Road Traffic Noise Assessment - Grange Road and Raymont ... · Executive Summary Brisbane City...

Road Traffic Noise Assessment -Grange Road and Raymont Road Intersection Upgrade ProjectBrisbane City Council

Date of Issue: 31 August 2017

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of 60 Brisbane City Council- Road Traffic Noise Assessment - Grange Road and Raymont Road Intersection Upgrade Project

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Document Details

Project Reference: 4094.8report03.odt

Document Title: Road Traffic Noise Assessment - Grange Road and Raymont Road Intersection

Upgrade Project

Client: Brisbane City Council

Document Reference: /Network/Projects/4094.8/Reporting/4094.8report03.odt

Revision History

Version: Issue Date: Author: Description: Approved by:

00 8/6/17 Samuel Wong Internal Draft -

01 9/6/17 Samuel Wong Draft for Client Beau Weyers

02 17/8/17 Samuel Wong Revised Draft Beau Weyers

03 31/8/17 Samuel Wong Final Beau Weyers

Revision: Issue Date: Author: Details of Revision:

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Executive SummaryBrisbane City Council commissioned Air Noise Environment to undertake a road traffic noise

assessment for the proposed Grange Road and Raymont Road intersection upgrade. The purpose of

the assessment is to quantify existing and future road traffic noise impacts with and without the

upgrade in accordance with the TMR Traffic Noise Management Code of Practice Volume 1 (2013).

The study area consists of single dwelling residential houses along Grange Road and Raymont Road.

The residential houses include single storey and two-storey houses, and houses raised on stilts. In

terms of potential changes to noise levels, the proposed upgrade involves the widening of Grange

Road to provide space for turning lanes onto Raymont Road. The widening of the road will involve

the resumption of land, resulting in road traffic being located closer to nearby houses.

To assess the potential for road traffic noise impacts on the nearest sensitive receptors,

computational noise modelling was completed using the Calculation of Road Traffic Noise (CoRTN)

methodology. The model was verified by comparing predicted 2017 noise levels with road traffic

noise monitoring data obtained in April 2017. Attended noise measurements were also undertaken

which confirmed there were no extraneous noise sources influencing the road traffic noise

measurements. The verification study indicated the model was over-predicting by approximately

3 dB. A minus correction has been applied to the source noise levels for Grange Road to bring the

model within the +/- 2 dB allowable tolerance.

Noise levels for the year 2017 and 2029 (with and without the upgrade) were predicted at the

nearest 50 residential houses for comparison with the TMR noise criteria applicable to upgraded

existing roads. The results of the modelling indicate non-compliance at 27 receptors for the year

2017 and 2029 (10-years from construction). All exceedences are associated with houses located

along Grange Road. Exceedences of up to 7 dB are predicted for the ‘No Upgrade’ scenario and up to

8 dB for the ‘With Upgrade’ scenario.

The proposed upgrade is predicted to result in a 1 dB increase to noise levels at only 5 houses.

These houses are located on the eastern side of Grange Road, closest to the proposed road widening

section. A 1 dB increase is considered a minor increase and would not be discernible to a resident.

No additional houses are predicted to exceed the criteria with the proposed upgrade.



Table of ContentsExecutive Summary 4

1 Introduction 7

1.1 Introduction 7

1.2 This Report 7

2 The Project 8

3 Noise Monitoring 11

3.1 Overview 11

3.2 Noise Monitoring Location 11

3.3 Monitoring Methodology 12

3.4 Weather Conditions 13

3.5 Monitoring Results 14

4 Noise Criteria 15

5 Noise Modelling 16

5.1 Modelling Methodology 16

5.2 Modelling Inputs 16

5.2.1 Traffic Data 16

5.2.2 Road Surface 17

5.2.3 Traffic Speed 18

5.2.4 Topography 18

5.2.5 Ground Absorption 19

5.2.6 Sensitive Receptors 19

5.2.7 Model Corrections 20

5.3 Calibration Results 20

5.4 Modelling Results 21

6 Conclusions 24

Appendix A - Acoustic Glossary 25

Appendix B – Noise Monitoring Field sheets 27

Appendix C – Meteorological Data 38

Appendix D – Noise Contour Plots 56

Index of TablesTable 3.1 - Noise Instrument Calibration Information 13

Table 3.2 - Position 1 - April 2017 - Measured Free-Field Noise Levels dB(A) 14

Table 3.3 - Position 2 - August 2017 - Measured Free-Field Noise Levels dB(A) 14



Table 4.1 - Assessment Noise Criteria 15

Table 5.1 - Modelled Traffic Data – No Upgrade Scenario 17

Table 5.2 - Pavement Surface Corrections 17

Table 5.3 - CoRTN Calibration Factors and Accuracies for Queensland Conditions 20

Table 5.4 - Calibration Results 20

Table 5.5 - Predicted LA10,18-hour Noise Levels (Facade-Corrected) 21

Table C1 - Position 1 Monitoring - Meteorological Data 39

Table C2 - Position 2 Monitoring - Meteorological Data 49

Index of FiguresFigure 2.1 - Project Area 9

Figure 2.2 - Proposed Intersection Upgrade 10

Figure 3.1 - Noise Monitoring Positions 12

Figure 5.1 - Existing Acoustic Barriers 19

Figure D1 - Predicted 2017 Noise Levels – No Upgrade 57

Figure D2 - Predicted 2017 Noise Levels – With Upgrade 58

Figure D3 - Predicted 2029 Noise Levels – No Upgrade 59

Figure D4 - Predicted 2029 Noise Levels – With Upgrade 60



1 Introduction

1.1 Introduction Brisbane City Council commissioned Air Noise Environment to undertake a road traffic noise

assessment for the Grange Road and Raymont Road intersection upgrade located in Grange. The

purpose of the assessment is to quantify existing and future road traffic noise impacts, and identify

noise attenuation strategies for achieving appropriate acoustic outcomes where required.

The assessment has been undertaken in accordance with the Queensland Department of Transport

and Main Roads (TMR) Traffic Noise Management Code of Practice (Volume 1, Road Traffic Noise,

2013).

1.2 This ReportThis report provides the methodology, results and conclusions of the assessment. A glossary of

acoustic terms is provided in Appendix A to assist the reader.



2 The ProjectThe Grange Road and Raymont Road Intersection Upgrade project extends south along Grange Road

from the intersection with Howard Street to the intersection with Dennis Street. The proposed

upgrade will involve the following works:

⚫ realignment of existing through lanes of the right turn lane on Grange Road (north of Raymont

Road) and resumption of land;

⚫ resumption of land on the western side of Grange Road to accommodate changes to left turn

lane on Grange Road (south of Raymont Road).

Residential houses on either side of both Grange Road and Raymont Road represent the nearest

affected sensitive receptors to the project site. The majority of houses are of weatherboard-clad

construction and typically two-storey or raised on stilts. No acoustic barriers are located along the

road frontage, except for one property with a 2 metre concrete blockwork fence and another

property with a wooden fence (no gaps) assumed to perform as acoustic barriers. All other properties

either have no fencing or standard wooden fences (not overlapping).

There is only minor variation in topography across the project area. Grange Road increases in height

slightly from an RL height of 28 metres at the Howard Road intersection to 33 metres at the Dennis

Street intersection. This corresponds to 3% road gradient (5 metres increase over a 180 metre

distance).

Figure 2.1 presents an aerial photo identifying the site of the road upgrade. Figure 2.2 presents a

layout of the proposed upgrade.



Figure 2.1 - Project Area



Figure 2.2 - Proposed Intersection Upgrade



3 Noise Monitoring

3.1 OverviewTo provide a basis for verifying the accuracy of the road traffic noise model, noise monitoring was

undertaken at two central positions along the study area from 18 April to 24 April 2017 and 1 August

to 4 August 2017. In accordance with TMR requirements, a minimum of 48 hours of continuous

logging was undertaken, including coincident short attended noise measurements. A local weather

station was also situated in the area to measure meteorological conditions during the monitoring

period. The following sections present the monitoring methodology and results.

3.2 Noise Monitoring LocationNoise monitoring at Position 1 was completed in April 2017. Position 1 was located immediately north

of the Grange Road and Raymont Road intersection, and setback from Grange at a distance of

approximately 9 metres. The monitor was in a free-field position and had a direct line of sight with

the road traffic. Initial noise model verification results indicated an over-prediction of the

computational model by more than 2 dB, therefore a second round of monitoring was completed in

August 2017. Position 2 is located north of Position 1 in the rear yard of 45 Prince Street. The noise

logger was located in an elevated position and representative of houses raised on stilts. Figure 2.1

identifies the monitoring location.



Figure 3.1 - Noise Monitoring Positions

3.3 Monitoring MethodologyNoise monitoring was undertaken in accordance with AS 2702-1984 Acoustics – Methods for the

measurement of road traffic. An averaging time of 1-hour was used and measurements were made

over a minimum period of 48-hours. The microphones were situated in free field positions and fitted

with a windshield throughout the measurements.

Attended noise monitoring was also undertaken over a 15-minute period at the commencement and

at the end of each continuous monitoring period. The purpose of the attended monitoring was to

confirm that no extraneous noise sources such as construction activity were influencing the

measured road traffic noise levels. Pre- and post-calibration checks were also undertaken at the

commencement and end of the monitoring period.

Instrument details including serial number and calibration information are presented in Table 3.1.



Table 3.1 - Noise Instrument Calibration Information

Instrument/

Serial No.Monitoring Dates NATA Calibration Current to:

Ngara (87809c) 18/4/17 – 24/4/17 14/3/18

B&K2250 Lite (2741105) 18/4/17 and 24/4/17 23/1/19

Nor140 (1404644) 1/8/17 – 4/8/17 12/06/19

B&K2250 Lite (2741104) 1/8/17 and 4/8/17 12/10/17

Pulsar 105 (62686) - 16/11/17

Meteorological monitoring was undertaken using a Davis Vantage Vue Pro Weather Station. The

weather station provided temperature, pressure and average wind speeds continuously with 15-

minute averaging periods.

Due to security reasons at Position 1, the weather station was located at an alternative location to

the noise monitor and obtaining a suitable position, unaffected by surrounding structures, was

problematic (see Figure 3.1). The selected position was within the drip line of nearby trees (therefore,

rainfall data was not considered reliable). While the weather station was located at an alternative

location to Position 1, wind data is still considered representative of the likely wind speeds

experienced at the ground level noise monitoring location and surrounding residential houses. For

the purpose of the assessment, rainfall data has been provided from Brisbane City Council’s

Floodwise data (obtained at a location approximately 1.2 km south-west of Position 1).

During monitoring at Position 2, the weather station was located adjacent to the noise monitor.

3.4 Weather ConditionsThe weather data was analysed to determine whether the noise monitoring may have been

influenced by prevailing meteorological conditions. TMR specifies the following maximum acceptable

values as follows:

⚫ average wind speed up to 3 m/s;

⚫ rainfall up to 0.3 mm/h.

Road traffic noise measurements over a 24 hour period are to be discarded if there are more than

two consecutive hours of adverse weather conditions or more than three non-consecutive hours of

adverse weather conditions. Analysis of the weather monitoring data indicates that during the

monitoring in April and July 2017, no periods were affected by wind or rain. Therefore, all monitoring

data is considered valid for the assessment.



3.5 Monitoring ResultsTable 3.2 presents a summary of the measured LA10,18-hour noise levels for the monitoring period. The

LA10,18-hour noise parameter is defined as the arithmetic average of the LA10,1-hour noise levels between

6 am and midnight. The results are presented for full 24-hour periods of monitoring.

Table 3.2 - Position 1 - April 2017 - Measured Free-Field Noise Levels dB(A)

Date LA10,18-hour

Wednesday 19/04/17 67.4

Thursday 20/04/17 67.0

Friday 21/04/17 67.4

Saturday 22/04/17 67.0

Sunday 23/04/17 65.2

Table 3.3 - Position 2 - August 2017 - Measured Free-Field Noise Levels dB(A)

Date LA10,18-hour

Tuesday 1/8/17 67.7

Wednesday 2/8/17 68.2

The results of the monitoring show that LA10,18-hour noise levels were comparable across each 24-hour

periods of monitoring. This indicates minimal change in road traffic counts between each day

(including the weekend). The measured LA10,18-hour noise levels have been used for the verification of

the road traffic noise model (as discussed in Section 5.3).

