday, 3 March
2020
AMBIENT NOISE SURVEY 6934‐1Appendix A2
DAY DESIGN PTY LTD
20
30
40
50
60
70
80
00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00 06:00 12:00 18:00 00:00
Noise Lev
el (d
BA)
Time (hh:mm)
L10 Leq L90
Tuesday, 25 February 2020
Wednesday, 26 February 2020
Thursday, 27 February 2020
Friday, 28 February 2020
Saturday, 29 February 2020
Sunday, 1 March 2020
Monday, 2 March 2020
Located at 25 Eyles Street, Orange, NSWTuesday, 3 March
2020
PROPOSED FASTFOOD OUTLETapprox 258 sqm
FFL.866.75
S E
W
E
R
M
A
I N
U
N
D
E
R
EXISTING STREET
TREE TO BE REMOVED
AS SHOWN DOTTED
S I T
E
B
O
U
N
D
A
R
Y
S I T E B O U N D A R Y
S I T E B O U N D A R Y
S
I
T
E
B
O
U
N
D
A
R
Y
LOADING
BAY
S I T E B O U N D A R Y
EX.RL 865.80+RL 865.65+
+EX.RL 865.40
+EX.RL 866.20
EX.RL 867.20+
+RL 865.60
+RL 865.60
+RL 865.75
+RL 866.80
R A M P U P
+RL 866.415 +RL 866.415
R A
M P
U
P
+RL 865.80
+RL 865.80
R A M P U P - 1 : 8.5
+RL 865.65
EX
IS
TIN
G S
IN
GL
E S
TO
RE
Y
DW
EL
LIN
G N
O. 2
3 E
YL
ES
S
T.
EXISTING SINGLE STOREY
DWELLING
NO. 50 BATHURST RD.
EXISTING
GARAGE
NO.94
CAR
PORT
EXISTING
GARAGE
NO. 92
EXISTING GARAGE
NO.50
EXISTING
GARAGE
NO.88
EXISTING DRIVEWAY
+RL 866.60
+RL 866.55
+RL 866.60
+RL 866.60
+RL 866.415
RL 866.60+
RL 866.45+
ENTRY
WS
21
WS WS WS WS WS WS WS WS WS WS
3 4 5 6 87 9 10 11
1213141516171819202122
WS WS WS WS WS WS WS WS WS WS WS
SITE AREA2432sqm
22 Car spaces= Max. 44 seats
2
3
2
4
2
5
WS
WS
WS
PEDESTRIAN
ACCESS
BIKE RACK FOR
8 OFF BIKES
BATHURST RD
EYLES STREET
SITE
EXIT
SITE
ENTRY
STAFF
PARKING
ONLY
STAFF
PARKING
ONLY
STAFF
PARKING
ONLY
RL 866.75+
TOW 866.75+
TOK 865.95+
SITE
EXIT
SITE
ENTRY
EX DRIVEWAY
NEW DRIVEWAY
EXISTING
POWER
POLE
EXISTING
POWER
POLE
PLANT
AREA
DOOR
+RL 865.80
RL866.75+
+RL866.12
TOK865.95+
5255
NEW 1.8m HIGH ACOUSTIC
PANELS ON BOUNDARY.
REFER TO ACOUSTIC REPORT
FOR DETAILS.
EXISTING STREET
TREES TO BE REMOVED
AS SHOWN DOTTED
7800
2450
6200
1225
3000
1100
3000
3100
60001120
1010
4550
EXISTING STORM
WATER MANHOLE
NEW DRIVE THRU ORDERING
STATION CANOPY WITH
SPEAKER, DIGITAL PREVIEW
AND MENU SCREENs
COLORBOND DOWNPIPE
AND RAINWATER HEAD.
RAINWATER TO BE
DRAINED DIRECTLY INTO
RAINWATER TANK
LOCATED INSIDE PLANT
ROOM AT GROUND LEVEL.
REFER TO STORM WATER
DRAWINGS FOR DETAILS
LINE OF
ENTRY
PORTAL
LP
LP
LP
EX
IS
TIN
G S
UB
DIV
IS
IO
N L
IN
E
EX
IS
TIN
G S
UB
DIV
IS
IO
N L
IN
E
6895
COS
+RL 865.80+RL 866.60
TOK 865.80+
TOK 865.75+
TOK 866.75+
+RL 866.44TOK 866.59+
TOK 866.565+
RL 865.65+
TOK 866.75+
+RL 866.60TOK 866.75+
TOK 865.95+
SITE BOUNDARY
NEW ACOUSTIC PANELS
LEGEND
OUTLINE OF NEW
LANDSAPE. REFER TO
LANDSCAPE DRAWINGS
OUTLINE OF
DETENION TANK
BELOW. REFER TO
ENG DRAWING.
EXISTING DRIVEWAY TO
BE REMOVED AS
SHOWN DOTTED
NEW 2.4m HIGH ACOUSTIC
PANELS ON BOUNDARY.
REFER TO ACOUSTIC REPORT
FOR DETAILS.
NEW 1.8m HIGH
ACOUSTIC PANELS
ON BOUNDARY.
REFER TO
ACOUSTIC REPORT
FOR DETAILS.
NEW
TREE
EX
TREE
EX
TREE
EX
TREE
EX
TREE
EX
TREE
EX
TREE
EX
TREE
+RL 866.39 +RL 866.39+RL 866.39
+RL 866.39
+RL 866.35
+RL 865.40
+RL 865.60+RL 866.10
+RL 866.60
+RL 866.60
150 DP150 DP150 DP
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
+RL 866.44
SHARED ZONE
FOR ACCESSIBLE
CAR SPACE
LP
LINE OF DRIVE-THRU
AWNING ABOVE
1182
023
125
2505
5500
7550
5500
2070
B
A
138306685
2160029345 35235
4105 3665
1 2
SITE PLAN
1:250 @ A3 DA01 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
COVERPAGE & LOCATION
NTS @ A3 DA00 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
PLAN
DRAWING LIST
DA00 COVER PAGE & LOCATION PLAN
DA01 SITE PLAN
DA02 SITE TRAFFIC PLAN
DA03 PROPOSED FLOOR PLAN
DA04 ROOF PLAN
DA05 ELEVATIONS SHEET 1
DA06 ELEVATIONS SHEET 2
DA07 BOUNDARY ELEVATIONS
DA08 SECTIONS
DA09 SIGNAGE PLAN
DA10 SIGNAGE DETAILS - SHEET 01
DA11 SIGNAGE DETAILS - SHEET 02
DA12 EXTERNAL FINISHES
TACO BELL ORANGE52-54 BATHURST ROAD, ORANGE NSW 2800
SITE LOCATION52-54 BATHURST ROADORANGENSW 2800
PROPOSED FASTFOOD OUTLETapprox 258 sqm
FFL.866.75
S E
W
E
R
M
A
I N
U
N
D
E
R
EXISTING STREET
TREE TO BE REMOVED
AS SHOWN DOTTED
S I T
E
B
O
U
N
D
A
R
Y
S I T E B O U N D A R Y
S I T E B O U N D A R Y
S
I
T
E
B
O
U
N
D
A
R
Y
LOADING
BAY
S I T E B O U N D A R Y
EX.RL 865.80+RL 865.65+
+EX.RL 865.40
+EX.RL 866.20
EX.RL 867.20+
+RL 865.60
+RL 865.60
+RL 865.75
+RL 866.80
R A M P U P
+RL 866.415 +RL 866.415
R A
M P
U
P
+RL 865.80
+RL 865.80
R A M P U P - 1 : 8.5
+RL 865.65
EX
IS
TIN
G S
IN
GL
E S
TO
RE
Y
DW
EL
LIN
G N
O. 2
3 E
YL
ES
S
T.
