McArthur River Mining orroloola aravan and Devils Spring ......from MRM Borroloola station on the...
Transcript of McArthur River Mining orroloola aravan and Devils Spring ......from MRM Borroloola station on the...
McArthur River Mining
Borroloola Caravan and Devils Spring Stations
Ambient Air Quality Monitoring
Validated Report
1st July 2016 – 31st July 2016
Report No.: DAT10991
Report issue date: 25th August 2016
Maintenance contract: MC1100, MC1101
ECOTECH PTY LTD. ABN: 32005752081
1492 Ferntree Gully Rd, Knoxfield VIC. 3180. AUSTRALIA
Tel No: 1300 364 946 Fax No: 1300 668 763
Email [email protected] WEB www.ecotech.com
This document shall not be reproduced except for in full, without the written approval of Ecotech Pty Ltd.
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Customer Details
Customer McArthur River Mining
Contact name Sebastien Moreno
Email [email protected]
Phone (08) 8975 8137
Revision History
Revision Report ID Date Analyst
0 DAT10991 25/08/2016 Caroline Knight
Report by: Caroline Knight
Approved Signatory: Jon Alexander
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Table of Contents Customer Details ....................................................................................................................................... 2
Revision History ........................................................................................................................................ 2
Table of Contents ...................................................................................................................................... 3
List of Figures ............................................................................................................................................ 4
List of Tables ............................................................................................................................................. 4
Executive Summary ....................................................................................................................................... 6
1.0 Introduction ...................................................................................................................................... 7
2.0 Monitoring and Data Collection ........................................................................................................ 7
2.1. Siting Details.................................................................................................................................. 7
2.2. Monitored Parameters ................................................................................................................. 8
2.3. Data Collection Methods ............................................................................................................ 10
2.3.1. Compliance with Standards ................................................................................................ 11
2.3.2. Data Acquisition .................................................................................................................. 12
2.4. Data Validation and Reporting .................................................................................................... 12
2.4.1. Validation ............................................................................................................................ 12
2.4.2. Reporting ............................................................................................................................. 12
3.0 Air Quality Goals ............................................................................................................................. 13
4.0 Calibrations and Maintenance ........................................................................................................ 13
4.1. Units and Uncertainties .............................................................................................................. 13
4.2. Maintenance ................................................................................................................................... 15
4.2.1. Calibration & Maintenance Summary Tables ......................................................................... 15
4.2.2. Maintenance Notes ................................................................................................................. 15
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5.0 Results ............................................................................................................................................. 16
5.1. Data Capture ............................................................................................................................... 16
5.2. Air Quality Summary ................................................................................................................... 18
5.3. Data Summary Tables ................................................................................................................. 18
5.4 Graphic Representations ............................................................................................................ 20
6.0 Valid Data Exception Tables ............................................................................................................ 26
7.0 Report Summary ............................................................................................................................. 28
Appendix 1 - Definitions & Abbreviations ................................................................................................... 29
Appendix 2 - Explanation of Exception Table ............................................................................................. 30
List of Figures Figure 1: MRM Monitoring Stations Locations ............................................................................................. 8
Figure 2: Borroloola Caravan Station SO2 1 Hour Averages for July 2016 .................................................. 20