Noise levels at Position 2 were marginally higher than at Position 1. It is noted that the microphone

at Position 2 was slightly elevated (3.0 m above ground), which is likely to contribute to the higher

measured noise levels (due to lesser influence from ground absorption).

The results of the attended noise monitoring are presented in Appendix B. No extraneous noise

sources were identified as affecting road traffic noise level measurements during the attended noise

measurements.



4 Noise CriteriaThe relevant noise criteria for the assessment are presented in Section 3.2 Categories and Criteria of

the TMR Code of Practice. Table 4.1 presents the road traffic noise criteria applicable to this noise

assessment.

Table 4.1 - Assessment Noise Criteria

Categories

Criteria

Existing Residences

(facade-corrected)

Educational,

Community and

Health Buildings

(facade-corrected)

Outdoor Educational

and Passive

Recreational Areas

(including Parks)

(free-field)

Upgrading Existing Road 68 LA10,18-hour 65 LA10,1-hour No Criteria Specified

The criteria apply to noise sensitive land uses only, which includes the following (as defined by TMR):

⚫ a dwelling (detached and attached) including house, townhouse, unit, reformatory institution,

caravan park or retirement village;

⚫ a library, child care centre, kindergarten, school, school playgrounds, college, university,

museum, art gallery or other educational institution;

⚫ a community building including a place of public worship;

⚫ a hospital, respite care facility, nursing home, aged care facility, surgery or other medical centre;

⚫ a hotel, motel or other premises which provides accommodation for the public;

⚫ a protected area, or an area identified under a conservation plan as a critical habitat or an area

of major interest under the Nature Conservation Act 1992; and

⚫ a public park or gardens that is open to the public (whether or not on payment of a fee) for use

other than for sport or organised entertainment (passive recreation only).

As discussed in Section 2, noise sensitive uses in the study area include residential houses only.



5 Noise Modelling

5.1 Modelling MethodologyFor the purposes of the assessment, predictions were undertaken in accordance with the

methodology described in the United Kingdom, Department of Transport (1988) procedure,

Calculation of Road Traffic Noise (CoRTN). CoRTN is commonly adopted in Australia for the

assessment of road traffic noise impacts and has been subject to scientific studies to determine its

performance in Queensland conditions (see Section 4.3.2.1 of the TMR Code of Practice).

The calculation method gives consideration to various elements of the road design including traffic

flows, traffic fleet composition, road gradient, acoustic shielding by other buildings and elevations,

and road surface type. The method predicts LA10,18hour noise levels which are the noise levels exceeded

10 % of the time between the hours of 6 am and midnight.

The CadnaA (Computer Aided Noise Abatement Model) interface (CadnaA) developed by DataKustik

has been used to undertake the noise predictions in accordance with the CoRTN methodology. The

following sections discuss the modelling inputs, assumptions and results.

5.2 Modelling Inputs5.2.1 Traffic Data

Traffic data for Grange Road and Raymont Road has been provided by Brisbane City Council in the

Raymont Road / Grange Road Intersection Upgrade Technical Note Report1. The report provides AM

and PM peak intersection analysis data for No Upgrade and With Upgrade scenarios for the years

2016 and 2031. Heavy vehicle counts are also provided. It is noted that the analysis indicates traffic

volumes are identical without and with the upgrade.

For the purpose of estimating the Annual Average Daily Traffic (AADT), it is assumed the peak traffic

flows are 10% of the AADT. Furthermore, the CoRTN model utilises traffic counts from 6 am to

midnight. Based on a review of hourly 2015 traffic data for Stafford Road to the north2, it is assumed

that 18 hour traffic counts are 96% of the AADT.

To predicted future traffic noise levels, a 10-year horizon from construction has been considered. It is

anticipated that construction would be completed by late 2018, therefore, the year 2029 has been

considered. To estimate 2029 counts from 2016 and 2031 traffic data, a constant growth rate has

been assumed and estimates have been made through interpolation.

Table 5.1 presents a summary of the traffic data considered in the assessment. For the With Upgrade

Scenario, turning lanes on Grange Road (southbound right turn and northbound left turn) were

considered separately given the upgraded intersection would provide these as separate lanes to the

1 Brisbane City Council, Raymont Road / Grange Road Intersection Upgrade Technical Note Report, June 2017, Issue No. Final

A.

2 2015 traffic data collected by TMR for Stations 135975 and 135976



main through road.

Table 5.1 - Modelled Traffic Data – No Upgrade Scenario

Road Section

2017 2029

18-hour

VolumeHV%

18-hour

VolumeHV%

Grange Road Northbound

(South of Raymont Rd)

16098

(4065 left turn

onto Raymont Rd)

2.4%

(3.5%)

24897

(7140 left turn

onto Raymont Rd)

2.3%

(3.5%)

Grange Road Northbound

(North of Raymont Rd)13563 2.2% 19283 2.1%

Grange Road Southbound

(North of Raymont Rd)

13226

(2250 right turn

onto Raymont Rd)

1.9%

(2.0%)

18454

(3126 right turn

onto Raymont Rd)

2.0%

(2.0%)

Grange Road Southbound

(South of Raymont Rd)14313 1.8% 18561 1.8%

Raymont Road 10517 2.1% 13949 2.1%

5.2.2 Road Surface

Table 5.2 presents the pavement surface corrections presented in the TMR Code of Practice. Site

observations indicate that the road link of interest comprises of a Dense Graded Asphalt (DGA)

pavement therefore, no correction to the predicted noise level is required.

Table 5.2 - Pavement Surface Corrections

Pavement Surface Type Change in Noise Level dB(A)

Portland Cement Concrete (PCC) + 5

16-20 mm Bituminous Seal (BS) + 4-5

5-14 Bituminous Seal (BS) + 1-3

Dense Graded Asphalt (DGA) 0

Stone Mastic Aslphalt (SMA) -1

Low Noise Stone Mastic Aslphalt (LNSMA) -2

Open Graded Asphalt (OGA) -3



5.2.3 Traffic Speed

The posted speed limit along both Grange Road and Raymont Road is 60 km/h. No change to the

speed limit have been identified with the upgrade.

5.2.4 Topography

Ground level terrain data for the road upgrade section has been provided by BCC in the form of 200

mm isopleth contour lines (DWG format). Terrain data for the area surrounding the road upgrade was

obtained from the Digital Elevation Model (DEM) 25 Metre Grid of Australia derived from LiDAR

model, which represents a National 25 metre (bare earth) DEM that has been derived from some 236

individual LiDAR surveys between 2001 and 2015.

The CadnaA model accounts for the influence of road gradients on predicted noise levels using the

terrain data provided and the CoRTN calculation methodology.

Building and barrier heights have been based on site inspections and a review of Google imagery.

The existing acoustic barriers included in the modelling are summarised in Figure 5.1. Only two

acoustic barriers (up to 1.8 m) were identified in the study areas (one concrete blockwork and a

second wooden paling fence with no air gaps). All other fences fronting houses were wooden with

gaps between palings and unlikely to provide significant acoustic benefit, and have therefore been

excluded from consideration.



Figure 5.1 - Existing Acoustic Barriers

5.2.5 Ground Absorption

To account for the influence of ground surface on the propagation of noise, a 0.75 ground absorption

value has been considered across the study area. A review of aerial photography indicates that the

ground surface of surrounding residential areas are primarily made up of absorptive ground (ie. grass

areas and garden beds), with smaller areas of reflective surfaces such as street pavement and

driveways.

In accordance with the CoRTN methodology, where barrier attenuation occurs, the greater of the

attenuation provided by the noise barrier and the ground absorption is applied.

5.2.6 Sensitive Receptors

Receptors have been modelled for each sensitive building using the Building Evaluation function of

CadnaA (see Figure 5.1). The Building Evaluation function provides the highest predicted noise level



at 1 metre from each facade of a building. The model does not automatically include a facade

correction in the predictions 1 m from a building, and the +2.5 dB facade correction has been applied

manually to the predicted results. A total of 50 sensitive receptor buildings have been included in the

study area.

In the absence of finished floor levels, receptors have been modelled at 1.8 m above ground height

for ground floor levels and 4.6 m high for second-storey receptors (as per the TMR Code of Practice).

A number of houses in the study area are located on stilts and this has been taken into account

modelling. For example, where the house is raised by 2.0 m, a receptor height of 3.8 m has been

considered for ground floor.

5.2.7 Model Corrections

In addition to the 0 dB DGA surface correction and +2.5 dB facade correction, a calibration factor has

been applied to the predicted results based on the recommendations of a CoRTN evaluation study

undertaken in 1983 by NAASRA Working Group.

Table 5.3 summarises the relevant calibration factors and CoRTN accuracy for Queensland Conditions

(as presented in Section 4.3.2.1 of the TMR Code of Practice). As all noise monitoring positions are in

free-field locations, the -0.7 dB correction has been applied.

Table 5.3 - CoRTN Calibration Factors and Accuracies for Queensland Conditions

Road Location Receptor Location Calibration

Factor dB(A)

Accuracy of

calibrated calculation

or prediction dB(A)

Across Queensland (except

Pacific Motorway from Logan

Motorway to Nerang)

Free field - 0.7 for all sites +/- 3.6

1 m in front of building facade -1.7 for all sites +/- 5.0

5.3 Calibration ResultsLA10,18-hour noise levels have been predicted for the year 2017 for comparison with the measured data.

Table 5.4 presents a comparison of predicted and measured noise levels.

Table 5.4 - Calibration Results

Position Average Measured Weekday

LA10, 18Hr dB(A)

Predicted

LA10, 18Hr dB(A)Difference dB(A)

1 67.0 – 67.4 70.4 + 3.0 to 3.4

2 67.7 – 68.2 71.0 + 2.8 to 3.3

Based on the above results, the model is over-predicting by 2.8 to 3.4 dB. One factor which may be

contributing to the over-prediction is the accuracy of adopted traffic count data. The traffic data is



based on a traffic forecast model which accounts for survey data from the surrounding road network.

The daily traffic provided is derived from peak hour estimations assuming peak hour counts are 10%

of total daily counts. Predicted noise levels are expected to be lower if actual traffic counts are lower

than those estimated.

It is noted that the over-prediction of 2.8 to 3.4 dB is within the typical +/- 3.6 dB accuracy of CoRTN

model predictions in Queensland (as presented in Table 5.3), however, these differences are outside

the +/- 2 dB correction considered reasonable for the accuracy of a model. For the purpose of the

assessment and to avoid potentially onerous mitigation options from being recommended, the

Grange Road source noise level has been corrected by minus 1.0 dB to result in a 2 dB over-

prediction at the monitoring positions.

5.4 Modelling ResultsTable 5.5 presents the predicted LA10,18-hour (facade-corrected) noise levels for the year 2017 and 2029.

A comparison of No Upgrade and With Upgrade noise levels is also presented for each model year.

Appendix D presents predicted LA10,18-hour facade-corrected noise level contours for the Years 2017 and

2029.