EXISTING SINGLE STOREY
DWELLING
NO. 50 BATHURST RD.
EXISTING
GARAGE
NO.94
CAR
PORT
EXISTING
GARAGE
NO. 92
EXISTING GARAGE
NO.50
EXISTING
GARAGE
NO.88
EXISTING DRIVEWAY
+RL 866.60
+RL 866.55
+RL 866.60
+RL 866.60
+RL 866.415
RL 866.60+
RL 866.45+
ENTRY
WS
21
WS WS WS WS WS WS WS WS WS WS
3 4 5 6 87 9 10 11
1213141516171819202122
WS WS WS WS WS WS WS WS WS WS WS
SITE AREA2432sqm
22 Car spaces= Max. 44 seats
2
3
2
4
2
5
WS
WS
WS
PEDESTRIAN
ACCESS
BIKE RACK FOR
8 OFF BIKES
BATHURST RD
EYLES STREET
SITE
EXIT
SITE
ENTRY
STAFF
PARKING
ONLY
STAFF
PARKING
ONLY
STAFF
PARKING
ONLY
RL 866.75+
TOW 866.75+
TOK 865.95+
SITE
EXIT
SITE
ENTRY
EX DRIVEWAY
NEW DRIVEWAY
EXISTING
POWER
POLE
EXISTING
POWER
POLE
PLANT
AREA
DOOR
+RL 865.80
RL866.75+
+RL866.12
TOK865.95+
5255
NEW 1.8m HIGH ACOUSTIC
PANELS ON BOUNDARY.
REFER TO ACOUSTIC REPORT
FOR DETAILS.
EXISTING STREET
TREES TO BE REMOVED
AS SHOWN DOTTED
7800
2450
6200
1225
3000
1100
3000
3100
60001120
1010
4550
EXISTING STORM
WATER MANHOLE
NEW DRIVE THRU ORDERING
STATION CANOPY WITH
SPEAKER, DIGITAL PREVIEW
AND MENU SCREENs
COLORBOND DOWNPIPE
AND RAINWATER HEAD.
RAINWATER TO BE
DRAINED DIRECTLY INTO
RAINWATER TANK
LOCATED INSIDE PLANT
ROOM AT GROUND LEVEL.
REFER TO STORM WATER
DRAWINGS FOR DETAILS
LINE OF
ENTRY
PORTAL
LP
LP
LP
EX
IS
TIN
G S
UB
DIV
IS
IO
N L
IN
E
EX
IS
TIN
G S
UB
DIV
IS
IO
N L
IN
E
6895
COS
+RL 865.80+RL 866.60
TOK 865.80+
TOK 865.75+
TOK 866.75+
+RL 866.44TOK 866.59+
TOK 866.565+
RL 865.65+
TOK 866.75+
+RL 866.60TOK 866.75+
TOK 865.95+
SITE BOUNDARY
NEW ACOUSTIC PANELS
LEGEND
OUTLINE OF NEW
LANDSAPE. REFER TO
LANDSCAPE DRAWINGS
OUTLINE OF
DETENION TANK
BELOW. REFER TO
ENG DRAWING.
EXISTING DRIVEWAY TO
BE REMOVED AS
SHOWN DOTTED
NEW 2.4m HIGH ACOUSTIC
PANELS ON BOUNDARY.
REFER TO ACOUSTIC REPORT
FOR DETAILS.
NEW 1.8m HIGH
ACOUSTIC PANELS
ON BOUNDARY.
REFER TO
ACOUSTIC REPORT
FOR DETAILS.
NEW
TREE
EX
TREE
EX
TREE
EX
TREE
EX
TREE
EX
TREE
EX
TREE
EX
TREE
+RL 866.39 +RL 866.39+RL 866.39
+RL 866.39
+RL 866.35
+RL 865.40
+RL 865.60+RL 866.10
+RL 866.60
+RL 866.60
150 DP150 DP150 DP
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
NEW
TREE
+RL 866.44
SHARED ZONE
FOR ACCESSIBLE
CAR SPACE
LP
LINE OF DRIVE-THRU
AWNING ABOVE
1182
023
125
2505
5500
7550
5500
2070
B
A
138306685
2160029345 35235
4105 3665
1 2
SITE PLAN
1:250 @ A3 DA01 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
vehicle:SERVICE8.8Mgroup:JOHNspeed:6:kphpathUnits:meterstime:2004-08-04-13-54-21display:1,1,1,1,1,1,1,0,1,0,0,0,0color:5,5,0,0,0,2,3,7,4,7,0,7,7style:0,0,0,0,0,0,0,2,0,0,2,0,0fill:0,0clearance:0.000,3.000,3.000spacing:0,2.500level:20,aircraft:N
vehicle:SERVICE8.8Mgroup:JOHNspeed:6:kphpathUnits:meterstime:2004-08-04-13-54-21display:1,1,1,1,1,1,1,0,1,0,0,0,0color:5,5,0,0,0,2,3,7,4,7,0,7,7style:0,0,0,0,0,0,0,2,0,0,2,0,0fill:0,0clearance:0.000,3.000,3.000spacing:0,2.500level:20,aircraft:N
PROPOSED FASTFOOD OUTLETapprox 258 sqm
FFL.866.75
S I T
E
B
O
U
N
D
A
R
Y
S I T E B O U N D A R Y
S I T E B O U N D A R Y
S
I
T
E
B
O
U
N
D
A
R
Y
LOADING
BAY
S I T E B O U N D A R Y
EX.RL 865.80+RL 865.65+
+EX.RL 865.40
+EX.RL 866.20
EX.RL 867.20+
+RL 865.60
+RL 865.60
+RL 865.75
+RL 866.80
R A M P U P
+RL 866.415 +RL 866.415
R A
M P
U
P
+RL 865.80
+RL 865.80
R A M P U P - 1 : 8.5
+RL 865.65
EX
IS
TIN
G S
IN
GLE
S
TO
RE
Y
DW
ELLIN
G N
O. 23 E
YLE
S S
T.
EXISTING SINGLE STOREY
DWELLING
NO. 50 BATHURST RD.