Figure 3: Borroloola Caravan station SO2 24 Hour Averages for July 2016 ................................................ 21
Figure 4: Borroloola Caravan Station Wind Rose for July 2016 .................................................................. 22
Figure 5: Devils Spring SO2 1 Hour Averages for July 2016 ......................................................................... 23
Figure 6: Devils Spring SO2 24 Hour Averages for July 2016 ....................................................................... 24
Figure 7: Devils Spring Station Wind Rose July 2016 .................................................................................. 25
List of Tables Table 1: MRM monitoring station locations ................................................................................................. 7
Table 2: Parameters measured at the MRM Borroloola Caravan and Devils Spring monitoring stations ... 9
Table 3: Data Collection Methods............................................................................................................... 10
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Table 4: NEPM Air Quality Goals for Borroloola Caravan and Devils Spring monitoring stations .............. 13
Table 5: Units and Uncertainties ................................................................................................................. 13
Table 6: MRM Borroloola Caravan Maintenance Table July 2016 .............................................................. 15
Table 7: MRM Devils Spring Maintenance Table July 2016 ........................................................................ 16
Table 8: Monthly Data Capture for MRM Borroloola Caravan Station for July 2016 ................................. 17
Table 9: Monthly Data Capture for MRM Devils Spring Station for July 2016............................................ 17
Table 10: Exceedances recorded for July 2016 ........................................................................................... 18
Table 11: SO2 5 Minute Data Summary Table ............................................................................................. 18
Table 12: SO2 1 Hour Data Summary Table ................................................................................................ 19
Table 13: SO2 24 Hour Data Summary Table .............................................................................................. 19
Table 14: MRM Borroloola Caravan Valid Data Exception Table ................................................................ 26
Table 15: MRM Devils Spring Valid Data Exception Table .......................................................................... 27
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Executive Summary
McArthur River Mining is one of the world’s largest providers of zinc in bulk concentrate form1. The
mine is located in the Northern Territory approximately 970km south-east from Darwin and 60km
south-west of Borroloola 2
Ecotech PTY LTD is providing air monitoring and data collection from two McArthur River Mining
(MRM) ambient air monitoring stations at two sites: Borroloola Caravan and Devils Spring. Both
stations are equipped to monitor SO2, wind speed, and wind direction. Borroloola Caravan is also
equipped with solar radiation, barometric pressure, ambient temperature, relative humidity and
rainfall.
This report presents the data collected at the Borroloola Caravan and Devils Spring stations in July
2016.
Data capture for SO2 at Devils Spring was 95% for SO2 and 100% capture for wind speed and wind
direction.
Data capture at Borroloola Caravan was 95% for SO2 and 100% for wind speed, wind direction,
ambient temperature, relative humidity, barometric pressure and rainfall. Percentage data capture
for solar radiation during July 2016 was 96%.
There were no recorded exceedances over the SO2 air quality goals for either station during July 2016.
1 Glencore McArthur River Mining Website http://www.mcarthurrivermine.com.au/EN/Pages/default.aspx
2 Release of Independent Monitor Report - MRM, 23/10/2014
http://www.mcarthurrivermine.com.au/EN/Media/Documents/Independent%20Monitor%20Report.pdf
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1. Introduction Ecotech Pty Ltd was commissioned by MRM to provide monitoring and data reporting for two ambient
air quality monitoring stations, located as detailed in Table 1. Ecotech commenced data collection
from MRM Borroloola station on the 17th June, and Devils Spring station on the 20th June 2015.
MRM Borroloola station was decommissioned on 1st March, and re-commissioned on the same day
new instruments and a permanent enclosure. The station remains in the same location as the previous
Borroloola station. It has been renamed Borroloola Caravan.
This report presents data for July 2016.
The data presented in this report:
Describes air quality measurements;
Compares monitoring results;
Has been quality assured;
2. Monitoring and Data Collection
2.1. Siting Details The network consists of two ambient air quality monitoring stations. The stations’ location and siting
details are described below.
Table 1: MRM monitoring station locations
Site Name Geographical Coordinates Height Above Sea Level (m)
Borroloola Caravan 16° 5'19"S, 136°30'40"E 21m
Devils Spring 16° 9'27"S, 136° 5'51"E 70m
Siting audits to assess for compliance with AS/NZS 3580.14:2011 ‘Methods for sampling and analysis of
ambient air – Method 14: Meteorological monitoring for ambient air quality monitoring applications’ were
performed on 2nd March 2016 at Devils Spring and 3rd March 2016 Borroloola Caravan station.
Siting audits to assess for compliance with AS/NZS 3580.1.1:2007 “Methods for sampling and analysis of
ambient air – guide to siting of air monitoring equipment” were completed on 18th March 2016 at both
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Devils Spring and Borroloola Caravan stations. Both were found to be compliant and classified as
Background sites.