Table 5.5 - Predicted LA10,18-hour Noise Levels (Facade-Corrected)

House Address

Predicted LA10,18-hour Noise Level (Facade-Corrected, dB(A))Difference dBWith Project

2017 2029

No Upgrade With Upgrade No Upgrade With Upgrade

15 Chermside Street 54 54 56 56 -



21-23 Chermside Street 57 57 58 58 -



29-31 Chermside Street 71 71 72 72 -











37 Dennis Street 56 56 57 57 -

38-40 Dennis Street 57 57 58 58 -




House Address

Predicted LA10,18-hour Noise Level (Facade-Corrected, dB(A))Difference dBWith Project

2017 2029

No Upgrade With Upgrade No Upgrade With Upgrade


50 Grange Road 73 73 75 75 -

51 Grange Road 73 73 74 74 -

52-54 Grange Road 72 72 74 74 -

53 Grange Road 74 74 75 75 -

56 Grange Road 71 71 73 73 -

58 Grange Road 72 72 74 74 -

59-61 Grange Road 73 73 74 74 -

60-62 Grange Road 72 72 74 74 -

63 Grange Road 74 74 76 76 -

64 Grange Road 73 73 74 74 -

65 Grange Road 74 74 76 76 -

67 Grange Road 73 74 74 75 1

71-73 Grange Road 74 75 76 77 1

74 Grange Road 73 73 75 75 -

76 Grange Road 73 73 75 75 -

78 Grange Road 72 72 74 74 -

80 Grange Road 72 72 74 74 -

81-83 Grange Road 72 73 73 74 1

82 Grange Road 72 72 74 74 -

84-86 Grange Road 72 72 74 74 -

85 Grange Road 74 74 75 76 1

88 Grange Road 73 73 74 74 -

54 Howard Street 62 62 64 64 -

56 Howard Street 69 69 70 70 -

41 Prince Street 62 62 64 64 -

45 Prince Street 73 74 75 76 1

54-56 Prince Street 63 63 64 64 -

7 Raymont Road 69 69 70 70 -

Noise Criteria 68

The results of the modelling indicate exceedence of the 68 dB(A) noise criteria for 27 of the 50

houses modelled in the project study area for the years 2017 and 2029. The majority of exceedences

are associated with houses located along Grange Road. Exceedences of up to 7 dB are predicted for

the ‘No Upgrade’ scenario and 8 dB for the ‘With Upgrade’ scenario.

The proposed upgrade is predicted to result in a 1 dB increase to noise levels at only 5 houses. These

houses are located on the eastern side of Grange Road, closest to the proposed road widening



section. A 1 dB increase is considered a minor increase and would not be discernible to a resident.

No additional houses are predicted to exceed the criteria with the proposed upgrade.



6 ConclusionsThe conclusions of the road traffic noise assessment are summarised as follows:

⚫ Sensitive receptors in the study area consist of residential buildings (in the form of single

dwellings). These houses are located adjacent to Grange Road and Raymont Road.

⚫ Comparison of measured noise levels with predicted noise levels indicate the model is over-

predicting by approximately 3 dB. A minus 1 dB correction has been applied to ensure the model

is predicting within the +/- 2 dB allowable tolerance referenced by TMR.

⚫ 27 of the modelled 50 residential dwellings in the study area are predicted to exceed the noise

criteria for the modelled scenarios (2017 ‘No Upgrade’, 2017 ‘With Upgrade’, 2029 ‘No Upgrade’

and 2029 ‘With Upgrade’). Exceedences of up to 7 dB are predicted for the ‘No Upgrade’

scenario and 8 dB for the ‘With Upgrade’ scenario.

⚫ The proposed upgrade is predicted to result in a 1 dB increase to noise levels at only 5 houses.

These houses are located on the eastern side of Grange Road, closest to the proposed road

widening section. A 1 dB increase is considered a minor increase and would not be discernible to

a resident. No additional houses are predicted to exceed the criteria with the proposed upgrade.



Appendix A - Acoustic Glossary



APPENDIX A: GLOSSARY OF ACOUSTIC TERMINOLOGY

A-Weighting A response provided by an electronic circuit which modifies sound in such a way

that the resulting level is similar to that perceived by the human ear.

dB (decibel) This is the scale on which sound pressure level is expressed. It is defined as 20

times the logarithm of the ratio between the root-mean-square pressure of the

sound field and the reference pressure (0.00002N/m2).

dB(A) This is a measure of the overall noise level of sound across the audible spectrum

with a frequency weighting (i.e. ‘A’ weighting) to compensate for the varying

sensitivity of the human ear to sound at different frequencies.

Facade Noise Level Refers to a sound pressure level determined at a point close to an acoustically

reflective surface (in addition to the ground). Typically a distance of 1 metre is

used.

Free Field Refers to a sound pressure level determined at a point away from reflective

surfaces other than the ground with no significant contribution due to sound from

other reflective surfaces; generally as measured outside and away from buildings.

Hertz (Hz) A measure of the frequency of sound. It measures the number of pressure peaks

per second passing a point when a pure tone is present.

LAeq

Equivalent Continuous

Sound Level

This is the equivalent steady sound level in dB(A) containing the same acoustic

energy as the actual fluctuating sound level over the given period. For a steady

sound with small fluctuations, its value is close to the average sound pressure level.

LA90,T This is the dB(A) level exceeded 90% of the time, T.

LA10,T This is the dB(A) level exceeded 10% of the time, T.

LA50, T This is the dB(A) level exceeded 50% of the time, T.

LWA The A-weighted sound power level in dB.



Appendix B – Noise Monitoring Fieldsheets



MONITORING POSITION 1

Noise Monitoring Data

Road Grange Road

Location Position 1 - Western end of Prince Street, 9 m from Grange Road

Lot and RP numbers Lot 1 on RP37493

Date 18 – 24 April 2017

Operator James Daramola

Sample Interval 60 minutes

Instrument Type/Serial No.

