Orora Compliance Monitoring

Orora Compliance Monitoring ORORA LIMITED

April Noise Monitoring

038900_20150420 | A

29 April 2015


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Orora Compliance Monitoring

Project no: IA038900

Document title: April Noise Monitoring

Document no: 038900_20150429

Revision: A

Date: 29 April 2015

Client name: Orora Limited

Client no: _

Project manager: J Ball

Author: S Hughes

File name: H:\Orora\Orora_April noise monitoring 20150423.docx

Jacobs Group (Australia) Pty Limited ABN 37 001 024 095 100 Christie Street St Leonards NSW 2065 Australia PO Box 164 St Leonards NSW 2065 Australia T +61 2 9928 2100 F +61 2 9928 2500 www.jacobs.com

COPYRIGHT: The concepts and information contained in this document are the property of Jacobs Group (Australia) Pty Limited. Use or copying of this document in whole or in part without the written permission of Jacobs constitutes an infringement of copyright.

Document history and status

Revision Date Description By Review Approved

A 29/04/2015 Issued for approval S Hughes B Ison 29/04/2015


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Contents Glossary ................................................................................................................................................................ iii

1. Introduction ................................................................................................................................................ 1

1.1 Background ..................................................................................................................................................................................... 1

1.2 Objective ......................................................................................................................................................................................... 1

1.3 Monitoring limitations ...................................................................................................................................................................... 1

1.4 Receiver locations .......................................................................................................................................................................... 1

1.5 Operational noise limits .................................................................................................................................................................. 3

2. Operational noise monitoring .................................................................................................................. 4

2.1 Monitoring results ........................................................................................................................................................................... 5

2.1.1 Discussion of results ....................................................................................................................................................................... 5

2.2 Comparison with previous monitoring ............................................................................................................................................. 8

3. Summary .................................................................................................................................................... 9

Appendix A. Noise logger graphs

Appendix B. LA90 1 min noise monitoring results (filtered)

Appendix C. LAeq 1 minute noise monitoring results (filtered)


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Glossary Acoustic and vibration related terms:

Acoustic Spectrum: A representation of a sound sample (usually short term) of the amount of energy or

sound level per frequency.

Ambient Noise: Ambient noise encompasses all sound present in a given environment, being usually a

composite of sounds from many sources near and far.

CONCAWE: noise modelling algorithm to predict the geographical propagation of noise from various noise

sources

CoRTN: Calculation of Road Traffic Noise (CRTN - ISBN 0 11 550847 3, UK Department of Transport

1988)

dB(A): A unit of sound measurement which has frequency characteristics weighted so that it approximates

the response of the human ear to sound waves

ENMM: Environmental Noise Management Manual (RMS, 2001)

eVDV: Is the estimated vibration dose for predicting an assessing human comfort exposure, measured as

ms-1.75

Heavy Vehicle: A truck, transport or other vehicle with a gross vehicle weight above a specified level (for

example: over 8 tonnes)

LA10: Descriptor used to define noise level which is exceeded 10 per cent of the time and is to the average

of maximum noise levels

LA10 (18hr): Is the arithmetic average of the L 10(1hr) levels for the 18-hour period between 0600 and 2400

hours on a normal working day.

LA90: Is the noise level that is exceeded 90 per cent of the measurement time. This parameter is commonly

referred to as the background noise level

LAeq: Noise level that represents the energy average noise from the source during a specified time period,

and is the equivalent continuous sound pressure level for a given period

LAeq(15hr): The Leq noise level for the period from 7 am to 10 pm.

LAeq(9hr): The Leq noise level for the period from 10 pm to 7 am.

NCA: Noise Catchment Area. Grouping dwellings or receivers together in terms of similar noise

environment.

Noise barrier: Generally a wall or an earth mound that obstructs or restricts the passage of sounds waves

from a noise source

Noise Logger: A data logging (data and audio in some cases) which records noise. Usually used for

unattended noise monitoring of background or ambient noise.

NML: Noise Management Level as detailed in the NSW Interim Construction Noise Guideline. The NML is

the noise goal for construction activities.

