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NATA ACCREDITATION No. 2778 (14391) Accredited for compliance with ISO/IEC 17025 This document is issued in accordance with NATA’s accreditation requirements. This document may not be reproduced except in full. Orora Limited 09-Apr-2014 Emissions Testing Report 2014 Orora Limited

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Page 1: Emissions Testing Report 2014 · 2018-04-02 · This document may not be reproduced except in full. 09-Apr-2014 Emissions Testing Report 2014 ... Distance from Upstream Disturbance

NATA ACCREDITATION No. 2778 (14391) Accredited for compliance with ISO/IEC 17025 This document is issued in accordance with NATA’s accreditation requirements. This document may not be reproduced except in full.

Orora Limited 09-Apr-2014

Emissions Testing Report 2014 Orora Limited

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AECOM Emissions Testing Report 2014

09-Apr-2014 Prepared for – Orora Limited – ABN: 55 004 275 165

Emissions Testing Report 2014 Orora Limited

Client: Orora Limited

ABN: 55 004 275 165

Prepared by AECOM Australia Pty Ltd 17 Warabrook Boulevard, Warabrook NSW 2304, PO Box 73, Hunter Region MC NSW 2310, Australia T +61 2 4911 4900 F +61 2 4911 4999 www.aecom.com ABN 20 093 846 925

09-Apr-2014

Job No.: 60318558

AECOM in Australia and New Zealand is certified to the latest version of ISO9001, ISO14001, AS/NZS4801 and OHSAS18001.

© AECOM Australia Pty Ltd (AECOM). All rights reserved.

AECOM has prepared this document for the sole use of the Client and for a specific purpose, each as expressly stated in the document. No other party should rely on this document without the prior written consent of AECOM. AECOM undertakes no duty, nor accepts any responsibility, to any third party who may rely upon or use this document. This document has been prepared based on the Client’s description of its requirements and AECOM’s experience, having regard to assumptions that AECOM can reasonably be expected to make in accordance with sound professional principles. AECOM may also have relied upon information provided by the Client and other third parties to prepare this document, some of which may not have been verified. Subject to the above conditions, this document may be transmitted, reproduced or disseminated only in its entirety.

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AECOM Emissions Testing Report 2014

09-Apr-2014 Prepared for – Orora Limited – ABN: 55 004 275 165

Table of Contents 1.0 Introduction 1 2.0 Sampling Plane Requirements 3 3.0 Methodology 5

3.1 NATA Accredited Methods 5 4.0 Sampling Location 7

4.1 Sampling Location Summary 7 5.0 Equipment Calibration 9 6.0 Results 11 Appendix A

Field Sheets and Final Calculations (34 pages) A Appendix B

Laboratory Analysis (2 pages) B Appendix C

Raw and Calculated Gas Data (12 pages) C

List of Tables

Table 1 Criteria for Selection of Sampling Planes (AS 4323.1-1995) 3 Table 2 AECOM NATA Endorsed Methods 5 Table 3 Sampling Location Summary 7 Table 4 Emission Testing Results Summary, 18 March 2014. 11 Table 5 Gas Data Results, 18 March 2014 11 Table 6 Stack 1 Fine Particulate (PM10) and Total Particulate Results, 18 March 2014 12 Table 7 Stack 2 Fine Particulate (PM10) and Total Particulate Results, 18 March 2014 13

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1.0 Introduction AECOM was appointed by Orora Limited to conduct a series of measurements to determine air emissions from Boiler Stacks 1 and 2 at the Port Botany Facility. Measurements were required for NSW EPA Licence compliance (NSW EPA Licence No. 1594).

Testing was undertaken on 18 March 2014 to investigate emission concentrations for the following parameters:

- Total Particulate (TP);

- Fine Particulate (PM10); and

- Oxides of Nitrogen.

Laboratory Analysis was undertaken by the following laboratory which holds NATA accreditation for the specified tests: - Steel River Testing Pty Ltd, NATA accreditation number 18079, performed the following analysis detailed in

report number 6232-0-P and 6232-0-M.

Particulates; and

Moisture.

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2.0 Sampling Plane Requirements The Criteria for Sampling Planes are specified in AS 4323.1-1995. Table 1 Criteria for Selection of Sampling Planes (AS 4323.1-1995)

Type of flow disturbance Minimum distance upstream from disturbance, diameters (D)

Minimum distance downstream from disturbance, diameters (D)

Bend, connection, junction, direction change

>2D >6D

Louvre, butterfly damper (partially closed or closed)

>3D >6D

Axial fan >3D >8D (see Note)

Centrifugal fan >3D >6D

NOTE: The plane should be selected as far as practicable from a fan. Flow straighteners may be required to ensure the position chosen meets the check criteria listed in Items (a) to (f) below.

a. The gas flow is basically in the same direction at all points along each sampling traverse;

b. The gas velocity at all sampling points is greater than 3 m/s;

c. The gas flow profile at the sampling plane shall be steady, evenly distributed and not have a cyclonic component which exceeds an angle of 15o to the duct axis, when measured near the periphery of a circular sampling plane;

d. The temperature difference between adjacent points of the survey along each sampling traverse is less than 10% of the absolute temperature, and the temperature at any point differs by less than 10% from the mean;

e. The ratio of the highest to lowest pitot pressure difference shall not exceed 9:1 and the ratio of highest to lowest gas velocities shall not exceed 3:1. For isokinetic testing with the use of impingers, the gas velocity ratio across the sampling plane should not exceed 1.6:1; and

f. The gas temperature at the sampling plane should preferably be above the dewpoint.