Ngara (87809c) Microphone Height 1.2 m

Calibrator/Serial No. Puslar 105 (62686) Façade Corrected? Free Field

Pre/Post Calibration 93.9/93.8 Average LA10 (18 hour) 67.4

Date End Time LAeq LAMax LA1 LA10 LA90 LAmin

18/04/2017 12:00 64.7 84.9 73.5 68.1 52.9 43.8

18/04/2017 13:00 64.2 80.0 72.3 67.5 54.1 45.5

18/04/2017 14:00 68.4 82.2 79.0 72.7 54.0 43.5

18/04/2017 15:00 79.0 101.6 92.5 77.9 58.3 47.1

18/04/2017 16:00 65.5 89.3 73.8 67.9 56.2 47.9

18/04/2017 17:00 65.7 89.6 73.3 68.0 56.7 45.6

18/04/2017 18:00 64.9 86.0 71.5 67.8 56.2 47.1

18/04/2017 19:00 63.7 81.9 72.1 66.9 52.8 42.6

18/04/2017 20:00 62.4 80.1 71.2 66.1 48.3 35.8

18/04/2017 21:00 60.8 79.9 69.8 65.1 45.3 35.7

18/04/2017 22:00 59.8 80.5 69.3 64.3 42.7 34.4

18/04/2017 23:00 57.9 82.1 68.5 62.1 35.4 32.5

19/04/2017 00:00 54.1 74.4 66.4 56.8 33.8 31.7

19/04/2017 01:00 51.3 74.8 64.6 50.2 33.3 32.0

19/04/2017 02:00 51.4 74.6 64.8 46.9 33.0 31.7

19/04/2017 03:00 49.8 79.2 62.7 46.1 33.0 31.5

19/04/2017 04:00 52.0 73.8 65.7 49.9 33.9 32.5

19/04/2017 05:00 57.7 75.6 69.7 61.2 35.8 33.4

19/04/2017 06:00 63.4 85.1 72.9 67.8 45.6 36.2

19/04/2017 07:00 66.8 82.6 75.0 70.3 55.0 45.2

19/04/2017 08:00 66.4 87.5 74.5 69.5 56.0 45.3

19/04/2017 09:00 66.0 84.5 74.3 68.9 56.6 47.5

19/04/2017 10:00 65.9 86.6 74.1 68.5 55.2 44.9

19/04/2017 11:00 72.8 89.6 84.0 76.0 55.3 45.7

19/04/2017 12:00 64.6 90.5 72.1 67.5 53.7 44.3

19/04/2017 13:00 64.3 81.2 71.8 67.5 54.7 45.6

19/04/2017 14:00 64.7 91.0 72.1 67.4 53.8 44.0

19/04/2017 15:00 65.4 90.2 72.9 68.0 55.5 45.8

19/04/2017 16:00 65.6 87.6 73.4 68.3 56.6 45.6

19/04/2017 17:00 65.7 90.2 72.8 67.9 56.9 49.4

19/04/2017 18:00 65.0 83.0 71.9 67.9 56.2 50.0




19/04/2017 19:00 65.0 87.4 72.4 67.7 54.8 44.6

19/04/2017 20:00 65.4 97.7 71.6 66.7 50.4 39.2

19/04/2017 21:00 61.4 79.8 70.3 65.4 47.5 37.0

19/04/2017 22:00 60.0 75.6 69.2 64.6 44.1 36.3

19/04/2017 23:00 58.0 77.6 68.4 62.5 37.8 34.3

20/04/2017 00:00 55.1 74.8 67.4 58.9 35.2 33.1

20/04/2017 01:00 52.9 73.9 66.2 53.6 34.3 32.6

20/04/2017 02:00 50.6 76.6 64.1 48.2 33.9 32.5

20/04/2017 03:00 50.0 72.8 63.7 47.4 34.1 32.4

20/04/2017 04:00 52.2 75.9 66.2 50.5 34.6 33.1

20/04/2017 05:00 57.5 76.1 69.7 60.7 37.0 33.4

20/04/2017 06:00 63.8 86.7 73.4 68.2 45.7 38.8

20/04/2017 07:00 67.2 88.3 75.9 70.2 55.5 46.6

20/04/2017 08:00 66.5 88.4 74.6 69.5 56.7 45.2

20/04/2017 09:00 65.8 86.4 74.3 68.8 55.4 46.1

20/04/2017 10:00 65.9 93.7 73.6 68.2 55.4 48.5

20/04/2017 11:00 64.5 82.4 72.5 67.9 54.6 45.2

20/04/2017 12:00 65.3 89.4 74.7 68.0 54.6 46.1

20/04/2017 13:00 64.4 88.5 71.9 67.3 54.2 46.2

20/04/2017 14:00 64.5 84.8 72.8 67.3 53.8 44.4

20/04/2017 15:00 65.0 93.3 72.4 67.4 55.0 46.1

20/04/2017 16:00 65.9 90.8 73.3 68.1 56.5 47.4

20/04/2017 17:00 65.7 87.4 73.8 68.3 56.8 48.1

20/04/2017 18:00 64.9 80.3 72.1 67.6 56.6 50.5

20/04/2017 19:00 64.4 90.2 71.3 67.3 54.7 45.4

20/04/2017 20:00 63.7 83.8 71.9 66.9 51.3 41.3

20/04/2017 21:00 63.2 85.3 71.8 66.6 49.2 39.1

20/04/2017 22:00 60.7 87.9 69.6 64.7 42.9 35.4

20/04/2017 23:00 58.4 84.0 68.4 62.5 37.0 33.9

21/04/2017 00:00 55.1 75.7 67.5 58.5 35.4 33.1

21/04/2017 01:00 53.5 78.0 66.1 53.8 34.9 32.8

21/04/2017 02:00 52.3 78.3 65.6 50.6 34.5 32.8

21/04/2017 03:00 52.7 76.1 65.8 50.6 34.0 32.3

21/04/2017 04:00 53.0 74.1 66.8 51.8 34.5 32.9

21/04/2017 05:00 58.0 78.6 69.8 61.6 38.2 34.4

21/04/2017 06:00 63.9 85.8 73.3 68.0 45.3 38.0

21/04/2017 07:00 66.6 87.6 74.7 69.9 54.7 45.2

21/04/2017 08:00 67.0 84.8 75.6 69.8 56.4 47.5

21/04/2017 09:00 65.9 86.3 73.5 69.1 56.1 47.4

21/04/2017 10:00 65.1 88.8 74.2 67.8 54.9 45.7

21/04/2017 11:00 65.8 85.0 74.1 68.8 56.6 49.4

21/04/2017 12:00 65.1 82.1 72.9 68.1 56.6 44.4

21/04/2017 13:00 64.3 80.4 72.4 67.5 54.7 47.8

21/04/2017 14:00 64.2 82.7 71.6 67.5 54.7 47.3

21/04/2017 15:00 65.0 84.5 72.6 67.8 56.0 47.3

21/04/2017 16:00 65.5 84.6 73.2 68.2 56.3 48.6




21/04/2017 17:00 65.0 83.9 72.8 67.8 55.8 47.8

21/04/2017 18:00 65.5 85.8 73.4 67.9 56.4 45.7

21/04/2017 19:00 65.8 92.4 75.6 68.2 54.7 46.6

21/04/2017 20:00 63.3 87.1 72.8 66.7 49.5 39.7

21/04/2017 21:00 61.2 82.7 70.0 65.2 46.5 38.0

21/04/2017 22:00 61.0 82.3 70.3 64.7 44.3 35.7

21/04/2017 23:00 59.7 75.7 69.4 64.5 41.6 35.0

22/04/2017 00:00 58.2 76.2 68.4 63.1 38.2 33.5

22/04/2017 01:00 55.1 76.1 66.6 58.9 34.8 32.7

22/04/2017 02:00 53.6 76.2 66.0 54.8 34.0 32.1

22/04/2017 03:00 53.0 73.8 66.4 52.7 33.2 31.6

22/04/2017 04:00 53.8 75.5 66.9 53.5 33.4 32.1

22/04/2017 05:00 57.0 74.6 69.8 59.3 33.9 31.9

22/04/2017 06:00 60.2 77.2 71.6 64.5 37.1 33.6

22/04/2017 07:00 62.6 79.0 71.8 67.2 47.6 39.4

22/04/2017 08:00 65.8 84.3 74.1 70.0 52.0 39.7

22/04/2017 09:00 66.0 84.2 73.5 69.8 54.8 43.5

22/04/2017 10:00 66.8 90.5 73.0 70.0 57.1 48.3

22/04/2017 11:00 66.5 85.9 74.0 69.4 56.6 48.2

22/04/2017 12:00 66.0 86.8 73.5 69.0 56.8 46.8

22/04/2017 13:00 65.2 82.4 73.0 68.3 55.7 46.9

22/04/2017 14:00 64.7 90.4 71.6 67.5 54.7 43.5

22/04/2017 15:00 64.0 86.3 71.2 67.1 54.7 45.6

22/04/2017 16:00 63.9 87.0 71.0 66.9 52.8 43.2

22/04/2017 17:00 63.5 85.5 70.7 67.0 52.7 44.6

22/04/2017 18:00 63.9 90.2 71.5 66.9 52.8 44.5

22/04/2017 19:00 63.3 87.4 70.8 66.6 49.3 40.7

22/04/2017 20:00 62.0 87.8 70.2 65.1 46.9 39.8

22/04/2017 21:00 62.0 88.0 70.4 64.2 44.8 36.4

22/04/2017 22:00 60.0 80.7 69.5 64.1 44.4 36.2

22/04/2017 23:00 59.2 74.2 69.3 63.7 42.4 35.7

23/04/2017 00:00 57.9 75.6 68.3 62.6 39.3 35.5

23/04/2017 01:00 55.6 75.1 67.3 59.4 36.5 33.8

23/04/2017 02:00 54.8 76.8 67.3 57.3 34.7 32.8

23/04/2017 03:00 52.7 74.6 65.6 53.4 33.5 31.8

23/04/2017 04:00 52.8 71.2 65.8 53.8 32.9 31.5

23/04/2017 05:00 53.9 74.1 67.0 54.8 32.6 30.7

23/04/2017 06:00 56.8 73.3 68.5 60.5 35.9 32.1

23/04/2017 07:00 59.2 83.1 69.8 63.4 43.4 37.0

23/04/2017 08:00 62.0 85.2 72.5 65.9 43.9 36.4

23/04/2017 09:00 62.1 79.1 70.3 66.3 49.2 38.0

23/04/2017 10:00 63.9 85.8 72.1 67.3 52.9 43.3

23/04/2017 11:00 63.9 83.8 71.8 67.4 52.8 42.7

23/04/2017 12:00 65.1 92.1 71.5 66.9 53.4 44.8

23/04/2017 13:00 63.0 80.1 70.1 66.4 52.9 42.7

23/04/2017 14:00 63.5 85.9 70.7 66.6 52.3 43.5




23/04/2017 15:00 64.0 89.8 71.0 66.6 52.3 39.8

23/04/2017 16:00 63.4 80.9 71.9 66.9 51.7 42.9

23/04/2017 17:00 64.3 93.4 71.0 66.7 51.9 43.9

23/04/2017 18:00 64.1 93.5 71.4 66.9 50.3 41.4

23/04/2017 19:00 62.0 80.1 70.5 66.1 47.9 37.4

23/04/2017 20:00 61.1 91.0 70.2 64.4 44.6 34.4

23/04/2017 21:00 61.4 85.5 70.8 64.7 43.7 35.9

23/04/2017 22:00 60.2 89.3 69.4 63.0 40.2 34.4

23/04/2017 23:00 56.4 74.6 68.0 60.7 35.4 32.0

24/04/2017 00:00 55.0 79.9 67.3 56.9 32.9 30.7

24/04/2017 01:00 50.9 73.6 64.3 49.7 31.1 30.0

24/04/2017 02:00 50.8 74.6 64.7 48.7 31.2 29.9

24/04/2017 03:00 50.4 78.5 63.8 45.8 31.2 29.8

24/04/2017 04:00 54.4 80.7 67.2 53.4 31.7 30.3

24/04/2017 05:00 57.7 77.8 70.3 60.2 34.0 31.0

24/04/2017 06:00 62.7 82.0 72.9 67.0 45.6 36.1

24/04/2017 07:00 66.6 88.1 75.9 70.0 54.0 42.6

24/04/2017 08:00 67.6 93.9 75.9 70.0 56.5 45.2

24/04/2017 09:00 66.0 85.2 74.3 69.1 55.4 44.6

24/04/2017 10:00 66.0 88.0 74.3 69.0 55.2 46.2

24/04/2017 11:00 65.9 94.7 74.8 67.9 53.7 41.3

24/04/2017 12:00 64.0 87.0 73.0 67.1 53.0 43.0



ATTENDED NOISE MONITORING FIELD SHEET – 18 APRIL 2017

Project Number: 4094.8 Date: 18/04/17

Client: BCC Operator: Jaie Wilde

Noise Instrument:

Serial No:

B & K 2250

2741104

Calibrator:

Serial No:

Pulsar 105

62686

Pre-calibration: 94.2 Post calibration: 94.2

Location End of Prince St Description

Time Start 11:40

Grange Road quite busy, road noise dominant.

50.5 dB(A) when no traffic, no other noise sources.

Insect noise also audible, not dominant.

75-78 dB(A) general traffic flow.

Plane audible 14:30 into measurement – no effect on sound pressure levels.

LAeq 69.2

LAmax 85.7

LA1 78.6

LA10 72.8

LA90 55.1



ATTENDED NOISE MONITORING FIELD SHEET – 18 APRIL 2017


Client: BCC Operator: James Daramola

Noise Instrument:

Serial No:

B & K 2250

2741104

Calibrator:

Serial No:

Pulsar 105

62686


Location End of Prince St Description

Time Start 12:18

Grange Road traffic noise dominant.

Other noise sources include leaves rustling, air craft and birds.

LAeq 69.5

LAmax 84.1

LA1 78.0

LA10 73.3

LA90 58.3



MONITORING POSITION 2

Noise Monitoring Data

Road Grange Road

Location Position 2 – Rear Yard of 45 Prince Street

Lot and RP numbers

Date 1 August – 8 August 2017

Operator James Daramola

Sample Interval 60 minutes

Instrument Type/Serial No.

Nor140 (1404664) Microphone Height 3.0 m

Calibrator/Serial No. Pulsar 105 (62686) Façade Corrected? Free Field

Pre/Post Calibration 93.9 / 94.0 Average LA10 (18 hour) 67.9


01/08/17 15:00 65.4 86.9 73.3 68.1 56.8 42.6

01/08/17 16:00 67.1 91.2 75.2 68.5 58.4 46.2

01/08/17 17:00 66.1 90.6 72.3 68.4 58.4 46.5

01/08/17 18:00 66.1 89.7 73.0 68.4 58.2 50.9

01/08/17 19:00 65.6 90.2 73.2 68.1 56.3 46.8

01/08/17 20:00 63.7 86.6 71.0 67.1 52.5 39.7

01/08/17 21:00 62.0 78.6 69.3 65.9 49.7 38.0

01/08/17 22:00 61.2 83.5 69.2 65.2 45.5 37.9

01/08/17 23:00 58.9 83.7 68.2 63.5 39.4 34.3

02/08/17 00:00 54.1 74.9 65.5 58.2 37.2 34.5

02/08/17 01:00 52.0 73.3 64.3 54.0 36.5 34.5

02/08/17 02:00 51.2 78.6 63.5 49.6 34.9 32.5

02/08/17 03:00 51.5 77.7 64.7 50.0 33.8 31.1

02/08/17 04:00 52.5 72.2 66.6 52.8 34.3 31.2

02/08/17 05:00 58.2 78.9 68.8 62.4 38.6 33.2

02/08/17 06:00 64.2 84.7 73.4 68.4 47.7 41.2

02/08/17 07:00 67.4 84.4 76.4 70.5 57.1 48.7

02/08/17 08:00 67.3 87.3 75.4 70.0 58.4 47.7

02/08/17 09:00 66.2 89.2 73.6 69.2 55.9 44.8

02/08/17 10:00 65.8 86.0 74.1 68.6 56.0 43.1

02/08/17 11:00 65.3 83.3 73.6 68.4 56.0 44.4

02/08/17 12:00 65.4 90.2 72.2 67.7 55.7 42.6

02/08/17 13:00 66.2 94.8 74.7 68.4 56.1 43.3

02/08/17 14:00 66.0 92.0 73.7 68.1 56.4 43.4

02/08/17 15:00 65.5 84.3 72.9 68.4 56.9 44.8

02/08/17 16:00 66.3 83.5 74.3 68.7 58.7 52.0

02/08/17 17:00 66.4 88.5 73.0 68.8 58.1 45.7

02/08/17 18:00 65.9 83.0 73.3 68.3 58.0 51.2

02/08/17 19:00 66.3 91.9 74.1 68.4 58.0 50.8

02/08/17 20:00 64.6 85.9 72.4 67.8 54.4 45.0

02/08/17 21:00 64.3 88.6 73.2 66.6 51.5 42.9




02/08/17 22:00 62.1 84.2 71.0 66.1 46.6 38.7

02/08/17 23:00 60.8 86.3 68.6 64.1 41.7 36.9

03/08/17 00:00 54.9 71.3 66.0 59.7 37.0 33.9

03/08/17 01:00 51.8 70.4 64.1 54.2 36.3 33.5

03/08/17 02:00 50.3 72.8 64.2 48.9 32.6 30.4

03/08/17 03:00 51.0 75.5 64.8 47.8 32.0 29.9

03/08/17 04:00 50.9 71.7 64.5 51.0 33.6 30.3

03/08/17 05:00 58.9 80.6 70.2 63.0 38.9 32.3

03/08/17 06:00 63.9 80.7 73.7 67.7 47.6 39.0

03/08/17 07:00 67.7 90.1 76.3 70.1 55.4 45.5

03/08/17 08:00 66.3 88.2 73.9 69.2 57.8 46.3

03/08/17 09:00 66.5 93.2 72.9 68.6 56.8 45.2

03/08/17 10:00 66.1 82.5 74.0 69.1 57.5 46.9

03/08/17 11:00 65.7 86.5 73.9 68.5 57.3 44.4

03/08/17 12:00 65.5 79.2 73.5 68.6 57.2 45.7

03/08/17 13:00 64.8 89.7 72.4 67.8 56.1 43.3

03/08/17 14:00 65.5 82.9 74.0 68.3 57.1 48.5

03/08/17 15:00 65.2 82.6 71.8 68.1 58.0 50.1

03/08/17 16:00 66.8 87.6 74.2 68.8 58.9 47.0

03/08/17 17:00 66.5 89.3 73.0 68.9 58.8 46.1

03/08/17 18:00 66.3 88.1 73.6 68.5 58.0 49.6

03/08/17 19:00 65.1 87.7 70.8 67.6 57.0 46.8

03/08/17 20:00 64.0 83.5 71.9 67.0 55.0 41.8

03/08/17 21:00 64.3 81.3 69.7 67.1 55.0 44.8

03/08/17 22:00 63.5 76.6 68.9 66.5 55.7 47.9

03/08/17 23:00 63.2 83.1 69.9 66.8 45.1 40.4

04/08/17 00:00 64.4 76.1 69.6 67.2 42.9 37.3

04/08/17 01:00 54.4 72.1 67.0 56.0 38.3 35.7

04/08/17 02:00 48.4 70.5 59.3 51.7 37.0 35.1

04/08/17 03:00 51.9 73.7 60.1 56.9 36.3 34.5

04/08/17 04:00 50.9 70.7 62.7 55.3 37.2 34.3

04/08/17 05:00 58.6 79.4 69.6 62.8 36.4 32.3

04/08/17 06:00 63.5 83.7 72.7 67.5 46.1 36.9

04/08/17 07:00 66.9 88.2 74.8 69.8 56.8 44.1

04/08/17 08:00 68.8 103.1 73.8 69.4 58.3 50.1

04/08/17 09:00 65.5 79.3 73.1 69.0 56.2 44.6

04/08/17 10:00 65.6 88.4 72.7 68.6 56.1 45.9

04/08/17 11:00 65.2 80.7 72.3 68.3 57.0 46.2

04/08/17 12:00 65.2 81.8 72.6 68.3 56.4 46.0

04/08/17 13:00 66.5 96.5 73.1 68.0 57.5 49.2



ATTENDED NOISE MONITORING FIELD SHEET – 1 AUGUST 2017



Noise Instrument:

Serial No:

B & K 2250

2741104

Calibrator:

Serial No:

Pulsar 105

62686


Location 45 Prince St Description

Time Start 13:51


Other noise sources include the traffic light beeper, a local dog barking

(distant), leaves rustling, air craft and birds.