Octave Bands: Sounds that contain energy over a wide range of frequencies are divided into sections

called bands. A common standard division is in 10 octave bands identified by their center frequencies 31.5,

63, 250, 500, 1000, 2000, and 4000 Hz

PPV: Peak Particle Velocity is is used to measure vibration through a solid surface. When a vibration is

measured, the point at which the measurement takes place can be considered to have a particle velocity.

This particle vibration will take place in three dimensions (x, y and z) and will usually end up back where it

started. The Peak Particle Velocity is the maximum velocity that is recorded during a particular event.


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RBL: Rating Background Level is the overall single figure background level representing each assessment

period over the whole monitoring period. The RBL is used for determining the appropriate construction

noise criteria.

RNP: Road Noise Policy (OEH, 2011)

Sound Level Meter: An instrument consisting of a microphone, amplifier and data analysis package for

quantifying and measuring noise.

Sound Power Level (Lw): Sound power level or acoustic power level is a logarithmic measure of the sound

power in comparison to a specified reference level.

Sound Pressure Level (SPL or Lp): The level of noise, usually expressed in dB(A), as measured by a

standard sound level meter.

VDV: Measured vibration dose value to indicate compliance with human comfort criteria

Vibration: Vibration is a force which oscillates about some specified reference point. Vibration is commonly

expressed in terms of frequency such as cycles per second (cps), Hertz (Hz), cycles per minute (cpm) or

(rpm) and strokes per minute (spm). This is the number of oscillations which occurs in that time period. The

amplitude is the magnitude or distance of travel of the force.


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Important note about your report

The sole purpose of this report and the associated services performed by Jacobs is to report on the quarterly monitoring for the Orora Paper Machine B9 operational noise levels in accordance with the scope of services set out in the contract between Jacobs and the Client. That scope of services, as described in this report, was developed with the Client.

In preparing this report, Jacobs has relied upon, and presumed accurate, any information (or confirmation of the absence thereof) provided by the Client and/or from other sources. Except as otherwise stated in the report, Jacobs has not attempted to verify the accuracy or completeness of any such information. If the information is subsequently determined to be false, inaccurate or incomplete then it is possible that our observations and conclusions as expressed in this report may change.

Jacobs derived the data in this report from information sourced from the Client (if any) and/or available in the public domain at the time or times outlined in this report. The passage of time, manifestation of latent conditions or impacts of future events may require further examination of the project and subsequent data analysis, and re-evaluation of the data, findings, observations and conclusions expressed in this report. Jacobs has prepared this report in accordance with the usual care and thoroughness of the consulting profession, for the sole purpose described above and by reference to applicable standards, guidelines, procedures and practices at the date of issue of this report. For the reasons outlined above, however, no other warranty or guarantee, whether expressed or implied, is made as to the data, observations and findings expressed in this report, to the extent permitted by law.

This report should be read in full and no excerpts are to be taken as representative of the findings. No responsibility is accepted by Jacobs for use of any part of this report in any other context.

This report has been produced based on the data sample taken during the field survey of noise and vibration impacts and the conclusions in this assessment reflect the limitations of this data set.

This report has been prepared on behalf of, and for the exclusive use of, Jacobs’s Client, and is subject to, and issued in accordance with, the provisions of the contract between Jacobs and the Client. Jacobs accepts no liability or responsibility whatsoever for, or in respect of, any use of, or reliance upon, this report by any third party. Introduction


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1. Introduction

1.1 Background

In May 2012, ORORA Packaging began constructing the new B9 Paper Mill at its Botany site in Sydney, NSW. The New Paper Mill would replace the two existing papermaking machines (No. 7 and No. 8) at the site. The New Paper Mill is subject to operational noise conditions set out in Ministers Conditions of Approval (MCoA) (including subsequent modifications) and the Environment Protection Licence (EPL) No. 1594.

As part of the EPL, there is a requirement to undertake quarterly monitoring at receivers surrounding the site to show compliance with set noise limits. At the time of preparing this report, the B9 paper machine has been operating for 30 months and is currently operating at 90% production. Traffic within the site accesses via Botany Road and exits via McCauley Road as per the site traffic plan.

There are no recent modifications or upgrades to the site layout or operations and the B7 paper machine building, scheduled for demolition, remains in situ.