EXISTING
GARAGE
NO.94
CAR
PORT
EXISTING
GARAGE
NO. 92
EXISTING GARAGE
NO.50
EXISTING
GARAGE
NO.88
EXISTING DRIVEWAY
+RL 866.60
+RL 866.55
+RL 866.60
+RL 866.60
+RL 866.415
RL 866.60+
RL 866.45+
ENTRY
WS
21
WS WS WS WS WS WS WS WS WS WS
3 4 5 6 87 9 10 11
1213141516171819202122
WS WS WS WS WS WS WS WS WS WS WS
vehicle:SERVICE8.8Mgroup:JOHNspeed:6:kphpathUnits:meterstime:2004-08-04-13-54-21display:1,1,1,1,1,1,1,0,1,0,0,0,0color:5,5,0,0,0,2,3,7,4,7,0,7,7style:0,0,0,0,0,0,0,2,0,0,2,0,0fill:0,0clearance:0.000,3.000,3.000spacing:0,2.500level:20,aircraft:N
SITE AREA2432sqm
22 Car spaces= Max. 44 seats
2
3
2
4
2
5
WS
WS
WS
PEDESTRIAN
ACCESS
BIKE RACK FOR
8 OFF BIKES
BATHURST RD
EYLES STREETTRUCK ENTRY PATH
TRUCK EXIT PATH
TRUCK REVERSING ZONE
TRUCK PATH LEGEND
7550 CARPARK
LANE WIDTH
2600
TYPICAL
CARSPACE
WIDTH
4000 LOADING
BAY WIDTH
3000
DRIVE THRU
WIDTH AT
ENTRY
2900
MINIMUM
LANDSCAPING
BUFFER ZONE
3000 DRIVE THRU
LANE WIDTH
2600
TYPICAL
CARSPACE
WIDTH
2600
TYPICAL
CARSPACE
WIDTH
SITE
EXIT
SITE
ENTRY
6000
NEW
DRIVEWAY
WIDTH
6
2
0
0
T
W
O
-
W
A
Y
W
I
D
T
H
2600
TYPICAL
CARSPACE
WIDTH
STAFF
PARKING
ONLY
STAFF
PARKING
ONLY
STAFF
PARKING
ONLY
RL 866.75+
TOW 866.75+
TOK 865.95+
SITE
EXIT
SITE
ENTRY
EX DRIVEWAY
NEW DRIVEWAY
EXISTING
POWER
POLE
EXISTING
POWER
POLE
PLANT
AREA
DOOR
+RL 865.80
RL866.75+
+RL866.12
TOK865.95+
LP
LP
LP
8
2
0
0
6
8
9
5
C
O
S
E
X
I
S
T
I
N
G
D
R
I
V
E
W
A
Y
W
I
D
T
H
+RL 865.80+RL 866.60
TOK 865.80+
TOK 865.75+
TOK 866.75+
+RL 866.44TOK 866.59+
TOK 866.565+
RL 865.65+
TOK 866.75+
+RL 866.60TOK 866.75+
TOK 865.95+
+RL 866.39 +RL 866.39+RL 866.39
+RL 866.39
+RL 866.35
+RL 865.40
+RL 865.60+RL 866.10
+RL 866.60
+RL 866.60
150 DP150 DP150 DP
+RL 866.44
SHARED ZONE
FOR ACCESSIBLE
CAR SPACE
LP
TURNING PATHS SHOWN
FOR 8.8m MRV ( MEDIUM
RIGID VEHICLE).
8.8m MRV
8.8m MRV
FOR 8.8m MRV (MEDIUM RIGID VEHICLE)
B
A
1 2
SITE TRAFFIC PLAN
1:250 @ A3 DA02 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
LP
EX
IS
TIN
G S
UB
DIV
IS
IO
N LIN
E
TACO BELLORANGE
TOTAL AREA = APPROX. 258sqm44 SEATS
ENTRY
PATHWAY
LOADING BAY
PLANT ROOM
LINE OF ENTRY
PORTAL
NEW PROPOSED ACOUSTIC
PANELS ON BOUNDARY
DP
LINE OF DRIVE-THRU
AWNING ABOVE
BIKE RACK
LINE OF DRIVE-THRU
AWNING ABOVE
DP DP
DA06
A
DA06
A
DA
06
BD
A06
B
PROPOSED FLOOR PLAN
1:100 @ A3 DA03 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
3° FALL
2° FALL
3° FALL
RITEK ROOF SYSTEM WITH
PROPRIETY FLASHING & CAPPING.
STEEL FRAME AWNING TO
STRUCTURAL ENGINEER DETAILS
3000TOWER
3000
TOWE
R
4800ENTRY PORTAL
PROPRIETY FLASHING &
CAPPING TO PARAPET ROOF
1000
COLORBOND DOWNPIPE AND
RAINWATER HEAD.REFER TO
STORM WATER DRAWINGS
FOR DETAILS
5000 AWNING
3800
AWNI
NG
BOX GUTTER WITH PARAPET
FLASHING + CAPPING
COLORBOND METAL ROOF
SHEETING
PROPRIETY FLASHING & CAPPING
TO PARAPET ROOF.
NEW SIGNAGE TOWER WITH
COLORBOND METAL ROOF
SHEETING. STEEL FRAMING TO
STRUCTURAL ENGINEER DETAILS.
NEW ENTRY PORTAL WITH
COLORBOND METAL ROOF
SHEETING. STEEL FRAMING TO
STRUCTURAL ENGINEER DETAILS.
5000 AWNING
3800
AWNI
NG
3° FALL
3° FALL
2° FALL
WALL LETTER SIGNAGE. REFER TO
DA10 FOR SIGNAGE DETAILS.
TOWER BELL SIGNAGE. REFER TO
DA10 FOR SIGNAGE DETAILS.
DPDPDP
EXPOSED PARAMETER STEEL
BEAM TO ENTRY PORTAL
SITE BOUNDARY LINE
ROOF PLAN
1:100 @ A3 DA04 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
R.L.
GALVANISED EXTERNAL
HANDRAIL TO EDGE OF KERB
ILLUMINATED SIGNAGE BELL
TO TOWER, REFER TO
SIGNAGE DRAWINGS FOR
FURTHER DETAIL
METAL CLADDING TO SIGNAGE
TOWER, REFER TO EXTERNAL
FINISHES SCHEDULE
NON ILLUMINATED LETTER SIGNAGE TO
ENTRY PORTAL, REFER TO SIGNAGE
DRAWINGS FOR FURTHER DETAIL
PAINTED FC SHEET EXTERNAL CLADDING
TO ENTRY PORTAL
EXPOSED STEEL FRAME TO
PERIMETER EDGE OF ENTRY
PORTAL IN PAINT FINISH
TIMBER CLADDING TO EXTERNAL WALLS,
REFER TO EXTERNAL FINISHES SCHEDULE
POWDERCOATED ALUMINIUM FRAMED
WINDOWS, REFER TO EXTERNAL FINISHES
SCHEDULE
FC SHEET CLAD CANTILVERED AWNING
TO EXTERNAL WALL IN PAINT FINISH
NON ILLUMINATED LETTER SIGNAGE TO
ENTRY PORTAL, REFER TO SIGNAGE
DRAWINGS FOR FURTHER DETAIL
2.4M. HIGH SLATTED ALUMINIUM
FENCE AROUND PLANT AREA TO REAR
OF LOADING BAY
LINE OF EXISTING GROUND ALONG EYLES ST.