LAeq 61.1

LAmax 73.7

LA1 68.4

LA10 64.2

LA90 52.1



ATTENDED NOISE MONITORING FIELD SHEET – 4 AUGUST 2017



Noise Instrument:

Serial No:

B & K 2250

2741104

Calibrator:

Serial No:

Pulsar 105

62686


Location 45 Prince St Description

Time Start 13:01


Other noise sources include leaves rustling, air craft and birds.

LAeq 65.5

LAmax 85.8

LA1 75.8

LA10 67.2

LA90 55.7



Appendix C – Meteorological Data



APPENDIX C – METEOROLOGICAL DATATable C1 - Position 1 Monitoring - Meteorological Data

Date Time Temp (oC) Average WindSpeed (m/s)

Wind Direction Rainfall (mm)

18/04/17 11:00 a 23.4 0.4 W 0

18/04/17 11:15 a 23.8 0.4 NW 0

18/04/17 11:30 a 23.8 0.9 W 0

18/04/17 11:45 a 24.2 0.9 W 0

18/04/17 12:00 p 24.6 0.9 WNW 0

18/04/17 12:15 p 24.2 0.9 S 0

18/04/17 12:30 p 23.6 0.9 WNW 0

18/04/17 12:45 p 23.7 0.4 W 0

18/04/17 1:00 p 23.8 0.4 SW 0

18/04/17 1:15 p 24 0.4 WNW 0

18/04/17 1:30 p 23.9 0.4 W 0

18/04/17 1:45 p 23.4 0.4 W 0

18/04/17 2:00 p 24.1 0.9 WNW 0

18/04/17 2:15 p 24.2 0.9 WNW 0

18/04/17 2:30 p 23.2 0.9 WSW 0

18/04/17 2:45 p 22.4 0.9 WNW 0

18/04/17 3:00 p 22.9 0.4 W 0

18/04/17 3:15 p 23.1 1.3 WNW 0

18/04/17 3:30 p 23.3 0.9 WNW 0

18/04/17 3:45 p 23.4 1.3 WNW 0

18/04/17 4:00 p 23.7 1.3 WNW 0

18/04/17 4:15 p 23.3 0.9 WNW 0

18/04/17 4:30 p 23.1 0.9 WNW 0

18/04/17 4:45 p 22.9 0.9 WNW 0

18/04/17 5:00 p 22.7 0 W 0

18/04/17 5:15 p 22.6 0.4 WSW 0

18/04/17 5:30 p 22.4 0.4 WNW 0

18/04/17 5:45 p 22.2 0.4 W 0

18/04/17 6:00 p 22.1 0.4 WNW 0

18/04/17 6:15 p 21.9 0.4 WNW 0

18/04/17 6:30 p 21.8 0.4 WNW 0

18/04/17 6:45 p 21.7 0.4 W 0

18/04/17 7:00 p 21.6 0.4 WNW 0

18/04/17 7:15 p 21.4 0.4 W 0

18/04/17 7:30 p 21.4 0 W 0

18/04/17 7:45 p 21.4 0 WNW 0

18/04/17 8:00 p 21.3 0.4 WNW 0

18/04/17 8:15 p 21.1 0.9 WNW 0

18/04/17 8:30 p 20.9 0.9 W 0

18/04/17 8:45 p 20.8 0.4 WNW 0

18/04/17 9:00 p 20.6 0 N 0

18/04/17 9:15 p 20.4 0 N 0

18/04/17 9:30 p 20.2 0 N 0



Date Time Temp (oC)Average WindSpeed (m/s)