Figure 1: MRM Monitoring Stations Locations
2.2. Monitored Parameters Table 2 below details the parameters monitored and the instruments used at the Borroloola and
Devils Springs monitoring stations. Appendix 1 defines any abbreviated parameter names used
throughout the report.
For meteorological sensors, the elevation given in the table below is the height above ground level at
the monitoring station.
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Table 2: Parameters measured at the MRM Borroloola Caravan and Devils Spring monitoring stations
Station Parameter Measured Instrument and Measurement
Technique
Borroloola
SO2
Ecotech S50 - fluorescence
Wind Speed (horizontal, elevation 10m)
Vaisala WXT520 – ultrasonic
Wind Direction (elevation 10m)
Vaisala WXT520 – ultrasonic
Sigma Calculation (Yamartino method)
Solar Radiation Middleton SK01-D2
Rain Vaisala WXT520
Barometric Pressure Vaisala WXT520
Ambient Temperature Vaisala WXT520
Relative Humidity Vaisala WXT520
Devils Spring
SO2
Ecotech EC9850B – fluorescence
Wind Speed (horizontal, elevation 10m)
Gil Windsonic OP3 – ultrasonic
Wind Direction (elevation 10m)
Gil Windsonic OP3 – ultrasonic
Sigma Calculation (Yamartino method)
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2.3. Data Collection Methods Table 3 below outlines the methods used for data collection. Any deviations from the stated methods
are detailed in section 2.3.1.
Table 3: Data Collection Methods
Parameter
Measured
Data Collection
Methods Used Description of Method
SO2
AS 3580.4.1 - 2008 Methods for sampling and analysis of ambient air. Method 4.1:
Determination of sulfur dioxide – Direct reading instrumental method
Ecotech Laboratory Manual
In-house method 6.2 Sulfur dioxide by fluorescence
Rain
AS/NZS 3580.14 2014
Methods for sampling and analysis of ambient air. Method 14: Meteorological monitoring for ambient air quality monitoring
applications
Ecotech Laboratory Manual
In-house method 8.7 – Rainfall by tipping bucket rain gauge
Solar Radiation
AS/NZS 3580.14 2014
Methods for sampling and analysis of ambient air. Method 14: Meteorological monitoring for ambient air quality monitoring
applications
Ecotech Laboratory Manual
In-house method 8.6 – Global solar radiation and Net radiation by pyranometer and net pyrradiometer
Ambient Temperature
(elevation 10m)
AS 3580.14 2014 Methods for sampling and analysis of ambient air. Method 14: Meteorological monitoring for ambient air quality monitoring
applications
Ecotech Laboratory Manual
In-house method 8.4 Temperature ambient by thermoelectric techniques
Relative Humidity
AS/NZS 3580.14 2014
Methods for sampling and analysis of ambient air. Method 14: Meteorological monitoring for ambient air quality monitoring
applications
Ecotech Laboratory Manual
In-house method 8.5 – Relative humidity by hygrometer
Barometric Pressure
AS/NZS 3580.14 2014
Methods for sampling and analysis of ambient air. Method 14: Meteorological monitoring for ambient air quality monitoring
applications
Ecotech Laboratory Manual
In-house method 8.9 – Barometric pressure by solid state pressure transducer
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Parameter
Measured
Data Collection
Methods Used Description of Method
Vector Wind Speed (Horizontal)
AS 3580.14 2014 Methods for sampling and analysis of ambient air. Method 14: Meteorological monitoring for ambient air quality monitoring
applications
Ecotech Laboratory Manual
In-house method 8.1 Wind speed (Horizontal) by anemometer
Vector Wind
Direction
AS 3580.14 2014 Methods for sampling and analysis of ambient air. Method 14: Meteorological monitoring for ambient air quality monitoring
applications
Ecotech Laboratory Manual
In-house method 8.3 Wind direction by anemometer
Sigma
AS 3580.14 2014 Methods for sampling and analysis of ambient air. Method 14: Meteorological monitoring for ambient air quality monitoring
applications
Ecotech Laboratory Manual
In-house method 8.3 Wind direction by anemometer
2.3.1. Compliance with Standards
Unless stated below, parameters are monitored at the MRM Borroloola Caravan and Devils Spring
Stations according to the methods detailed in Table 3 above.