1.2 Objective

This report presents the details of operational licence conditions for noise measurements of the noise environment around the Orora site during a period of shut down and operations. The purpose of this document is to satisfy Condition M6.1 and M6.2 of EPL 1594 as follows:

M6.1 The licensee must undertake noise monitoring at least once every three months to check

compliance with the noise limits specified in Condition L4.1.

M6.2 All monitoring required by this licence must be undertaken in accordance with Australian Standard

2659.1 – 1998: Guide to the use of sound measuring equipment – Portable sound level meters, or any

revisions of that standard which may be made by Australian Standards Authority, and the compliance

monitoring guidance provided in the NSW Industrial Noise Policy.

1.3 Monitoring limitations

The Orora monitoring survey relies on the cooperation of the local community to place loggers in key locations used in the compliance assessment, and Orora gratefully acknowledges this fact. While the noise surveys are scheduled to give residents enough notice of upcoming activities, the meteorological conditions during these surveys are not always favourable to the collection of data.

In the most recent noise monitoring survey, long term monitoring was undertaken over a period of about one week at five of the six receiver locations due to construction activities at one of the properties. The receiver at R1 (see Figure 1) was monitored using a handheld sound level meter for a 15 minute period. The results from this location have been used in the assessment of noise levels and the compliance monitoring for the April period.

1.4 Receiver locations

The EPL provides guidance on the location of six noise measurement sites to be reported for the quarterly monitoring. The position of these sites relative to the Orora site is presented in Figure 1.


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Figure 1 Compliance monitoring locations

Observations of the typical noise environment at each receiver location have been generalised to assist in the discussion and understanding of general noise impacts at these locations.

Receiver 1: The receiver at this location has a large degree of acoustic shielding from local noise sources due to a boundary noise wall located on the opposite side of Australia Avenue. The noise environment at this location is heavily influenced by traffic on McCauley Street, Perry Street and Beauchamp Road. Local industrial noise from Raymond Avenue is also audible during the day and night time.

Receiver 2: This receiver is located opposite the bottom apex of the Purcell Park on Australia Avenue. At this location residences have a clear line of sight to the paper mill. Noise walls have less effectiveness for the residences due to the large separation distances. Noise from port activities also has less shielding from the Orora site. Background noise levels are heavily dominated by road traffic noise from all sources.

Receiver 3: These receivers are the closest and most exposed to general operational activities having less benefit of shielding from the boundary wall. At the end of Murrabbin Avenue, the terrain is slightly elevated further reducing any attenuation from the noise wall. Receivers in Murrabin Avenue also have elevated background noise levels generated by Botany Road and Bunnerong Road.

Receiver 4: The receivers at Partanna Avenue are physically the closest to the Orora site but have the benefit of significant shielding of operational activities from the B7 paper machine building and the No. 7 reel store. Road traffic noise contributes to background noise for this receiver.

Receiver 5::Physically the furthest location from the Orora site, having a higher degree of influence from Botany Road, Bunnerong Road and the port. Noise from the Orora site is generally inaudible at this location although significant noise from the Orora site has been observed here during adverse meteorological conditions.

Receiver 6: In this location receivers are well shielded from operational noise from the Orora site due to the presence of the redundant No. 7 and No. 8 paper machine buildings. Noise levels at this location are heavily influenced by local bird colonies, port noise, traffic on Botany road and traffic on Bunnerong Road.

R1

R3

R4

R6

ORORA

R2

R5


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1.5 Operational noise limits

Operational noise limits for the new Orora Paper Mill are detailed in condition L4.1 of EPL 1594 and Condition 10 of the MCoA. These have been replicated in Table 1.

Table 1 Operational noise limits

ID Location Day

LAeq,15min, dB(A)

Evening LAeq,15min, dB(A)

Night LAeq,15min, dB(A)

Night LAmax,

dB(A)

R1 Cnr. McCauley Street and Australia Avenue

46 45 43 55

R2 Australia Avenue 45 45 43 55

R3 Murrabin Avenue 46 45 43 55

R4 Partanna Avenue 42 41 41 55

R5 Cnr. Partanna and Moorina Avenues

42 42 39 55

R6 Moorina Avenue 43 43 39 55


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2. Operational noise monitoring

Operational noise monitoring for the April 2015 quarter has been incorporated into a six day monitoring survey. Due to access issues at receiver R1, noise loggers were deployed at five of the six representative locations and were operational for the duration of the survey.