BOUNDARY
EDGE OF RAISED CARPARK KERB ALONG
EYTLES ST.
FC SHEET CLADDING TO
ENTRY DOOR NIB WALLS IN
PAINT FINISH
RAMP DOWN TO BATHURST
RD. ENTRY / EXIT
POWDERCOATED ALUMINIUM
FRAMED SLIDING ENTRY
DOORS, REFER TO EXTERNAL
FINISHES SCHEDULE
ENTRY PORTAL SIDES IN
METAL CLADDING, REFER TO
EXTERNAL FINISHES
SCHEDULE
R.L. 866.75
BOUN
DARY
R.L. R.L.
FREE STANDING DRIVE-THRU STEEL FRAMED
AWNINGS
METAL CLADDING TO SIGNAGE TOWER
BEYOND, REFER TO EXTERNAL FINISHES
SCHEDULE
FC SHEET CLAD CANTILVERED AWNING TO
EXTERNAL WALL IN PAINT FINISH
ENTRY PORTAL SIDES IN METAL CLADDING,
REFER TO EXTERNAL FINISHES SCHEDULE
TIMBER CLADDING TO EXTERNAL WALLS,
REFER TO EXTERNAL FINISHES SCHEDULE
NEW 1.8m HIGH ACOUSTIC WALL PANELLING
ON THE BOUNDARY. COLOUR OF PANELS TO
BE DULUX 'WINDSPRAY'. REFER TO
ACOUSTIC REPORT FOR DETAILS.
2.4M. HIGH SLATTED ALUMINIUM
FENCE AROUND PLANT AREA TO REAR
OF LOADING BAY
OUTLINE OF NEW 1.8m HIGH ACOUSTIC WALL
PANELLING ON THE BOUNDARY. COLOUR OF
PANELS TO BE DULUX 'WINDSPRAY'.
REFER TO ACOUSTIC REPORT FOR DETAILS.
NEW METAL AWNING OVER DRIVE-THRU
PAY & PICK UP WINDOWS
SIDE ACCESS DOOR FROM KITCHEN
ROLLER SHUTTER TO BIN STORE
R.L. 866.75R.L. 866.60
3000
3°
550060
0070
00
550060
0070
00
ELEVATIONS SHEET 1
1:100 @ A3 DA05 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
02
-SOUTH ELEVATION
1:100 @A3
01
-EAST ELEVATION
1:100 @A3
550060
0070
00
R.L.
CEMENT COMPOSITE CLADDING TO REAR
EXTERNAL WALLS, REFER TO EXTERNAL
FINISHES SCHEDULE
OUTLINE OF NEW 1.8m HIGH ACOUSTIC WALL
PANELLING ON THE BOUNDARY. COLOUR OF
PANELS TO BE DULUX 'WINDSPRAY'.
REFER TO ACOUSTIC REPORT FOR DETAILS
METAL CLADDING TO SIGNAGE
TOWER, REFER TO EXTERNAL
FINISHES SCHEDULE
TIMBER CLADDING TO
EXTERNAL WALLS, REFER TO
EXTERNAL FINISHES SCHEDULE
NON ILLUMINATED GRAPHIC PANEL AT
DRIVE-THRU WALL BETWEEN SERVICE
WINDOWS. REFER TO SIGNAGE DRAWINGS
FOR FURTHER DETAIL
POWDERCOATED ALUMINIUM FRAMED
DRIVE-THRU 'ORDER' & 'PICK UP'
WINDOWS, REFER TO EXTERNAL
FINISHES SCHEDULE
FC SHEET CLAD
CANTILVERED AWNING TO
EXTERNAL WALL IN PAINT
FINISH
RAMP DOWN TO BATHURST
RD. ENTRY / EXIT
2.4M. HIGH SLATTED ALUMINIUM
FENCE AROUND PLANT AREA TO
REAR OF LOADING BAY
LINE OF EXISTING
NATURAL GROUND LEVEL
ALONG BOUNDARY
MASONRY PLANTER BED
FOR LANDSCAPING
BETWEEN BUILDING AND
CARPARK
NEW METAL AWNING OVER DRIVE-THRU
PAY & PICK UP WINDOWS
R.L. 866.75
R.L. 866.45
BOUN
DARY
POWDERCOATED ALUMINIUM FRAMED
WINDOWS , REFER TO EXTERNAL FINISHES
SCHEDULE
GALVANISED EXTERNAL HANDRAIL TO
EDGE OF KERB
ILLUMINATED SIGNAGE BELLS TO TOWER,
REFER TO SIGNAGE DRAWINGS FOR FURTHER
DETAIL
RAMP UP TO RESTAURANT CAR PARK AND
ENTRY
FC SHEET CLAD CANTILVERED AWNING TO
EXTERNAL WALL IN PAINT FINISH
ILLUMINATED LETTER SIGNAGE TO SIDE WALL,
REFER TO SIGNAGE DRAWINGS FOR FURTHER
DETAIL
NEW METAL AWNING OVER DRIVE-THRU
PAY & PICK UP WINDOWS
TIMBER CLADDING TO EXTERNAL WALLS,
REFER TO EXTERNAL FINISHES SCHEDULE
RAMP DOWN TO BATHURST RD. ENTRY / EXITMASONRY PLANTER BED FOR LANDSCAPING
BETWEEN BUILDING AND CARPARK
NEW 2.4m HIGH ACOUSTIC WALL PANELLING
ON THE BOUNDARY. COLOUR OF PANELS TO
BE DULUX 'WINDSPRAY'. REFER TO ACOUSTIC
REPORT FOR DETAILS.
R.L. 866.75
R.L. 865.45
R.L. 865.80
R.L. 865.90
R.L. 866.60
ENTRY PORTAL SIDES IN METAL CLADDING,
REFER TO EXTERNAL FINISHES SCHEDULE
METAL CLADDING TO SIGNAGE TOWER,
REFER TO EXTERNAL FINISHES SCHEDULE
3000
3°
550060
0070
00
ELEVATIONS SHEET 2
1:100 @ A3 DA06 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
03
-WEST ELEVATION
1:100 @A3
04
-NORTH ELEVATION
1:100 @A3
R.L. 866.75
BOUN
DARY
R.L. 865.80
NEW 1.8m HIGH ACOUSTIC WALL
PANELLING ON THE BOUNDARY.
REFER TO ACOUSTIC REPORT FOR
DETAILS.
BOUN
DARY
70
00
60
00
55
00
BOUN
DARY
NEW 1.8m HIGH ACOUSTIC WALL
PANELLING ON THE BOUNDARY.
REFER TO ACOUSTIC REPORT FOR
DETAILS.