Measurement of wind speed and wind direction by the Vaisala WXT520 does not meet
performance criteria of AS 3580.14 2014
Measurement of SO2 at Devils Spring does not meet the requirements of AS 3580.4.1 – 2008.
A proficiency check has not been performed on the instrument. Maintenance has not been
performed in according to the prescribed maintenance schedule.
Measurement of SO2 at Borroloola Caravan does not meet the requirements of AS 3580.4.1–
2008 as maintenance has not been carried out according to the prescribed maintenance
schedule.
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2.3.2. Data Acquisition
Data acquisition is performed using a PC based WinAQMS logger (using WinAQMS Version 2.3)
situated at each of the monitoring sites. Each logger is equipped with a 3G modem for remote data
collection. The recorded data is remotely collected from the AQMS loggers on a daily basis (using
AirodisTM version 5.1) and stored at Ecotech’s Environmental Reporting Services (ERS) department in
Melbourne, Australia. Data samples are logged in 5 minute intervals.
2.4. Data Validation and Reporting
2.4.1. Validation
The Ecotech ERS department perform daily data checks to ensure maximum data capture rates are
maintained. Any equipment failures are communicated to the responsible field engineers for urgent
rectification. Ecotech ERS maintains two distinct databases containing non-validated and validated
data respectively.
The validated database is created by duplicating the non-validated database and then flagging data
affected by instrument faults, calibrations and other maintenance activities. The data validation
software requires the analyst to supply a valid reason (e.g. backed by maintenance notes, calibration
sheets etc) in the database for flagging any data as invalid. Details of all invalid or missing data are
recorded in the Valid Data Exception Tables in section 6.
Validation is performed by the analyst, and the validation is reviewed. Graphs and tables are
generated based on the validated 5 minute data.
2.4.2. Reporting
The reported data is presented in two Microsoft Excel format files named “MRM Borroloola Caravan
Validated Data Report July 2016.xls” and “MRM Devils Spring Validated Data Report July 2016”.
The Excel files consist of 5 Excel worksheets:
1. Cover
2. 5 Minute Data
3. 1 Hour Data
4. 24 Hour Data
5. Valid Data Exception Table
The data contained in this report is based on Darwin UTC +9.30 time.
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Averaging periods of eight hours or less are reported for the end of the period, i.e. the hourly average
02:00am is for the data collected from 1:00am to 2:00am. One hour averages are calculated based on
a clock hour. One day averages are calculated based on calendar days.
3. Air Quality Goals The air quality goals for SO2 monitored at the Borroloola Caravan and Devils Spring monitoring
stations are based on the Australian National Environmental Council (NEPC) Ambient Air Quality
NEPM. The air quality goals are shown in Table 4 below.
Table 4: NEPM Air Quality Goals for Borroloola Caravan and Devils Spring monitoring stations
Parameter Time Period Exceedance Level Maximum allowable
exceedances
SO2 1 hour 200ppb (0.2ppm) 1 day a year
SO2 1 Day 80ppb (0.08ppm) 1 day a year
4. Calibrations and Maintenance
4.1. Units and Uncertainties The uncertainties for each parameter have been determined by the manufacturer’s tolerance limits
of the equipment’s parameters, and by the data collection standard method.
The reported uncertainties are expanded uncertainties, calculated using coverage factors which give
a level of confidence of approximately 95%.
Table 5: Units and Uncertainties
Parameter Units Resolution Uncertainty Measurement
Range3
SO2 (S50 and
EC9850B) ppb 1 ppb
± 14 ppb
K factor of 2.01 0 ppb to 500 ppb
3 Uncertainties may not be calculated based on the full measurement range. Uncertainty for SO2 by S50 and
EC9850B is calculated based on a measurement range of 0-125 ppb.