The sampling planes tested satisfied the above criteria.

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3.0 Methodology

3.1 NATA Accredited Methods The following methods are accredited with the National Association of Testing Authorities (NATA) (accreditation number 2778 (14391)) and are approved for the sampling and analysis of gases. Specific details of the methods are available on request.

All sampling and analysis is conducted according to the methods in Table 2. Table 2 AECOM NATA Endorsed Methods

NSW EPA Approved Methods USEPA Methods Method Title

AS4323.1 (NSW EPA TM-1)

USEPA (2000) Method 1 Selection of sampling positions

AS4323.2 (NSW EPA TM-15)

USEPA (2000) Method 5 under approved circumstances

Determination of total particulate matter – isokinetic manual sampling – gravimetric method

NSW EPA TM-11 USEPA (2000) Method 7 Nitrogen dioxide (NO2) or nitric oxide (NO)

NSW EPA TM-2 USEPA (2000) Method 2 or 2C or USEPA (1999) Method 2F or 2G or 2H (as appropriate)

Determination of stack gas velocity and volumetric flow rate (type s pitot tube)

NSW EPA TM-22 USEPA (2000) Method 4 Determination of moisture content in stack gases

NSW EPA TM-23 USEPA (2000) Method 3 Gas analysis for the determination of dry molecular weight

NSW EPA OM-5 ‘Fine’ particulates (PM10) USEPA (1997) Method 201 or 201A (as appropriate)

All parameters are reported adjusted to 0oC at 1 atmosphere and dry gas.

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4.0 Sampling Location

4.1 Sampling Location Summary Table 3 provides a summary of the location sampled by AECOM on 18 March 2014.

Table 3 Sampling Location Summary

Discharge Description Stack 1 Stack 2

Duct Shape Circular Circular

Construction Material Metal Metal

Duct Diameter (mm) 1960 1960

Minimum No. Sampling Points 16 16

Sampling Ports 2 2

Min. Points/Traverse 8 8

Disturbance No No

Distance from Upstream Disturbance ~7D ~7D

Type of Disturbance Junction Junction

Distance from Downstream Disturbance ~2D ~2D

Type of Disturbance Stack Exit Stack Exit

Ideal Sampling Location Yes Yes

Correction Factors Applied No No

Total No. Points Sampled1 16 16

Points/Traverse 8 8

Sampling Performed to Standard2 Yes Yes 1NSW EPA OM-5 (USEPA Method 201 & 201A) states the maximum number of sampling points for a fine particulate (PM10) testing shall not exceed a total of 12, as such only 12 points were tested for this test. 2AS 4323.1 Stationary source emissions Method 1 – Selection of sampling positions.

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5.0 Equipment Calibration AECOM has a calibration schedule to ensure the emission testing equipment is maintained in good order and with known calibration. Equipment used in this project was calibrated according to the procedures and frequency identified in the AECOM calibration schedule. Details of the schedule and the calibration calculations are available on request.

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6.0 Results A summary of the air emission test results and gas data results are shown in Tables 4-5 respectively. Detailed results along with gas stream properties during the testing periods can be found in Tables 6-7. All emission concentrations are converted to standard conditions of 0oC, dry gas and 1 atmosphere pressure for comparison with appropriate guideline levels.

AECOM has a calculated limit of uncertainty in regards to results. The estimation of measurement uncertainty in source testing is conducted to provide an indication of the precision of the measurement result and a degree of confidence in the range of values the reported result may represent. The measurement of uncertainty has been calculated at ±13.6%.

Field sheets and final calculations can be referred to in Appendix A and analytical results are provided in Appendix B. Raw and calculated gas data, relating to Oxides of Nitrogen can be referred to in Appendix C. Table 4 Emission Testing Results Summary, 18 March 2014.