18/04/17 9:45 p 19.9 0 N 0

18/04/17 10:00 p 19.8 0 N 0

18/04/17 10:15 p 19.7 0 NW 0

18/04/17 10:30 p 19.6 0 NW 0

18/04/17 10:45 p 19.5 0 NW 0

18/04/17 11:00 p 19.4 0 NW 0

18/04/17 11:15 p 19.4 0 NW 0

18/04/17 11:30 p 19.3 0 NW 0

18/04/17 11:45 p 19.1 0 --- 0

19/04/17 12:00 a 18.9 0 --- 0

19/04/17 12:15 a 18.9 0 NW 0

19/04/17 12:30 a 18.8 0 NW 0

19/04/17 12:45 a 18.7 0 NW 0

19/04/17 1:00 a 18.7 0 NW 0

19/04/17 1:15 a 18.6 0 NW 0

19/04/17 1:30 a 18.5 0 NW 0

19/04/17 1:45 a 18.3 0 NW 0

19/04/17 2:00 a 18.2 0 NW 0

19/04/17 2:15 a 18.1 0 NW 0

19/04/17 2:30 a 18.2 0 NW 0

19/04/17 2:45 a 18.2 0 NW 0

19/04/17 3:00 a 18 0 NW 0

19/04/17 3:15 a 17.8 0 NW 0

19/04/17 3:30 a 17.8 0 NW 0

19/04/17 3:45 a 17.6 0 NW 0

19/04/17 4:00 a 17.4 0 NW 0

19/04/17 4:15 a 17.3 0 --- 0

19/04/17 4:30 a 17.3 0 --- 0

19/04/17 4:45 a 17.2 0 NW 0

19/04/17 5:00 a 17.1 0 NW 0

19/04/17 5:15 a 17 0 NW 0

19/04/17 5:30 a 17 0 NW 0

19/04/17 5:45 a 16.9 0 NW 0

19/04/17 6:00 a 17.1 0 NW 0

19/04/17 6:15 a 17.1 0 NW 0

19/04/17 6:30 a 17.1 0 NW 0

19/04/17 6:45 a 17.2 0 NW 0

19/04/17 7:00 a 17.6 0 NW 0

19/04/17 7:15 a 17.9 0 WNW 0

19/04/17 7:30 a 18.5 0 WNW 0

19/04/17 7:45 a 18.9 0 WNW 0

19/04/17 8:00 a 19.3 0 WNW 0

19/04/17 8:15 a 19.9 0.4 WNW 0

19/04/17 8:30 a 20.2 0.4 WNW 0

19/04/17 8:45 a 20.7 0.4 WNW 0

19/04/17 9:00 a 21.2 0.4 W 0





19/04/17 9:15 a 21.6 0.4 NW 0

19/04/17 9:30 a 21.6 0.4 WNW 0

19/04/17 9:45 a 21.7 0.4 NW 0

19/04/17 10:00 a 22.1 0.9 WNW 0

19/04/17 10:15 a 23.4 0.9 WNW 0

19/04/17 10:30 a 24.2 0.9 WNW 0

19/04/17 10:45 a 23.8 1.3 WNW 0

19/04/17 11:00 a 23.8 1.3 SW 0

19/04/17 11:15 a 24.1 0.9 WNW 0

19/04/17 11:30 a 23.6 1.3 WNW 0

19/04/17 11:45 a 24.1 0.9 SW 0

19/04/17 12:00 p 24.6 0.9 WSW 0

19/04/17 12:15 p 24.3 1.3 WNW 0

19/04/17 12:30 p 24.6 1.3 WNW 0

19/04/17 12:45 p 24.6 1.3 WNW 0

19/04/17 1:00 p 24.4 0.9 W 0

19/04/17 1:15 p 24.7 1.3 WNW 0

19/04/17 1:30 p 24.4 0.9 WNW 0

19/04/17 1:45 p 24.7 0.9 SSW 0

19/04/17 2:00 p 24.3 0.9 W 0

19/04/17 2:15 p 24.3 0.9 WSW 0

19/04/17 2:30 p 24.2 0.4 W 0

19/04/17 2:45 p 23.8 0.9 WNW 0

19/04/17 3:00 p 23.7 0.9 SW 0

19/04/17 3:15 p 23.6 1.3 WNW 0

19/04/17 3:30 p 23.2 0.9 W 0

19/04/17 3:45 p 23.2 0.9 WNW 0

19/04/17 4:00 p 23 1.3 W 0

19/04/17 4:15 p 22.9 0.9 WNW 0

19/04/17 4:30 p 22.6 0.9 W 0

19/04/17 4:45 p 22.5 0.9 WNW 0

19/04/17 5:00 p 22.2 1.3 WSW 0

19/04/17 5:15 p 21.6 1.3 WNW 0

19/04/17 5:30 p 21.6 0.4 W 0

19/04/17 5:45 p 21.6 0.9 WNW 0

19/04/17 6:00 p 21.5 0.4 WNW 0

19/04/17 6:15 p 21.4 0.9 W 0

19/04/17 6:30 p 21.2 0.9 WNW 0

19/04/17 6:45 p 21 0.4 WNW 0

19/04/17 7:00 p 20.9 0.4 WNW 0

19/04/17 7:15 p 20.9 0.9 WNW 0

19/04/17 7:30 p 20.8 0.4 WNW 0

19/04/17 7:45 p 20.7 0.9 W 0

19/04/17 8:00 p 20.6 0.4 WNW 0

19/04/17 8:15 p 20.6 0.9 WNW 0

19/04/17 8:30 p 20.5 0.4 WNW 0





19/04/17 8:45 p 20.5 0.4 WNW 0

19/04/17 9:00 p 20.4 0.4 WNW 0

19/04/17 9:15 p 20.2 0.4 WNW 0

19/04/17 9:30 p 20.1 0 WNW 0

19/04/17 9:45 p 19.8 0 NW 0

19/04/17 10:00 p 19.7 0 NW 0

19/04/17 10:15 p 19.4 0 NW 0

19/04/17 10:30 p 19.2 0 NW 0

19/04/17 10:45 p 19.2 0 NNE 0

19/04/17 11:00 p 19.2 0 NNE 0

19/04/17 11:15 p 19.3 0 NNE 0

19/04/17 11:30 p 19 0 NNE 0

19/04/17 11:45 p 18.8 0 NNE 0

20/04/17 12:00 a 18.7 0 NNE 0

20/04/17 12:15 a 18.4 0 NNE 0

20/04/17 12:30 a 18.3 0 NNE 0

20/04/17 12:45 a 18.2 0 N 0

20/04/17 1:00 a 18.1 0 NNW 0

20/04/17 1:15 a 17.9 0 NNW 0

20/04/17 1:30 a 17.8 0 NNW 0

20/04/17 1:45 a 17.7 0 NNW 0

20/04/17 2:00 a 17.6 0 NNW 0

20/04/17 2:15 a 17.4 0 --- 0

20/04/17 2:30 a 17.3 0 NNW 0

20/04/17 2:45 a 17.3 0 NNW 0

20/04/17 3:00 a 17.3 0 NNW 0

20/04/17 3:15 a 17.3 0 NNW 0

20/04/17 3:30 a 17.2 0 NNW 0

20/04/17 3:45 a 17.1 0 NNW 0

20/04/17 4:00 a 17 0 NNW 0

20/04/17 4:15 a 16.9 0 NNW 0

20/04/17 4:30 a 16.9 0 NNW 0

20/04/17 4:45 a 16.7 0 NNW 0

20/04/17 5:00 a 16.5 0 NNW 0

20/04/17 5:15 a 16.5 0 NNW 0

20/04/17 5:30 a 16.7 0 NNW 0

20/04/17 5:45 a 16.7 0 NNW 0

20/04/17 6:00 a 16.8 0 NNW 0

20/04/17 6:15 a 16.8 0 --- 0

20/04/17 6:30 a 16.9 0 NNW 0

20/04/17 6:45 a 17.2 0 NNW 0

20/04/17 7:00 a 17.5 0 NNW 0

20/04/17 7:15 a 17.8 0.4 WNW 0

20/04/17 7:30 a 18.1 0.4 WNW 0

20/04/17 7:45 a 18.4 0 N 0

20/04/17 8:00 a 18.8 0 N 0





20/04/17 8:15 a 19.1 0.4 WNW 0

20/04/17 8:30 a 19.2 0 WNW 0

20/04/17 8:45 a 19.3 0 NW 0

20/04/17 9:00 a 20.2 0.4 WNW 0

20/04/17 9:15 a 21.1 0.4 WNW 0

20/04/17 9:30 a 21.4 0.4 W 0

20/04/17 9:45 a 21.9 0.4 W 0

20/04/17 10:00 a 22.2 0.4 W 0

20/04/17 10:15 a 22.7 0.9 WNW 0

20/04/17 10:30 a 22.7 0.4 WNW 0

20/04/17 10:45 a 23.2 0.9 W 0

20/04/17 11:00 a 23.1 0.4 W 0

20/04/17 11:15 a 23 0.4 WSW 0

20/04/17 11:30 a 23.4 0.4 W 0

20/04/17 11:45 a 23.5 1.3 WNW 0

20/04/17 12:00 p 23.7 0.9 WNW 0

20/04/17 12:15 p 23.9 0.4 WSW 0

20/04/17 12:30 p 23.9 0.4 W 0

20/04/17 12:45 p 23.5 0.9 WSW 0

20/04/17 1:00 p 23.7 0.4 SW 0

20/04/17 1:15 p 23.3 0.9 WNW 0

20/04/17 1:30 p 23.4 0.4 WSW 0

20/04/17 1:45 p 23.2 0.9 WSW 0

20/04/17 2:00 p 22.8 0.9 WSW 0

20/04/17 2:15 p 22.2 0.9 WSW 0

20/04/17 2:30 p 21.3 0.9 WNW 0

20/04/17 2:45 p 21.1 0.4 WSW 0

20/04/17 3:00 p 21.4 0.4 WNW 0

20/04/17 3:15 p 21.6 0 WNW 0

20/04/17 3:30 p 21.8 0 WNW 0

20/04/17 3:45 p 22.1 0 WNW 0

20/04/17 4:00 p 22.3 0.4 WNW 0

20/04/17 4:15 p 22.5 0.4 WSW 0

20/04/17 4:30 p 22.4 0.4 WNW 0

20/04/17 4:45 p 22.4 0.4 WSW 0

20/04/17 5:00 p 22.3 0 W 0

20/04/17 5:15 p 22.1 0 SSW 0

20/04/17 5:30 p 21.9 0.4 W 0

20/04/17 5:45 p 21.7 0 W 0

20/04/17 6:00 p 21.6 0 W 0

20/04/17 6:15 p 21.4 0 W 0

20/04/17 6:30 p 21.3 0 W 0

20/04/17 6:45 p 21.1 0 W 0

20/04/17 7:00 p 20.9 0 W 0

20/04/17 7:15 p 20.9 0 W 0

20/04/17 7:30 p 20.8 0 W 0





20/04/17 7:45 p 20.7 0 W 0

20/04/17 8:00 p 20.7 0 W 0

20/04/17 8:15 p 20.6 0 W 0

20/04/17 8:30 p 20.2 0 --- 0

20/04/17 8:45 p 19.9 0 W 0

20/04/17 9:00 p 19.7 0 W 0

20/04/17 9:15 p 19.6 0 W 0

20/04/17 9:30 p 19.4 0 W 0

20/04/17 9:45 p 19.4 0 --- 0

20/04/17 10:00 p 19.3 0 W 0

20/04/17 10:15 p 19.1 0 W 0

20/04/17 10:30 p 19 0 W 0

20/04/17 10:45 p 19.1 0 W 0

20/04/17 11:00 p 19.1 0 W 0

20/04/17 11:15 p 18.8 0 W 0

20/04/17 11:30 p 18.6 0 W 0

20/04/17 11:45 p 18.4 0.4 W 0

21/04/17 12:00 a 18.4 0.4 W 0

21/04/17 12:15 a 18.3 0.4 W 0

21/04/17 12:30 a 18.1 0.4 W 0

21/04/17 12:45 a 18 0.4 WNW 0

21/04/17 1:00 a 17.9 0.4 WNW 0

21/04/17 1:15 a 17.9 0.4 WNW 0

21/04/17 1:30 a 17.7 0.4 WNW 0

21/04/17 1:45 a 17.6 0 WNW 0

21/04/17 2:00 a 17.5 0.4 WNW 0

21/04/17 2:15 a 17.5 0.4 WNW 0

21/04/17 2:30 a 17.4 0.4 WNW 0

21/04/17 2:45 a 17.4 0 WNW 0

21/04/17 3:00 a 17.3 0.4 WNW 0

21/04/17 3:15 a 17.2 0.4 WNW 0

21/04/17 3:30 a 17.1 0.4 WNW 0

21/04/17 3:45 a 17.1 0.4 WNW 0

21/04/17 4:00 a 17 0.4 WNW 0

21/04/17 4:15 a 17 0.4 WNW 0

21/04/17 4:30 a 17.1 0 WNW 0

21/04/17 4:45 a 17.2 0 WNW 0

21/04/17 5:00 a 17.2 0 WNW 0

21/04/17 5:15 a 17.2 0 WNW 0

21/04/17 5:30 a 17.2 0 WNW 0

21/04/17 5:45 a 17.2 0 WNW 0

21/04/17 6:00 a 17.2 0 WNW 0

21/04/17 6:15 a 17.2 0 WNW 0

21/04/17 6:30 a 17.2 0 WNW 0

21/04/17 6:45 a 17.3 0 --- 0

21/04/17 7:00 a 17.3 0 WNW 0





21/04/17 7:15 a 17.4 0 WNW 0

21/04/17 7:30 a 17.4 0 WNW 0

21/04/17 7:45 a 17.6 0 --- 0

21/04/17 8:00 a 17.7 0 --- 0

21/04/17 8:15 a 17.7 0 WNW 0

21/04/17 8:30 a 17.8 0 WNW 0

21/04/17 8:45 a 17.9 0 WNW 0

21/04/17 9:00 a 18.1 0 WNW 0

21/04/17 9:15 a 18.5 0 WNW 0

21/04/17 9:30 a 18.8 0 WNW 0

21/04/17 9:45 a 19.1 0 WNW 0

21/04/17 10:00 a 19.2 0 WNW 0

21/04/17 10:15 a 19.7 0 NW 0

21/04/17 10:30 a 20.2 0 NW 0

21/04/17 10:45 a 20.4 0 NW 0

21/04/17 11:00 a 20.7 0 NW 0

21/04/17 11:15 a 21.1 0.4 NW 0

21/04/17 11:30 a 21.7 0.4 WNW 0

21/04/17 11:45 a 21.9 0.4 W 0

21/04/17 12:00 p 22.2 0.4 W 0

21/04/17 12:15 p 22.5 0.4 WNW 0

21/04/17 12:30 p 22.6 0.9 WNW 0