NEW 2.4m HIGH ACOUSTIC
WALL PANELLING TO ALL THE
WAY ON THE BOUNDARY.
REFER TO ACOUSTIC REPORT
FOR DETAILS.
BOUN
DARY
7000
6000
5500
BOUNDARY ELEVATIONS
1:200 @ A3 DA07 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
01
-SOUTH ELEVATION
1:200 @A3
02
-WEST ELEVATION
1:200 @A3
DINING
TIMBER CLADDING TO EXTERNAL WALLS,
REFER TO EXTERNAL FINISHES SCHEDULE
EU9182EP2205
EU9182EP2205
SERVING
NEW 2.1m HIGH ACOUSTIC WALL
PANELLING ALONG THE BOUNDARY.
CONCRETE SLAB
COLORBOND ROOF SHEET
ON TRUSS FRAME
ENTRY
BOUN
DARY
DRIVEWAY
NEW METAL AWNING OVER
DRIVE-THRU PAY & PICK UP WINDOWS
EXISTINGGARAGE
CARPARK
EXISITNG GROUND LINE
FILL TO UNDERSIDE OF SLAB
SHOWN HATCHED
ENTRY PORTAL SIDES IN METAL
CLADDING
PAINTED FC SHEET EXTERNAL
CLADDING TO ENTRY PORTAL
NON ILLUMINATED SIGNAGE TO
ENTRY PORTAL. REFER TO SIGNAGE
DRAWINGS FOR FURTHER DETAILS
3°
5500
EU9182EP2205
EP2206
COOLROOM DINING270032
50
TIMBER CLADDING TO EXTERNAL WALLS,
REFER TO EXTERNAL FINISHES SCHEDULE
TIMBER CLADDING TO
EXTERNAL WALLS, REFER
TO EXTERNAL FINISHES
SCHEDULE
STORES
POWDERCOATED ALUMINIUM WINDOWS
AND SLIDING ENTRY DOORS, REFER TO
EXTERNAL FINISHES SCHEDULE
COLORBOND ROOF SHEETING ON
TRUSS FRAME
FC SHEET CLAD CANTILVERED AWNING
TO EXTERNAL WALL IN PAINT FINISH
LOADING BAY
LANDSCAPELANDSCAPE
FILL TO UNDERSIDE OF SLAB SHOWN
HATCHED
LINE OF EXISITNG GROUND LEVEL
SHOWN DASHED
CONCRETE KERB
ST.
OUTLINE OF 2.4M HIGH
LOADING BAY SLATTED
ALUMINIUM FENCE
5500
270032
50
7000
BOUN
DARY
RETAINING WALL
SECTIONS
1:100 @ A3 DA08 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
1
-SECTION A-A
1:100 @A3
2
-SECTION B-B
1:100 @A3
PROPOSED FASTFOOD OUTLETapprox 258 sqm
S E
W
E
R
M
A
I N
U
N
D
E
R
LOADING
BAY
EX
IS
TIN
G S
IN
GL
E S
TO
RE
Y
DW
EL
LIN
G N
O. 2
3 E
YL
ES
S
T.
EXISTING
GARAGE
NO.94
CAR
PORT
EXISTING GARAGE
NO.50
ENTRY
SITE AREA2432sqm
22 Car spaces= Max. 44 seats
BIKE RACK FOR
8 OFF BIKES
BATHURST RD
EYLES STREET
EX DRIVEWAY
NEW DRIVEWAY
PLANT
AREA
LP
LP
LP
150 DP150 DP150 DP
SHARED ZONE
FOR ACCESSIBLE
CAR SPACE
LP
S01
DA10
S02
DA10
S10
DA10
S04
DA10
S11
DA10
S05
DA10
S06
DA10
S12
DA10
S07
DA10
S08
DA10
S14
DA11
S09
DA10
S05
DA10
S06
DA10
S08
DA10
S09
DA10
S03
DA10
S13
DA11
SIGNAGE PLAN
1:200 @ A3 DA09 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
SIGNAGE LEGEND:
NEW ILLUMINATED SIGNAGE
REFER TO DA10 & DA11 FOR SIGNAGE
DETAILS
S--
S01 - NEW ILLUMINATED PYLON SIGN
WITH GRAPHICS ON BOTH SIDES
S02 - NEW NON-ILLUMINATED BANNER
SIGN
S03 - NEW ILLUMINATED DIGITAL
MENUBOARD & ORDER SPEAKER
S04 - NEW ILLUMINATED DIGITAL
PREVIEW MENUBOARD
S05 - NEW ILLUMINATED 2.1M HIGH
'ENTRY' DIRECTIONAL SIGN X2
S06 - NEW ILLUMINATED 2.1M HIGH
'DRIVE-THRU' DIRECTIONAL SIGN
S07 - NEW ILLUMINATED 2.1M HIGH 'NO
ENTRY' DIRECTIONAL SIGN
S08 - NEW ILLUMINATED 2.1M HIGH 'EXIT'
DIRECTIONAL SIGN X2
S09 - NEW ILLUMINATED TOWER
SWINGING BELL SIGN X2
S10 - NEW NON-ILLUMINATED LETTER
FLAT CUT OUT SIGNAGE WITH
MATTE WHITE FINISH
S11 - NEW NON-ILLUMINATED GRAPHIC
PANEL 'LIVE A LIFE STENCIL'
S12 - NEW NON-ILLUMINATED LETTER
FLAT CUT OUT SIGNAGE WITH
MATTE WHITE FINISH
S13 - NEW NON-ILLUMINATED 2.7M HIGH
CLEARANCE BAR
S14 - NEW NON-ILLUMINATED DRIVE
THRU WALL GRAPHIC PANEL
NEW NON-ILLUMINATED SIGNAGE
S--
Drive Thru
500
1820 1640
3640
2873
NEW ILLUMINATED PYLON SIGN WITH
GRAPHICS ON BOTH SIDES.
254
FRONT SIDE
NEW ILLUMINATED DIGITAL DRIVE THRU
PREVIEW BOARD.
NEW ILLUMINATED DIGITAL DRIVE
THRU MENUBOARD
1760
610610
1225
1055
1760
610
1055
705
705
200
ENTRY
700
2100
FRONT SIDE
GROUND LINE
V
I
N
Y
L
B
A
N
N
E
R
B
Y
O
T
H
E
R
S
.
G
R
A
P
H
I
C
S
T
O
F
U
T
U
R
E
D
E
T
A
I
L
3600
185
3050
185
90
155
155
90
90 90
2000
460
1050
2100
NEW ILLUMINATED DIRECTIONAL SIGN WITH
GRAPHICS ON BOTH SIDES.
NEW NON-ILLUMINATED BANNER SIGN
1500
1645 150
350
METAL CANOPY
R.L. 870.35
NEW NON-ILLUMINATEDLETTER-FLAT CUT OUT SIGNAGEWITH MATTE WHITE FINISH FIXEDTO AWNING.
5600
695
2530 2280
5060
76
FRONT SIDE
NEW NON-ILLUMINATED LETTER-FLAT CUT OUT SIGNAGE
WITH MATTE WHITE FINISH TO FRONT AND PURPLE TO SIDE.