The measurements were taken using Acoustic Research Laboratories Ngara Type 1 noise loggers, set to record noise levels continuously over consecutive 24 hour periods at each location.

Weather conditions during the noise survey were obtained from the BOM and the nearby automatic weather station located at Sydney Airport. The weather data was incorporated into the monitoring results to provide an indication of the quality of the data.

Weather conditions for the monitoring period have been sourced from the Bureau of Meteorology (Sydney Airport) and plotted showing daily trends in wind speed which are presented in Figure 2.

Figure 2 Wind speed and direction during monitoring period

The plotted data indicates that the wind direction generally blew from between the north west to westerly directions affecting receiver locations in the south east and east of the Orora site. Stronger winds from the south and south-south west were also recorded for the monitoring period. These conditions typically favour an increase in the local noise environment with noise from sources such as Botany Road and Sydney Ports having a greater contribution to ambient noise levels.

Wind speeds during the monitoring period included about 50% of measured velocities above 5 m/s.


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2.1 Monitoring results

The purpose of the noise monitoring survey is to distinguish the noise emissions from the Orora site from the ambient noise environment Noise sources audible at the monitoring locations represent a large variety of acoustic influences from the area, which contribute to the overall local noise environment. The LAeq noise level parameter that is the basis of the Orora operational criteria is therefore affected by all other extraneous noise sources in the area.

Generally Orora operations have a noise profile consistent with plant and equipment that operate at more or less a steady state level and therefore there is little variability in noise emissions from the site. This type of noise emission is in contrast with other noise sources in the local area. To assist in identifying the site noise emissions, the LA90 statistical parameter has been considered in conjunction with the LAeq noise level to provide additional information for assessment of impacts.

The parameters of LAeq and LA90 are used to provide information for comparison against the project criteria and the background noise environment. Noise levels at R1 are reported against attended monitoring only for the April monitoring period. A summary of the noise monitoring results is presented in Table 2. The results of long term monitoring have been graphed and are shown in Appendix A with areas of grey shading indicating adverse weather conditions recorded at the time of monitoring.

The most recent round of compliance measurements presents details of the noise environment with the Orora site operational. Table 2 presents the assessment background noise levels and the rating background noise levels as well as the LAeq, 15 minute for each assessment period.

Due to the complex noise environment surrounding the Orora site, it is impractical to directly measure the contribution of Orora operations when monitoring at nearby receiver locations. Evidence of this is provided in earlier studies where the measured LAeq noise levels at compliance locations are consistently above the EPL criteria, even when the Orora site is not operational.

To further assist in the understanding of the local noise environment, additional graphs of the measured 1 minute results for the LAeq and LA90 parameters have been plotted against time of day over the duration of the noise survey at each of the monitoring sites. These results demonstrate the spread of noise levels recorded at each site and are presented in Appendices B and C.

2.1.1 Discussion of results

Observations during the survey period suggest that the Orora site was occasionally audible in the general acoustic environment but was not the dominant noise source. Some activities such as truck movements (deliveries or pick ups) represent the more audible components of site activities however; these audible events tend to be infrequent.

The ambient measured noise levels during the survey are consistently above the EPL criteria for day evening and night operations of the Orora site, but these levels are not wholly attributable to Orora’s contribution. The measured levels indicate a significant variation in the short term noise levels at all sites throughout the day evening and night. The typically high noise levels measured during this survey period are expected to be influenced by the prevailing strong winds, predominantly from the south, south-west and westerly directions.