21/04/17 12:45 p 22.8 0.9 WNW 0

21/04/17 1:00 p 22.8 0.4 WSW 0

21/04/17 1:15 p 22.9 0.4 WSW 0

21/04/17 1:30 p 22.8 0.4 WNW 0

21/04/17 1:45 p 23.1 0.4 WNW 0

21/04/17 2:00 p 23.5 0.4 WSW 0

21/04/17 2:15 p 23.1 0.4 W 0

21/04/17 2:30 p 22.8 0.4 WNW 0

21/04/17 2:45 p 22.7 0.4 SW 0

21/04/17 3:00 p 22.7 0.4 WNW 0

21/04/17 3:15 p 22.7 0.4 WNW 0

21/04/17 3:30 p 22.7 0.9 WNW 0

21/04/17 3:45 p 22.6 0.9 WNW 0

21/04/17 4:00 p 22.7 0.9 WNW 0

21/04/17 4:15 p 22.5 0.4 WNW 0

21/04/17 4:30 p 22.3 0.4 WNW 0

21/04/17 4:45 p 22.1 0 WNW 0

21/04/17 5:00 p 22.1 0.4 WNW 0

21/04/17 5:15 p 22 0 WNW 0

21/04/17 5:30 p 21.8 0 NW 0

21/04/17 5:45 p 21.8 0 NW 0

21/04/17 6:00 p 21.6 0 --- 0

21/04/17 6:15 p 21.4 0 NW 0

21/04/17 6:30 p 21.2 0 NW 0





21/04/17 6:45 p 21 0 --- 0

21/04/17 7:00 p 20.7 0 --- 0

21/04/17 7:15 p 20.6 0 --- 0

21/04/17 7:30 p 20.4 0 --- 0

21/04/17 7:45 p 20.3 0 --- 0

21/04/17 8:00 p 19.9 0 --- 0

21/04/17 8:15 p 19.9 0 NW 0

21/04/17 8:30 p 19.9 0 --- 0

21/04/17 8:45 p 19.9 0 NW 0

21/04/17 9:00 p 19.8 0 --- 0

21/04/17 9:15 p 19.7 0 NW 0

21/04/17 9:30 p 19.4 0 --- 0

21/04/17 9:45 p 19.1 0 --- 0

21/04/17 10:00 p 18.8 0 NW 0

21/04/17 10:15 p 18.9 0 NNW 0

21/04/17 10:30 p 18.7 0 NNW 0

21/04/17 10:45 p 18.6 0 NNW 0

21/04/17 11:00 p 18.6 0 NNW 0

21/04/17 11:15 p 18.4 0 --- 0

21/04/17 11:30 p 18.2 0 NNW 0

21/04/17 11:45 p 18.2 0 NNW 0

22/04/17 12:00 a 18 0 NNW 0

22/04/17 12:15 a 17.8 0 NNW 0

22/04/17 12:30 a 17.8 0 NNW 0

22/04/17 12:45 a 17.6 0 NNW 0

22/04/17 1:00 a 17.4 0 NNW 0

22/04/17 1:15 a 17.4 0 NNW 0

22/04/17 1:30 a 17.3 0 NNW 0

22/04/17 1:45 a 17.3 0 NNW 0

22/04/17 2:00 a 17.3 0 NNW 0

22/04/17 2:15 a 17.3 0 NNW 0

22/04/17 2:30 a 17.3 0 NNW 0

22/04/17 2:45 a 17.3 0 NNW 0

22/04/17 3:00 a 17.2 0 NNW 0

22/04/17 3:15 a 17.1 0 NNW 0

22/04/17 3:30 a 17.1 0 NNW 0

22/04/17 3:45 a 16.9 0 NNW 0

22/04/17 4:00 a 16.8 0 --- 0

22/04/17 4:15 a 16.7 0 --- 0

22/04/17 4:30 a 16.7 0 --- 0

22/04/17 4:45 a 16.7 0 NNW 0

22/04/17 5:00 a 16.6 0 NNW 0

22/04/17 5:15 a 16.6 0 NNW 0

22/04/17 5:30 a 16.5 0 NNW 0

22/04/17 5:45 a 16.4 0 --- 0

22/04/17 6:00 a 16.3 0 --- 0





22/04/17 6:15 a 16.3 0 NNW 0

22/04/17 6:30 a 16.4 0 NNW 0

22/04/17 6:45 a 16.5 0 NNW 0

22/04/17 7:00 a 16.7 0 NNW 0

22/04/17 7:15 a 17.1 0 NNW 0

22/04/17 7:30 a 17.5 0 NNW 0

22/04/17 7:45 a 18.1 0.4 NNW 0

22/04/17 8:00 a 18.6 0 WNW 0

22/04/17 8:15 a 18.9 0.4 WNW 0

22/04/17 8:30 a 19.3 0.4 WNW 0

22/04/17 8:45 a 19.8 0.4 WNW 0

22/04/17 9:00 a 20 0.4 WNW 0

22/04/17 9:15 a 20.3 0.4 NW 0

22/04/17 9:30 a 20.8 0.4 WNW 0

22/04/17 9:45 a 21.3 0.4 WNW 0

22/04/17 10:00 a 21.7 0.4 NW 0

22/04/17 10:15 a 21.9 0.4 WNW 0

22/04/17 10:30 a 22.3 0 WNW 0

22/04/17 10:45 a 22.9 0 W 0

22/04/17 11:00 a 23.1 0.4 W 0

22/04/17 11:15 a 23.2 0.4 WNW 0

22/04/17 11:30 a 23.2 0 WNW 0

22/04/17 11:45 a 23.4 0 W 0

22/04/17 12:00 p 24.2 0 WSW 0

22/04/17 12:15 p 23.8 0.4 W 0

22/04/17 12:30 p 23.9 0 WNW 0

22/04/17 12:45 p 24.1 0 WNW 0

22/04/17 1:00 p 23.9 0.4 WNW 0

22/04/17 1:15 p 23.9 0 WNW 0

22/04/17 1:30 p 24.1 0 WNW 0

22/04/17 1:45 p 24.4 0 SSE 0

22/04/17 2:00 p 24.3 0 SSE 0

22/04/17 2:15 p 23.9 0 WSW 0

22/04/17 2:30 p 23.7 0 WNW 0

22/04/17 2:45 p 23.7 0 WSW 0

22/04/17 3:00 p 23.6 0 SSW 0

22/04/17 3:15 p 23.4 0 WNW 0

22/04/17 3:30 p 23.2 0 WNW 0

22/04/17 3:45 p 23.1 0 S 0

22/04/17 4:00 p 23.2 0 S 0

22/04/17 4:15 p 23 0 S 0

22/04/17 4:30 p 22.9 0 S 0

22/04/17 4:45 p 22.7 0 S 0

22/04/17 5:00 p 22.6 0 S 0

22/04/17 5:15 p 22.3 0 SW 0

22/04/17 5:30 p 22.1 0 --- 0





22/04/17 5:45 p 21.9 0 --- 0

22/04/17 6:00 p 21.7 0 WSW 0

22/04/17 6:15 p 21.6 0 WSW 0

22/04/17 6:30 p 21.4 0 --- 0

22/04/17 6:45 p 21.2 0 --- 0

22/04/17 7:00 p 21 0 --- 0

22/04/17 7:15 p 20.8 0 --- 0

22/04/17 7:30 p 20.7 0 --- 0

22/04/17 7:45 p 20.6 0 --- 0

22/04/17 8:00 p 20.4 0 --- 0

22/04/17 8:15 p 20.3 0 --- 0

22/04/17 8:30 p 20.2 0 --- 0

22/04/17 8:45 p 19.9 0 --- 0

22/04/17 9:00 p 19.7 0 --- 0

22/04/17 9:15 p 19.4 0 --- 0

22/04/17 9:30 p 19.3 0 --- 0

22/04/17 9:45 p 19.3 0 --- 0

22/04/17 10:00 p 19.4 0 --- 0

22/04/17 10:15 p 19.2 0 --- 0

22/04/17 10:30 p 19.1 0 --- 0

22/04/17 10:45 p 19.1 0 WSW 0

22/04/17 11:00 p 19 0 --- 0

22/04/17 11:15 p 18.9 0 --- 0

22/04/17 11:30 p 18.8 0 --- 0

22/04/17 11:45 p 18.6 0 --- 0

23/04/17 12:00 a 18.4 0 --- 0

23/04/17 12:15 a 18.4 0 --- 0

23/04/17 12:30 a 18.5 0 --- 0

23/04/17 12:45 a 18.6 0 --- 0

23/04/17 1:00 a 18.7 0 --- 0

23/04/17 1:15 a 18.9 0 WSW 0

23/04/17 1:30 a 18.9 0 --- 0

23/04/17 1:45 a 18.9 0 --- 0

23/04/17 2:00 a 18.8 0 --- 0

23/04/17 2:15 a 18.7 0 WSW 0

23/04/17 2:30 a 18.7 0 WSW 0

23/04/17 2:45 a 18.7 0 WSW 0

23/04/17 3:00 a 18.7 0 WSW 0

23/04/17 3:15 a 18.6 0 WSW 0

23/04/17 3:30 a 18.4 0 WSW 0

23/04/17 3:45 a 18.3 0 WSW 0

23/04/17 4:00 a 18.2 0 WSW 0

23/04/17 4:15 a 18 0 WSW 0

23/04/17 4:30 a 17.9 0 WSW 0

23/04/17 4:45 a 17.8 0 WSW 0

23/04/17 5:00 a 17.6 0 WSW 0





23/04/17 5:15 a 17.4 0 WSW 0

23/04/17 5:30 a 17.3 0 WSW 0

23/04/17 5:45 a 17.3 0 WSW 0

23/04/17 6:00 a 17.2 0 WSW 0

23/04/17 6:15 a 17.1 0 --- 0

23/04/17 6:30 a 17.1 0 WSW 0

23/04/17 6:45 a 17.2 0 WSW 0

23/04/17 7:00 a 17.4 0 WSW 0

23/04/17 7:15 a 17.7 0.4 W 0

23/04/17 7:30 a 18 0.4 W 0

23/04/17 7:45 a 18.4 0.4 WNW 0

23/04/17 8:00 a 18.7 0.4 NW 0

23/04/17 8:15 a 19.2 0.4 WNW 0

23/04/17 8:30 a 19.6 0.4 WNW 0

23/04/17 8:45 a 20.1 0 WNW 0

23/04/17 9:00 a 20.5 0 WNW 0

23/04/17 9:15 a 20.9 0 WNW 0

23/04/17 9:30 a 21.2 0.4 WNW 0

23/04/17 9:45 a 21.6 0.4 W 0

23/04/17 10:00 a 21.9 0.4 WNW 0

23/04/17 10:15 a 22.3 0 W 0

23/04/17 10:30 a 22.8 0 WNW 0

23/04/17 10:45 a 22.8 0.4 WNW 0

23/04/17 11:00 a 22.9 0 WNW 0

23/04/17 11:15 a 23.4 0 WNW 0

23/04/17 11:30 a 23.5 0.4 WNW 0

23/04/17 11:45 a 23.3 0 WNW 0

23/04/17 12:00 p 23.7 0 WNW 0

23/04/17 12:15 p 23.6 0 SW 0

23/04/17 12:30 p 24.1 0.4 WSW 0

23/04/17 12:45 p 24.2 0.4 SW 0

Table C2 - Position 2 Monitoring - Meteorological Data



01/08/17 2:00 p 25.1 0.4 NW 0

01/08/17 2:15 p 25.7 0.4 ENE 0

01/08/17 2:30 p 25.2 0.9 WNW 0

01/08/17 2:45 p 24.3 1.3 WNW 0

01/08/17 3:00 p 23.4 1.3 WNW 0

01/08/17 3:15 p 23 0.9 W 0

01/08/17 3:30 p 22.3 0.9 NNW 0

01/08/17 3:45 p 21.7 0.9 NNW 0

01/08/17 4:00 p 21.2 0.4 W 0

01/08/17 4:15 p 20.4 0.9 WNW 0

01/08/17 4:30 p 19.8 0.9 NW 0





01/08/17 4:45 p 19.4 0.4 W 0

01/08/17 5:00 p 18.8 0.4 NW 0

01/08/17 5:15 p 18.3 0.4 NNW 0

01/08/17 5:30 p 17.9 0.4 WNW 0

01/08/17 5:45 p 17.5 0 NW 0

01/08/17 6:00 p 16.8 0 --- 0

01/08/17 6:15 p 16.2 0 NW 0

01/08/17 6:30 p 15.8 0 NNW 0

01/08/17 6:45 p 15.5 0 NNW 0

01/08/17 7:00 p 15.3 0 W 0

01/08/17 7:15 p 15.1 0 WNW 0

01/08/17 7:30 p 14.9 0 WNW 0

01/08/17 7:45 p 14.8 0 NW 0

01/08/17 8:00 p 14.5 0 --- 0

01/08/17 8:15 p 14.3 0 NW 0

01/08/17 8:30 p 14.3 0 NW 0

01/08/17 8:45 p 14 0 NW 0

01/08/17 9:00 p 13.7 0 NW 0

01/08/17 9:15 p 13.5 0 --- 0

01/08/17 9:30 p 13.2 0 --- 0

01/08/17 9:45 p 13.1 0 --- 0

01/08/17 10:00 p 12.7 0 --- 0

01/08/17 10:15 p 12.4 0 --- 0

01/08/17 10:30 p 12.2 0 --- 0

01/08/17 10:45 p 12.1 0 --- 0

01/08/17 11:00 p 12 0 NW 0

01/08/17 11:15 p 12.1 0 NW 0

01/08/17 11:30 p 12.1 0 NW 0

01/08/17 11:45 p 11.7 0 --- 0

02/08/17 12:00 a 11.3 0 --- 0

02/08/17 12:15 a 10.9 0 --- 0

02/08/17 12:30 a 10.6 0 --- 0

02/08/17 12:45 a 10.2 0 --- 0

02/08/17 1:00 a 9.8 0 --- 0

02/08/17 1:15 a 9.6 0 --- 0

02/08/17 1:30 a 9.4 0 --- 0

02/08/17 1:45 a 9.2 0 --- 0

02/08/17 2:00 a 9.1 0 --- 0

02/08/17 2:15 a 8.9 0 --- 0

02/08/17 2:30 a 8.8 0 --- 0

02/08/17 2:45 a 8.9 0 --- 0

02/08/17 3:00 a 9.2 0 NW 0

02/08/17 3:15 a 9.4 0 NW 0

02/08/17 3:30 a 9.4 0 --- 0

02/08/17 3:45 a 9.3 0 --- 0

02/08/17 4:00 a 9.1 0 --- 0





02/08/17 4:15 a 8.9 0 --- 0