S01
DA10NEW PYLON SIGN
SCALE 1:50
S05
DA10
SA05 - SA08
NEW DIRECTIONAL SIGNAGE
SCALE 1:50
S02
DA10NEW BANNER SIGN
SCALE 1:50
S03
DA10NEW DIGITAL MENUBOARD
SCALE 1:50
S09
DA10NEW TOWER SWINGING BELL
SCALE 1:50
S10
DA10NEW LETTER SIGN
SCALE 1:50
S11
DA10NEW GRAPHIC PANEL
SCALE 1:50
S04
DA10NEW DIGITAL PREVIEWBOARD
SCALE 1:50
S12
DA10NEW LETTER SIGN
SCALE 1:50
FRONT SIDE
NEW ILLUMINATED SWINGING BELL SIGN.
FRONT
SIDE
NEW NON-ILLUMINATED LETTER-FLAT CUT OUT
SIGNAGE WITH MATTE WHITE FINISH TO FRONT
AND PURPLE TO SIDE.
30
FRONT SIDE
76
1720
8350
SIGNAGE DETAILS
1:50 @ A3 DA10 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
2961
2859
2489370
102
3051
Clearance 2.7M
NEW NON-ILLUMINATED CLEARANCE BAR
950
1400
7570
WEST FACE ELEVATION
NEW NON-ILLUMINATEDGRAPHIC PANEL
FFL 866.75
S14
DA11NEW GRAPHIC PANEL
SCALE 1:50
S13
DA11NEW DRIVE THRU CLEARNCE BAR
SCALE 1:50
SIGNAGE DETAILS
1:50 @ A3 DA11 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
PROFILED METAL
CLADDING
RANGE: LYSAGHT TRIMDEK
RIB DEPTH: 29MM
COLOUR: COLOURBOND ULTRA, IRONSTONE
PATTERN: HORIZONTAL INSTALLATION
COMPRESSED FIBRE
CEMENT CLADDING
THICKNESS: 8MM
COLOUR RANGE: DULUX EXTERIOR WEATHERSHIELD
COLOUR: GREY
CODE: S45H9
PATTERN: JOINTS TO BE FINISHED WITH SMOOTH
RENDER AND PAINT FINISH
GLAZING
ENTRY SLIDING DOOR,
SHOPFRONT & SIDE WINDOWS
AND PAY/ PICK UP WINDOWS
- CLEAR GLASS / NEUTRAL
- ALUMINIUM POWERCOATED DARK GREY FRAMING
- SILICON JOINTS TO WINDOW FRAMES
DRIVE-THRU METAL AWNING
RANGE: ARCPANEL ECOTEK PANEL ROOF SYSTEM
PANEL THICKNESS: TO BE CONFIRMED BY STRUCTURAL ENGINEER
COLOUR: COLOURBOND ULTRA, IRONSTONE
NOTES:
CONTRACTOR TO PROVIDE PROPRIETY CAPPING & FLASHING WITH
PRESSURE SEAL TO TOP.
TIMBER LOOK
ALUMINIUM CLADDING
RANGE: DECOCLAD SHADOWLINE
SIZE : 200MM BOARD WIDTH X 6.5M LENGTHS
PROFILE: 20MM RECESSED SHADOWLINE
COLOUR: NATURAL WESTERN RED CEDAR
PATTERN: HORIZONTAL INSTALLATION
NOTES:
- PRE PUNCHED FIXING HOLES FOR INSTALLATION.
STRIA CLADDING
PROFILE: 325MM
THICKNESS: 14MM
COLOUR RANGE: DULUX EXTERIOR WEATHERSHIELD
COLOUR: LIMED WHITE QUARTER
CODE: S13B1Q
PATTERN: JOINTS TO BE FINISHED WITH SMOOTH PAINT FINISH
SLATTED
ALUMINIUM FENCE
SYSTEM: HORIZONTAL SPACED FENCING
COLOUR: TERRAIN SATIN
CODE: 2608232S
SUPPLIER: KNOTWOOD
NOTES:
- INSTALL IN ACCORDANCE WITH
MANUFACTURERS INSTRUCTIONS
COMPRESSED FIBRE
CEMENT CLADDING
COLOUR: DULUX WHITECODE: S45H9
COLOUR RANGE: DULUX
EXTERIOR WEATHERSHIELD
PATTERN: JOINTS TO BE FINISHED
WITH SMOOTH RENDER
AND PAINT FINISH
COLORBOBND DOWNPIPE WITH
RAINWATER HEAD
RAINWATER HEAD RADIUS = 450MM AT TOP & 250MM AT NARROW END
DOWNPIPE RADIUS= 150MMCOLOUR RANGE:
COLOUR: DULUX MONUMENT
EXTERNAL FINISHES
1:100 @ A3 DA12 A
TACO BELL ORANGE
20102 MAR 2020
NOTE: WORK TO COMPLY WITH AS 4674 2004CONSTRUCTION & FITOUT OF FOOD PREMISES
52-54 BATHURST RD
project
drawing
project ref datechecked
rev.dwg. no.scale
amendments
date notes rev.
DA ISSUE
Contractor shall verify all levels and dimensions on site prior to
commencing any work or shop drawings. Figured dimensions to be
used - do not scale.
© Copyright. This drawing remains the property of BDAI Pty Ltd.
ACN 973 747 660. The designs, concepts, details and information
described in the drawings are copyright. Other than for the
purposes prescribed under the Copyright Act, no part of it may in
any form or by any means be used or reproduced without prior
permission.
NOMINATEDARCHITECT:MAURICE BERALDONSW Reg 6354VIC Reg 4884
Suite 14, Level 322-36 Mountain StreetUltimo NSW 2007T 02 9281 6177
bdai.com.au
ORANGE, NSW 2800
BK
XX/02/20 DA ISSUE A
GLOSSARY OF ACOUSTICAL TERMS AC108Sheet 1 of 4
DAY DESIGN PTY LTD
ACOUSTICAL–Pertainingtothescienceofsound,includingthegeneration,propagation,effectsandcontrolofbothnoiseandvibration.
AMBIENTNOISE–Theambientnoiselevelataparticularlocationistheoverallenvironmentalnoise level caused by all noise sources in the area, both near and far, including road traffic,factories,windinthetrees,birds,insects,animals,etc.
AUDIBLE – meansthatasoundcanbeheard. However, thereareawiderangeofaudibilitygrades,varyingfrom“barelyaudible”to“justaudible”,“clearlyaudible”and“prominent”.Chapter83oftheNSWEnvironmentProtectionAuthority–EnvironmentalNoiseControlManual(1985)states:“noisefromaparticularsourcemightbeoffensiveifitisclearlyaudible,distinctfromtheprevailingbackgroundnoiseandofavolumeorcharacterthatareasonablepersonwouldbeconsciousoftheintrusionandfinditannoyingordisruptive”.