Parameter Stack 1

(Boilers 1 and 2) Stack 2

(Boilers 3 and 4) Regulatory Limit

Fine Particulate (PM10) (mg/m3) <0.26 <0.26 N/A

Total Particulate (TP) (mg/m3) 0.17 0.18 100 Table 5 Gas Data Results, 18 March 2014

Parameter Stack 1 (Boilers 1 and 2)

Stack 2 (Boilers 3 and 4)

Regulatory Limit

Sampling Time 12:08-13:08 14:57-15:57 60 mins

Stack gas flowrate (0°C, dry gas, 1 atm pressure) (m3/s) 9.2 10

Oxides of Nitrogen (NOx) (mg/m3) 57 46

Oxides of Nitrogen (NOx) (mg/s) 524 460

Nitrogen Oxide (NO) (mg/m3) 42 42

Nitrogen Oxide (NO) (mg/s) 386 420

Nitrogen Dioxide (NO2) (mg/m3) 14 4

Nitrogen Dioxide (NO2) (mg/s) 129 40

Equivalent Nitrogen Dioxide (NO2) (mg/m3) 79 69 200

Equivalent Nitrogen Dioxide (NO2) (mg/s) 727 690

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Table 6 Stack 1 Fine Particulate (PM10) and Total Particulate Results, 18 March 2014

Sampling Conditions:

Stack internal diameter at test location 1690 mm

Stack gas temperature (average) 127.3 oC 400.5 K

Stack pressure (average) 1018 hPa

Stack gas velocity (average, stack conditions) 6.9 m/s

Stack gas flowrate (stack conditions) 16 m3/s

Stack gas flowrate (0°C, dry gas, 1 atm pressure) 9.2 m3/s Fine Particulate (PM10) Testing

Test Period 12:06 - 13:30

Fine Particulate (PM10) Mass <0.2 mg

Gas Volume Sampled 0.778 m3

Fine Particulate (PM10) Emission*1 <0.26 mg/m3

Fine Particulate (PM10) Mass Emission Rate*2 <2.4 mg/s

Regulatory Limit NA Total Particulate Testing

Test Period 12:06 - 13:30

Total Particulate Mass 0.2 mg

Gas Volume Sampled 1.16 m3

Total Particulate Emission*1 0.17 mg/m3

Total Particulate Mass Emission Rate*2 1.5 mg/s

Regulatory Limit 100 mg/m3 Moisture Content (%) 14.0 Gas Density (dry at 1 atmosphere) 1.32 kg/m3 Dry Molecular Weight 29.6 g/g-mole Notes *1 Emission concentration at Standard conditions of 0°C, 1 atm, dry gas *2 Mass emission rate determined from pre and post-test sampling flow measurements and the respective test moisture content. See Qstd in field sheets and final calculations "Stack Analysis - Final Calculations" for each test.

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Table 7 Stack 2 Fine Particulate (PM10) and Total Particulate Results, 18 March 2014

Sampling Conditions:

Stack internal diameter at test location 1690 mm

Stack gas temperature (average) 121.8 oC 395.0 K

Stack pressure (average) 1018 hPa

Stack gas velocity (average, stack conditions) 7.6 m/s

Stack gas flowrate (stack conditions) 17 m3/s

Stack gas flowrate (0°C, dry gas, 1 atm pressure) 10 m3/s Fine Particulate (PM10) Testing

Test Period 14:54 - 16:17

Fine Particulate (PM10) Mass <0.2 mg

Gas Volume Sampled 0.772 m3

Fine Particulate (PM10) Emission*1 <0.26 mg/m3

Fine Particulate (PM10) Mass Emission Rate*2 <2.6 mg/s

Regulatory Limit NA Total Particulate Testing

Test Period 14:54 - 16:17

Total Particulate Mass 0.2 mg

Gas Volume Sampled 1.11 m3

Total Particulate Emission*1 0.18 mg/m3

Total Particulate Mass Emission Rate*2 1.8 mg/s

Regulatory Limit 100 mg/m3 Moisture Content (%) 15.0 Gas Density (dry at 1 atmosphere) 1.32 kg/m3 Dry Molecular Weight 29.6 g/g-mole

Notes *1 Emission concentration at Standard conditions of 0°C, 1 atm, dry gas *2 Mass emission rate determined from pre and post-test sampling flow measurements and the respective test moisture content. See Qstd in field sheets and final calculations "Stack Analysis - Final Calculations" for each test.

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Appendix A

Field Sheets and Final Calculations (34 pages)

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Appendix A Field Sheets and Final Calculations (34 pages)

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Appendix B

Laboratory Analysis (2 pages)

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Appendix B Laboratory Analysis (2 pages)

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Appendix C

Raw and Calculated Gas Data (12 pages)

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Appendix C Raw and Calculated Gas Data (12 pages)

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AECOM Australia Pty Ltd Error! Unknown document property name. Error! Unknown document property name. ABN 20 093 846 925

This is the last page of the report

AECOM AECOM Australia Pty Ltd 17 Warabrook Boulevard Warabrook NSW 2304 PO Box 73 Hunter Region MC NSW 2310 Australia T +61 2 4911 4900 F +61 2 4911 4999 www.aecom.com ABN 20 093 846 925