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Table 2 Summary of noise monitoring

Time and date* Profile of Noise Environment - Noise Monitoring Location¥

R1 R2 R3 R4 R5 R6

7:00:00 AM to 6:00:00 PM L90 (10th Percentile)

Leq - over period

L90 (10th Percentile)

Leq - over period


Leq - over period


Leq - over period


Leq - over period


Leq - over period

Wednesday 8 April 2015

Thursday 9 April 2015 51.7 56.0 50.5 56.7 47.8 54.8 48.95 58.1 46.3 54.3

Friday 10 April 2015 50.0 53.7 48.6 52.7 47.2 59.0 46.3 54.3 46.2 53.7

Saturday 11 April 2015 38.5 52.0 39.6 49.3 39.6 54.2 38.6 52.0 41.4 52.1

Sunday 12 April 2015 45.7 52.0 45.2 50.8 42.3 50.0 41.8 51.2 41.0 53.0

Monday 13 April 2015 47.4 54.0 46.2 51.2 44.3 57.5 43.0 56.9 44.1 53.1

Tuesday 14 April 2015 38.8 50.3 39.5 50.1 40.4 55.6 41.0 54.7 41.3 51.0

Wednesday 15 April 2015 40.9 53.5 41.9 51.0 41.4 52.4 41.4 52.9

Median 42.0 56.0 45.7 53.5 45.2 51.0 42.3 54.8 42.4 54.5 41.4 53.0

6:00:00 PM to 10:00:00 PM L90 (10th Percentile)

Leq - over period


Leq - over period


Leq - over period


Leq - over period


Leq - over period


Leq - over period


Thursday 9 April 2015

Friday 10 April 2015 48.9 56.8 46.5 51.1 43.7 50.0 41.5 52.0

Saturday 11 April 2015 38.0 59.9 41.1 46.2 37.3 46.7 43.3 51.0 39.7 50.4

Sunday 12 April 2015 47.7 51.5 46.3 49.9 42.6 48.7 39.1 50.4 42.7 49.5

Monday 13 April 2015 45.8 50.8 44.5 48.3 41.5 52.0 41.5 50.5 41.4 47.7

Tuesday 14 April 2015 37.2 47.6 39.2 45.6 37.6 48.8 40.1 48.3 39.4 47.0


Median - - 45.8 51.5 44.5 48.3 41.5 48.8 40.8 50.5 41.4 49.5


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Time and date* Profile of Noise Environment - Noise Monitoring Location¥

R1 R2 R3 R4 R5 R6

10:00:00 PM to 7:00:00 AM L90 (10th Percentile)

Leq - over period


Leq - over period


Leq - over period


Leq - over period


Leq - over period


Leq - over period

Wednesday 8 April 2015 49.5 54.5 48.4 54.1 47.1 52.3 45.7 52.2

Thursday 9 April 2015 47.9 52.4 46.4 50.1 43.9 48.2 46.0 51.7 39.5 47.1

Friday 10 April 2015 45.1 50.6 44.5 48.6 38.5 43.5 42.0 47.6 38.3 47.1

Saturday 11 April 2015 43.2 48.4 44.1 47.5 39.3 43.8 39.2 44.9 36.7 45.0

Sunday 12 April 2015 46.0 50.7 44.5 48.1 41.2 45.7 42.4 45.6 37.0 44.5

Monday 13 April 2015 41.9 48.9 42.4 46.8 38.6 43.3 39.9 44.8 34.1 43.5

Tuesday 14 April 2015 40.4 49.1 42.4 48.0 38.0 43.7 37.7 45.8 35.3 43.0


Median 56.0 58.1 45.1 50.6 44.5 48.1 39.3 43.8 41.0 45.7 37.0 45.0 ¥ Blanks are shown where data is excluded due to adverse weather.


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2.2 Comparison with previous monitoring

An indicator of the contribution of Orora operational noise to existing noise levels may be made using background noise levels measured during survey. During the night time period fewer extraneous noise influences are present providing lower overall noise levels in the area. Under these conditions constant noise sources such as Orora operations are more likely to be apparent in the background noise levels during this time.

The data in Table 3 provides a chronological progression of noise data for both shutdown and operational conditions over several years. These results demonstrate the degree of variability in the noise environment at these locations due to seasonal and local influences.

The background noise levels from Table 3 are not directly related to the LAeq criteria; however, they provide an indication of the increase in background environmental noise levels during periods of activity within the Orora site.

Measurements recorded in July 2014 (shaded) are representative of background noise levels resulting from adverse meteorology (temperature inversion), and are not typical of noise influences in the area.