Itfollowsthattheword“audible”inanenvironmentalnoisecontextmeans“clearlyaudible”.
BACKGROUNDNOISELEVEL–Silencedoesnotexistinthenaturalorthebuilt‐environment,onlyvaryingdegreesofnoise.TheBackgroundNoiseLevelistheaverageminimumdBAlevelofnoisemeasuredintheabsenceofthenoiseunderinvestigationandanyothershort‐termnoisessuchasthosecausedbycicadas,lawnmowers,etc.ItisquantifiedbytheLA90orthedBAnoiselevelthatisexceededfor90%ofthemeasurementperiod(usually15minutes).
AssessmentBackgroundLevel (ABL) is the single figure background level representingeachassessmentperiod–day,eveningandnight(iethreeassessmentbackgroundlevelsaredeterminedforeach24hrperiodofthemonitoringperiod).Determinationoftheassessmentbackgroundlevelisbycalculatingthetenthpercentile(thelowesttenthpercentvalue)ofthebackgroundlevels(LA90)foreachperiod(refer:NSWIndustrialNoisePolicy,2000).
RatingBackgroundLevel(RBL)asspecifiedbytheEnvironmentProtectionAuthorityistheoverallsinglefigure(LA90)backgroundnoiselevelrepresentinganassessmentperiod(day,eveningornight)overamonitoringperiodof(normally)threetosevendays.
TheRBLforanassessmentperiodisthemedianofthedaily lowesttenthpercentileofL90backgroundnoiselevels.
Ifthemeasuredbackgroundnoiselevelislessthan30dBA,thentheRatingBackgroundLevel(RBL)isconsideredtobe30dBA.
DECIBEL–Thehumanearhasavastsound‐sensitivityrangeofoverathousandbilliontoone.Thedecibelisalogarithmicunitthatallowsthissamerangetobecompressedintoasomewhatmorecomprehensiblerangeof0to120dB.Thedecibelistentimesthelogarithmoftheratioofasoundleveltoareferencesoundlevel.SeealsoSoundPressureLevelandSoundPowerLevel.
Decibelnoiselevelscannotbeaddedarithmeticallysincetheyarelogarithmicnumbers. Ifonemachineisgeneratinganoiselevelof50dBA,andanothersimilarmachineisplacedbesideit,thelevelwillincreaseto53dBA,not100dBA.Tensimilarmachinesplacedsidebysideincreasethesoundlevelby10dBA,andonehundredmachinesincreasethesoundlevelby20dBA.
dBA–Thehumanearislesssensitivetolowfrequencysoundthanhighfrequencysound.Wearemostsensitivetohighfrequencysounds,suchasachild’sscream.Soundlevelmetershaveaninbuiltweightingnetwork,termedthedBAscale,thatapproximatesthehumanloudnessresponseatquietsoundlevels(roughlyapproximatesthe40phonequalloudnesscontour).
GLOSSARY OF ACOUSTICAL TERMS AC108Sheet 2 of 4
DAY DESIGN PTY LTD
However, the dBA sound level provides a poor indication of loudness for sounds that aredominated by low frequency components (below 250 Hz). If the difference between the “C”weightedandthe“A”weightedsoundlevelis15dBormore,thentheNSWIndustrialNoisePolicyrecommendsa5dBApenaltybeappliedtothemeasureddBAlevel.
dBC–ThedBCscaleofasoundlevelmeterissimilartothedBAscaledefinedabove,exceptthatathighsoundintensitylevels,thehumanearfrequencyresponseismorelinear.ThedBCscaleapproximatesthe100phonequalloudnesscontour.
EQUIVALENT CONTINUOUS NOISE LEVEL, LAeq – Many noises, such as road traffic orconstructionnoise,varycontinuallyinleveloveraperiodoftime.Moresophisticatedsoundlevelmetershaveanintegratingelectronicdeviceinbuilt,whichaveragetheAweightedsoundpressurelevelsoveraperiodoftimeandthendisplaytheenergyaverageorLAeqsoundlevel.Becausethedecibel scale is a logarithmic ratio the higher noise levels have far more sound energy, andthereforetheLAeqleveltendstoindicateanaveragewhichisstronglyinfluencedbyshortterm,highlevelnoiseevents.Manystudiesshowthathumanreactiontolevel‐varyingsoundstendstorelatecloselytotheLAeqnoiselevel.
FREEFIELD–Thisisasoundfieldnotsubjecttosignificantreflectionofacousticalenergy.Afree fieldoverareflectingplane isusuallyoutdoorswith thenoisesourcerestingonhard flatground,andnotcloserthan6metrestoanylargeflatobjectsuchasafenceorwall;orinsideananechoicchamber.
FREQUENCY–Thenumberofoscillationsorcyclesofawavemotionperunittime,theSIunitbeingtheHertz,oronecyclepersecond.
IMPACTISOLATIONCLASS(IIC)–TheAmericanSocietyforTestingandMaterials(ASTM)hasspecified that the IIC of a floor/ceiling system shall be determined by operating an ISO 140StandardTappingMachineonthefloorandmeasuringthenoisegeneratedintheroombelow.TheIICisanumberfoundbyfittingareferencecurvetothemeasuredoctavebandlevelsandthendeductingthesoundpressurelevelat500Hzfrom110decibels.ThusthehighertheIIC,thebettertheimpactsoundisolation.
IMPACTSOUNDINSULATION(LnT,w)–AustralianStandardASISO717.2–2004hasspecifiedthattheImpactSoundInsulationofafloor/ceilingsystembequantifiedbyoperatinganISO140StandardTappingMachineonthefloorandmeasuringthenoisegeneratedintheroombelow.TheWeightedStandardisedImpactSoundPressureLevel(LnT,w)isthesoundpressurelevelat500Hzforareferencecurvefittedtothemeasuredoctavebandlevels.ThusthelowerLnT,wthebettertheimpactsoundinsulation.
IMPULSENOISE–Animpulsenoiseistypifiedbyasuddenrisetimeandarapidsounddecay,suchasahammerblow,rifleshotorballoonburst.
INTRUSIVENOISELEVEL,LAeq–Thelevelofnoisefromafactory,placeofentertainment,etc.inNSWisassessedonthebasisoftheaveragemaximumnoiselevel,ortheLAeq(15min).ThisistheenergyaverageAweightednoiselevelmeasuredoverany15minuteperiod.
LOUDNESS–Thedegreetowhichasoundisaudibletoalisteneristermedtheloudness.Thehumanearperceivesa10dBAnoiselevelincreaseasadoublingofloudnessanda20dBAnoiseincreaseasaquadruplingoftheloudness.
GLOSSARY OF ACOUSTICAL TERMS AC108Sheet 3 of 4
DAY DESIGN PTY LTD
MAXIMUMNOISELEVEL,LAmax–Thermsmaximumsoundpressurelevelmeasuredonthe"A"scaleofasoundlevelmeterduringanoisesurveyistheLAmaxnoiselevel. ItmaybemeasuredusingeithertheFastorSlowresponsetimeofthemeter.Thisshouldbestated.