02/08/17 4:30 a 8.7 0 --- 0

02/08/17 4:45 a 8.8 0 --- 0

02/08/17 5:00 a 8.8 0 --- 0

02/08/17 5:15 a 8.8 0 --- 0

02/08/17 5:30 a 8.8 0 --- 0

02/08/17 5:45 a 8.8 0 --- 0

02/08/17 6:00 a 8.8 0 --- 0

02/08/17 6:15 a 8.8 0 --- 0

02/08/17 6:30 a 8.8 0 --- 0

02/08/17 6:45 a 8.7 0 --- 0

02/08/17 7:00 a 8.8 0 NW 0

02/08/17 7:15 a 9.2 0 NW 0

02/08/17 7:30 a 9.8 0 NNW 0

02/08/17 7:45 a 10.7 0 NE 0

02/08/17 8:00 a 11.6 0 ENE 0

02/08/17 8:15 a 12.3 0 NNW 0

02/08/17 8:30 a 13.2 0.4 NNW 0

02/08/17 8:45 a 14.2 0.4 ENE 0

02/08/17 9:00 a 15.3 0.4 NW 0

02/08/17 9:15 a 16 0.4 ENE 0

02/08/17 9:30 a 16.7 0.4 ENE 0

02/08/17 9:45 a 17.2 0.4 NNW 0

02/08/17 10:00 a 18.2 0.4 NNW 0

02/08/17 10:15 a 19.1 0.4 NW 0

02/08/17 10:30 a 19.6 0.4 ENE 0

02/08/17 10:45 a 20.3 0.4 NW 0

02/08/17 11:00 a 20.7 0.4 NW 0

02/08/17 11:15 a 21 0.4 NNW 0

02/08/17 11:30 a 21.4 0.4 NW 0

02/08/17 11:45 a 21.6 0.4 NNW 0

02/08/17 12:00 p 22.2 0.4 NW 0

02/08/17 12:15 p 22.8 0.4 NW 0

02/08/17 12:30 p 23.3 0 SW 0

02/08/17 12:45 p 23.7 0.4 SSW 0

02/08/17 1:00 p 23.7 0.4 WNW 0

02/08/17 1:15 p 23.7 0 S 0

02/08/17 1:30 p 24.2 0 SSE 0

02/08/17 1:45 p 24.6 0.4 SSW 0

02/08/17 2:00 p 24.4 0.4 SSE 0

02/08/17 2:15 p 24 0.4 SSE 0

02/08/17 2:30 p 23.7 0.4 SE 0

02/08/17 2:45 p 24.2 0.4 SSE 0

02/08/17 3:00 p 23.7 0.9 SSE 0

02/08/17 3:15 p 23.3 0.9 W 0

02/08/17 3:30 p 22.7 0.4 SSW 0





02/08/17 3:45 p 22.2 0.4 W 0

02/08/17 4:00 p 21.4 1.3 WNW 0

02/08/17 4:15 p 20.9 0.4 WNW 0

02/08/17 4:30 p 20.4 0.4 W 0

02/08/17 4:45 p 19.8 0.4 W 0

02/08/17 5:00 p 19.3 0.4 WNW 0

02/08/17 5:15 p 18.8 0 WNW 0

02/08/17 5:30 p 18.3 0 W 0

02/08/17 5:45 p 17.8 0 W 0

02/08/17 6:00 p 17.2 0 --- 0

02/08/17 6:15 p 16.7 0 --- 0

02/08/17 6:30 p 16.2 0 --- 0

02/08/17 6:45 p 15.8 0 --- 0

02/08/17 7:00 p 15.4 0 --- 0

02/08/17 7:15 p 14.9 0 --- 0

02/08/17 7:30 p 14.6 0 --- 0

02/08/17 7:45 p 14.3 0 --- 0

02/08/17 8:00 p 14 0 --- 0

02/08/17 8:15 p 13.7 0 --- 0

02/08/17 8:30 p 13.4 0 --- 0

02/08/17 8:45 p 13.2 0 --- 0

02/08/17 9:00 p 12.9 0 --- 0

02/08/17 9:15 p 12.8 0 --- 0

02/08/17 9:30 p 12.6 0 --- 0

02/08/17 9:45 p 12.4 0 --- 0

02/08/17 10:00 p 12.3 0 --- 0

02/08/17 10:15 p 12.2 0 --- 0

02/08/17 10:30 p 11.9 0 --- 0

02/08/17 10:45 p 11.8 0 --- 0

02/08/17 11:00 p 11.7 0 --- 0

02/08/17 11:15 p 11.7 0 --- 0

02/08/17 11:30 p 11.6 0 --- 0

02/08/17 11:45 p 11.4 0 --- 0

03/08/17 12:00 a 11.3 0 --- 0

03/08/17 12:15 a 11.3 0 --- 0

03/08/17 12:30 a 11.4 0 --- 0

03/08/17 12:45 a 11.6 0 --- 0

03/08/17 1:00 a 11.6 0 --- 0

03/08/17 1:15 a 11.6 0 --- 0

03/08/17 1:30 a 11.6 0 --- 0

03/08/17 1:45 a 11.5 0 --- 0

03/08/17 2:00 a 11.5 0 --- 0

03/08/17 2:15 a 11.6 0 --- 0

03/08/17 2:30 a 11.7 0 --- 0

03/08/17 2:45 a 11.6 0 --- 0

03/08/17 3:00 a 11.6 0 --- 0





03/08/17 3:15 a 11.5 0 --- 0

03/08/17 3:30 a 11.4 0 --- 0

03/08/17 3:45 a 11.4 0 --- 0

03/08/17 4:00 a 11.2 0 --- 0

03/08/17 4:15 a 11 0 --- 0

03/08/17 4:30 a 10.8 0 --- 0

03/08/17 4:45 a 10.6 0 --- 0

03/08/17 5:00 a 10.4 0 --- 0

03/08/17 5:15 a 10.3 0 --- 0

03/08/17 5:30 a 10.2 0 --- 0

03/08/17 5:45 a 10.1 0 --- 0

03/08/17 6:00 a 10.1 0 --- 0

03/08/17 6:15 a 10.2 0 W 0

03/08/17 6:30 a 10.3 0 --- 0

03/08/17 6:45 a 10.4 0 --- 0

03/08/17 7:00 a 10.6 0 W 0

03/08/17 7:15 a 10.8 0 W 0

03/08/17 7:30 a 11.4 0 NW 0

03/08/17 7:45 a 12.1 0 N 0

03/08/17 8:00 a 12.8 0 NNE 0

03/08/17 8:15 a 13.7 0 NE 0

03/08/17 8:30 a 14.6 0 ENE 0

03/08/17 8:45 a 15.1 0 NNW 0

03/08/17 9:00 a 15.8 0.4 NNW 0

03/08/17 9:15 a 16.6 0.4 NW 0

03/08/17 9:30 a 16.9 0.4 NNW 0

03/08/17 9:45 a 17.5 0.4 NW 0

03/08/17 10:00 a 18.6 0 ENE 0

03/08/17 10:15 a 19.4 0.4 NW 0

03/08/17 10:30 a 20.1 0.4 NW 0

03/08/17 10:45 a 20.5 0.4 NNW 0

03/08/17 11:00 a 21.1 0.4 NNW 0

03/08/17 11:15 a 21.6 0.4 NNW 0

03/08/17 11:30 a 22.3 0.4 NNW 0

03/08/17 11:45 a 22.9 0.4 NNW 0

03/08/17 12:00 p 22.9 0 NW 0

03/08/17 12:15 p 22.7 0.4 SSE 0

03/08/17 12:30 p 22.8 0.4 WNW 0

03/08/17 12:45 p 22.7 0.4 SSE 0

03/08/17 1:00 p 23.3 0.4 WNW 0

03/08/17 1:15 p 23.8 0.4 SSE 0

03/08/17 1:30 p 23 0.9 SSE 0

03/08/17 1:45 p 22.9 0.4 SSE 0

03/08/17 2:00 p 22.6 0.4 S 0

03/08/17 2:15 p 22.3 0.4 SSE 0

03/08/17 2:30 p 22.7 0.4 SSE 0





03/08/17 2:45 p 22.2 0.4 W 0

03/08/17 3:00 p 22.6 0.9 W 0

03/08/17 3:15 p 22.6 0.9 SSE 0

03/08/17 3:30 p 21.8 0.4 SSE 0

03/08/17 3:45 p 21.2 0.4 S 0

03/08/17 4:00 p 20.8 0.4 S 0

03/08/17 4:15 p 20.4 0.4 W 0

03/08/17 4:30 p 20.1 0 SSE 0

03/08/17 4:45 p 19.8 0 W 0

03/08/17 5:00 p 19.5 0.4 W 0

03/08/17 5:15 p 19.2 0 WSW 0

03/08/17 5:30 p 18.9 0 SSW 0

03/08/17 5:45 p 18.5 0 --- 0

03/08/17 6:00 p 18.2 0 SSW 0

03/08/17 6:15 p 17.7 0 --- 0

03/08/17 6:30 p 17.3 0 --- 0

03/08/17 6:45 p 17.1 0 --- 0

03/08/17 7:00 p 16.8 0 --- 0

03/08/17 7:15 p 16.3 0 --- 0

03/08/17 7:30 p 15.9 0 --- 0

03/08/17 7:45 p 15.6 0 --- 0

03/08/17 8:00 p 15.2 0 --- 0

03/08/17 8:15 p 14.9 0 --- 0

03/08/17 8:30 p 14.7 0 --- 0

03/08/17 8:45 p 14.5 0 --- 0

03/08/17 9:00 p 14.2 0 --- 0

03/08/17 9:15 p 14.1 0 --- 0

03/08/17 9:30 p 14.1 0 --- 0

03/08/17 9:45 p 13.9 0 --- 0

03/08/17 10:00 p 13.9 0 --- 0

03/08/17 10:15 p 13.8 0 --- 0

03/08/17 10:30 p 13.7 0 --- 0

03/08/17 10:45 p 13.6 0 --- 0

03/08/17 11:00 p 13.3 0 --- 0

03/08/17 11:15 p 13.1 0 --- 0

03/08/17 11:30 p 12.9 0 --- 0

03/08/17 11:45 p 13.1 0 --- 0

04/08/17 12:00 a 13.4 0 --- 0

04/08/17 12:15 a 13.5 0 --- 0

04/08/17 12:30 a 13.6 0 --- 0

04/08/17 12:45 a 13.8 0 --- 0

04/08/17 1:00 a 13.8 0 --- 0

04/08/17 1:15 a 13.8 0 --- 0

04/08/17 1:30 a 13.9 0 --- 0

04/08/17 1:45 a 14.2 0 --- 0

04/08/17 2:00 a 14.4 0 --- 0





04/08/17 2:15 a 14.6 0 SSW 0

04/08/17 2:30 a 15.2 0 SSW 0

04/08/17 2:45 a 15.8 0 S 0

04/08/17 3:00 a 16 0 --- 0

04/08/17 3:15 a 16.2 0 --- 0

04/08/17 3:30 a 16.1 0 --- 0

04/08/17 3:45 a 15.8 0 --- 0

04/08/17 4:00 a 15.6 0 --- 0

04/08/17 4:15 a 15.4 0 --- 0

04/08/17 4:30 a 15.5 0 --- 0

04/08/17 4:45 a 15.6 0 SSE 0

04/08/17 5:00 a 15.7 0 SSE 0

04/08/17 5:15 a 15.7 0 SSE 0

04/08/17 5:30 a 15.9 0 SSE 0

04/08/17 5:45 a 16.1 0 SSW 0

04/08/17 6:00 a 16.1 0 SSE 0

04/08/17 6:15 a 15.9 0 SSE 0

04/08/17 6:30 a 16.1 0.4 SSE 0

04/08/17 6:45 a 16.2 0.9 SSE 0

04/08/17 7:00 a 16.1 0.9 SSE 0

04/08/17 7:15 a 16.1 0.4 SSE 0

04/08/17 7:30 a 16.3 0.4 SSE 0

04/08/17 7:45 a 16.6 0.4 SSE 0

04/08/17 8:00 a 16.9 0.4 ENE 0

04/08/17 8:15 a 17.2 0.9 ENE 0

04/08/17 8:30 a 17.6 0.4 ENE 0

04/08/17 8:45 a 17.8 0.9 NE 0

04/08/17 9:00 a 18.1 0.9 ENE 0

04/08/17 9:15 a 18.3 0.4 NE 0

04/08/17 9:30 a 18.6 0.9 SSE 0

04/08/17 9:45 a 18.8 0.9 SSE 0

04/08/17 10:00 a 19.4 0.9 ENE 0

04/08/17 10:15 a 19.8 0.9 ENE 0

04/08/17 10:30 a 20.1 0.9 SSE 0

04/08/17 10:45 a 20.1 1.3 SSE 0

04/08/17 11:00 a 20.4 0.9 ENE 0

04/08/17 11:15 a 20.7 1.3 ENE 0

04/08/17 11:30 a 21.1 1.3 NE 0

04/08/17 11:45 a 21.2 1.3 SSE 0

04/08/17 12:00 p 21.6 0.9 SE 0



Appendix D – Noise Contour Plots



Figure D1 - Predicted 2017 Noise Levels – No Upgrade

Year: 2017

Scenario: No Upgrade

Location: Grange

Height Above Ground: 4.6 m

Units: dB(A)

Noise Parameter: LA10,18-hour (Facade-corrected)

Criteria: 68 dB(A)



Figure D2 - Predicted 2017 Noise Levels – With Upgrade

Year: 2017

Scenario: With Upgrade

Location: Grange


Units: dB(A)


Criteria: 68 dB(A)



Figure D3 - Predicted 2029 Noise Levels – No Upgrade

Year: 2029

Scenario: No Upgrade

Location: Grange


Units: dB(A)


Criteria: 68 dB(A)



Figure D4 - Predicted 2029 Noise Levels – With Upgrade

Year: 2029

Scenario: With Upgrade

Location: Grange


Units: dB(A)


Criteria: 68 dB(A)



Road Traffic Noise Assessment - Grange Road and Raymont ... · Executive Summary Brisbane City...

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