Table 3 Comparison of background noise (rounded)

ID Location

EPL - Night LA90

15min

Operational (O) or Shutdown (S)

S O O S O S O O

05/12

Night RBL

08/13

Night LA90

15min

07/14

Night LA90

15min

09/14

Night RBL

09/14

Night RBL

01/15

Night RBL

01/15

Night RBL

04/15

Night RBL

R1

Cnr. McCauley Street and Australia Avenue

43 46 44 47 39 40 36 38 -

R2 Australia Avenue

43 46 46 50 47 - 35 35 45

R3 Murrabin Avenue

43 42 48 52 38 43 39 39 45

R4 Partanna Avenue

41 41 42 47 42 41 41 40 39

R5 Cnr. Partanna and Moorina Avenues

39 43 42 46 - - - 40 41

R6 Moorina Avenue

39 43 44 44 38 38 33 34 37


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3. Summary

When the LAeq measured noise levels during the April monitoring survey are compared to the criteria outlined in Orora’s EPL No. 1594, exceedances of the day, evening, and night time periods are indicated. Observations from previous studies indicate that the Orora B9 operations have only a minor contribution to the noise environment in the local area and therefore the measured noise levels do not solely reflect emissions from the site.

The local meteorological conditions have a significant influence on the measured noise levels. The weather patterns recorded during the April survey generally favoured the propagation of noise from the direction of the major noise sources such as Orora, Botany Road, and Sydney Ports. These conditions influence the measured noise levels for the April period towards the residential locations to the east and north-east of the Orora site.

It is expected that continued compliance monitoring will add more detail to the noise emission data collected in the area and enhance the current understanding of Orora’s operational noise contribution. Currently, it is the opinion of the Jacob’s representative, that Orora is operating within the noise goals outlined in its EPL.


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Appendix A. Noise logger graphs

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Profile of Noise Environment ‐ Noise Monitoring Location 2Wednesday 8 April 2015

Data Excluded from Analysis L1 L10 L90 Leq Ave Wind Speed (m/s) Ave Air Temp (degC) Measurable Rainfall

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60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)






038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)


dB(A)





038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)






038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)






038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)






038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)





0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)






038900_20150429

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0

5

10

15

20

25

30

35

40

45

50

55

60

65

70

75

80

85

90

0:00 2:00 4:00 6:00 8:00 10:00 12:00 14:00 16:00 18:00 20:00 22:00 0:00

Air Te

mperatu

re (D

egC) ‐

and

Wind Sp

eed (m

/s)






038900_20150429

Appendix B. LA90 1 min noise monitoring results (filtered)

35.0

37.5

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM

L A90Noise Level d

B(A)

Time of Day

Receiver R2 ‐ Background noise level

Measured 1 Min LA90

35.0

37.5

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM

L A90Noise Level dB(A)

Time of Day


Measured 1 min LA90


038900_20150429

35.0

37.5

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM


Time of Day


Measutred 1 Min LA90

35.0

37.5

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM


Time of Day




038900_20150429

35.0

37.5

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM


Time of Day




038900_20150429

Appendix C. LAeq 1 minute noise monitoring results (filtered)

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

62.5

65.0

67.5

70.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM

L AeqNoise Level d

B(A)

Time of Day

Receiver R2 ‐ Ambient noise level

Measured 1 Min LAeq

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

62.5

65.0

67.5

70.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM

L AeqNoise Level d

B(A)

Time of Day


Measured 1 Min LAeq


038900_20150429

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

62.5

65.0

67.5

70.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM

L AeqNoise Level d

B(A)

Time of Day


Measured 1 Min LAeq

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

62.5

65.0

67.5

70.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM

L AeqNoise Level d

B(A)

Time of Day


Measured 1 Min LAeq


038900_20150429

40.0

42.5

45.0

47.5

50.0

52.5

55.0

57.5

60.0

62.5

65.0

67.5

70.0

12:00 AM

01:00 AM

02:00 AM

03:00 AM

04:00 AM

05:00 AM

06:00 AM

07:00 AM

08:00 AM

09:00 AM

10:00 AM

11:00 AM

12:00 PM

01:00 PM

02:00 PM

03:00 PM

04:00 PM

05:00 PM

06:00 PM

07:00 PM

08:00 PM

09:00 PM

10:00 PM

11:00 PM

L AeqNoise Level d

B(A)

Time of Day


Measured 1 min LAeq

Documents

Orora Compliance Monitoring