NOISE RATING NUMBERS – Asetofempiricallydevelopedequal loudnesscurveshasbeenadoptedasAustralianStandardAS1469‐1983.ThesecurvesallowtheloudnessofanoisetobedescribedwithasingleNRnumber. TheNoiseRatingnumberisthatcurvewhichtouchesthehighestlevelonthemeasuredspectrumofthesubjectnoise.Forbroadbandnoisesuchasfansandengines,theNRnumberoftenequalsthedBAlevelminusfive.
NOISE–Noiseisunwantedsound.Soundiswavemotionwithinmatter,beitgaseous,liquidorsolid.“Noiseincludessoundandvibration”.
NOISEREDUCTIONCOEFFICIENT–See:"SoundAbsorptionCoefficient".
OFFENSIVE NOISE ‐(Reference:DictionaryoftheProtectionoftheEnvironmentOperationsAct1997)."OffensiveNoisemeansnoise:(a) that,byreasonofitslevel,nature,characterorquality,orthetimeatwhichitismade,orany
othercircumstances:(i) isharmfulto(orlikelytobeharmfulto)apersonwhoisoutsidethepremisefromwhich
itisemitted,or(ii) interferesunreasonablywith(orislikelytointerfereunreasonablywith)thecomfortor
reposeofapersonwhoisoutsidethepremisesfromwhichitisemitted,or(b) thatisofalevel,nature,characterorqualityprescribedbytheregulationsorthatismadeata
time,orinothercircumstancesprescribedbytheregulations."
PINKNOISE–Pinknoiseisabroadbandnoisewithanequalamountofenergyineachoctaveorthirdoctavebandwidth.Becauseofthis,PinkNoisehasmoreenergyatthelowerfrequenciesthanWhiteNoiseandisusedwidelyforSoundTransmissionLosstesting.
REVERBERATION TIME, T60 – Thetimeinseconds,afterasoundsignalhasceased,forthesoundlevelinsidearoomtodecayby60dB. Thefirst5dBdecayisoftenignored,becauseoffluctuationsthatoccurwhilereverberantsoundconditionsarebeingestablishedintheroom.Thedecaytimeforthenext30dBismeasuredandtheresultdoubledtodeterminetheT60.TheEarlyDecayTime(EDT)istheslopeofthedecaycurveinthefirst10dBnormalisedto60dB.
SOUND ABSORPTION COEFFICIENT, – Sound is absorbed inporousmaterialsby theviscousconversionofsoundenergytoheatenergyasthesoundwavespassthroughit.Soundissimilarlyabsorbedbytheflexuralbendingofinternallydampedpanels.ThefractionofincidentenergythatisabsorbedistermedtheSoundAbsorptionCoefficient,.Anabsorptioncoefficientof0.9indicatesthat90%oftheincidentsoundenergyisabsorbed.Theaveragefrom250to2000HzistermedtheNoiseReductionCoefficient(NRC).
SOUNDATTENUATION–Ifanenclosureisplacedaroundamachine,orasilencerisfittedtoaduct,thenoiseemissionisreducedorattenuated.Anenclosurethatattenuatesthenoiselevelby30dBA,reducesthesoundenergybyonethousandtimes.
SOUNDEXPOSURELEVEL(SEL)–ThetotalsoundenergyofasinglenoiseeventcondensedintoaoneseconddurationorinotherwordsitisanLeq(1sec).
GLOSSARY OF ACOUSTICAL TERMS AC108Sheet 4 of 4
DAY DESIGN PTY LTD
SOUND PRESSURE LEVEL, Lp – The level of soundmeasuredon a sound levelmeter andexpressedindecibels,dB,dBA,dBC,etc. Lp=20xlog(P/Po)...dB
wherePisthermssoundpressureinPascalandPoisareferencesoundpressureof20µPa. Lpvarieswithdistancefromanoisesource.
SOUNDPOWERLEVEL,Lw–TheSoundPowerLevelofanoisesourceisanabsolutethatdoesnotvarywithdistanceorwithadifferentacousticenvironment.
Lw=Lp+10logA...dB,re:1pW, whereAisthemeasurementnoise‐emissionareainsquaremetresinafreefield.
SOUNDTRANSMISSIONCLASS(STC)–Aninternationallystandardisedmethodofratingthesoundtransmissionlossofpartitionwallstoindicatethedecibelsofnoisereductionofahumanvoicefromonesidetotheother.(Refer:AustralianStandardAS1276–1979)
SOUNDTRANSMISSIONLOSS–Theamountindecibelsbywhicharandomsoundisreducedas it passes through a sound barrier. A method for the measurement of airborne SoundTransmissionLossofabuildingpartitionisgiveninAustralianStandardAS1191‐2002.
STATISTICALEXCEEDENCESOUNDLEVELS,LA90,LA10,LA1,etc–Noisewhichvariesinleveloveraspecificperiodoftime(usually15minutes)maybequantifiedintermsofvariousstatisticaldescriptors:
TheLA90isthedBAlevelexceededfor90%ofthetime.InNSWtheLA90ismeasuredoverperiodsof15minutes,andisusedtodescribetheaverageminimumorbackgroundnoiselevel.
TheLA10isthedBAlevelthatisexceededfor10%ofthetime.InNSWtheLA10measuredoveraperiodof10to15minutes. Itwasuntilrecentlyusedtodescribetheaveragemaximumnoiselevel,buthaslargelybeenreplacedbytheLAeqfordescribinglevel‐varyingnoise.
TheLA1 isthedBAlevelthat isexceededfor1%ofthetime. InNSWtheLA1maybeusedfordescribingshort‐termnoiselevelssuchascouldcausesleeparousalduringthenight.
STEADYNOISE–Noise,whichvariesinlevelby6dBAorless,overtheperiodofinterestwiththetime‐weightingsetto“Fast”,isconsideredtobe“steady”.(ReferAS1055.11997)
WEIGHTEDSOUNDREDUCTIONINDEX,Rw–Thisisasinglenumberratingoftheairbornesoundinsulationofawall,partitionorceiling.Thesoundreductionisnormallymeasuredoverafrequencyrangeof100to3,150HertzandaveragedinaccordancewithISOstandardweightingcurves(ReferAS/NZS1276.1:1999).
InternalpartitionwallRw+Cratingsarefrequencyweightedtosimulateinsulationfromhumanvoicenoise.TheRw+CisalwayssimilarinvaluetotheSTCratingvalue.Externalwalls,doorsandwindowsmaybeRw+Ctrratedtosimulateinsulationfromroadtrafficnoise.ThisisnormallyalowernumberthantheSTCratingvalue.
WHITE NOISE – Whitenoise isbroadbandrandomnoisewhosespectraldensity isconstantacrossitsentirefrequencyrange.Thesoundpoweristhesameforequalbandwidthsfromlowtohighfrequencies.Becausethehigherfrequencyoctavebandscoverawiderspectrum,whitenoisehasmoreenergyatthehigherfrequenciesandsoundslikeahiss.