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Parameter Units Resolution Uncertainty Measurement
Range3
Vector Wind
Speed m/s 0.1 m/s
0.22 m/s or 3.0% of reading, whichever is greater
K factor of 1.96 0m/s to 15 m/s
Vector Wind
Direction Deg 1 deg
4 deg
K factor of 2.11
0 deg to 360 deg
Starting threshold:
0 m/s
Barometric
Pressure mbar 1 mbar
2.4 mbar
k factor of 1.96 980 to 1040 mbar
Ambient
Temperature ˚C 0.1˚C
± 0.25˚C
K factor of 2.01 0˚C to 50˚C
Relative
Humidity % 1%
± 5%
K factor of 2.31 0-100%
Rainfall % 0.1 mm
0.60 mm or 7.5% of reading, whichever is the
greater
K factor of 2.14
Rainfall rates of 0
to 80 mm/hr
Solar
Radiation W/m2 1 W/m2
± 5 % of reading or ±32 w/m² or whichever is
greater
K factor of 1.96
0 to 1100 W/m2
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4.2. Maintenance
4.2.1. Calibration & Maintenance Summary Tables The last calibrations for the following parameters were performed on the indicated dates. Data
supplied after this time is subject to further validation, to be performed at the next calibration cycle.
Note: Maintenance and calibration dates may differ, as calibrations may be less frequent than
scheduled maintenance visits.
4.2.2. Maintenance Notes Tables 6 and 7 indicate when the gas and meteorological equipment were last maintained.
Table 6: MRM Borroloola Caravan Maintenance Table July 2016
Parameter Date of Last
Maintenance Maintenance Type
Date of Last
Calibration
Calibration
Cycle
SO2 01/07/2016 Monthly4 01/07/2016 Monthly4
Wind Speed 02/03/2016 3 Monthly 22/05/2015 2 Yearly
Wind Direction 02/03/2016 3 Monthly 22/05/2015 2 Yearly
Ambient Temperature 02/03/2016 6 Monthly 02/03/2016 6 Monthly
Relative Humidity 02/03/2016 6 Monthly 02/03/2016 6 Monthly
Barometric Pressure 02/03/2016 6 Monthly 02/03/2016 6 Monthly
Rain 02/03/2016 6 Monthly 02/03/2016 6 Monthly
Solar Radiation 02/03/2016 6 Monthly 02/03/2016 6 Monthly
4 Remote calibration performed only
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Table 7: MRM Devils Spring Maintenance Table July 2016
Parameter Date of Last
Maintenance Maintenance Type
Date of Last
Calibration
Calibration
Cycle
SO2 01/07/2016 Monthly5 01/07/2016 Monthly5
Wind Speed 03/03/2016 6 Monthly 07/09/2015 2 Yearly
Wind Direction 03/03/2016 6 Monthly 07/09/2015 2 Yearly
5. Results
5.1. Data Capture Data capture is based on 1 hour averages, calculated from 5 minute data, and refers to the amount of
available data collected during the report period.
The percentage of data captured is calculated using the following equation:
Data capture = (Reported air quality data / Total data) x 100%
Where:
Reported air quality data = Number of instrument readings which have been validated through a
quality assured process and excludes all data errors, zero data collection due to calibration,
failures and planned and unplanned maintenance.
Total data = Total number of instrument readings since the start of the term assuming no
maintenance, errors, loss of data or calibration.
5 Remote calibration only
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Tables 8 and 9 below displays data capture statistics for July 2016. Bold values in the table indicate
data capture below 95%. Details of all invalid or missing data affecting data affecting data capture are
included in the Valid Data Exception Tables in section 6 of this report.
Table 8: Monthly Data Capture for MRM Borroloola Caravan Station for July 2016
Parameter Data Capture (%)
SO2 95
WS, WD, Sigma 100
Ambient Temperature 100
Relative Humidity 100
Barometric Pressure 100
Solar Radiation 96
Rain 100
Table 9: Monthly Data Capture for MRM Devils Spring Station for July 2016
Parameter Data Capture (%)
SO2 95
WS, WD, Sigma 100
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5.2. Air Quality Summary
Table 10 records the number of exceedances for SO2 measured at the Borroloola Caravan and Devils
Spring station.
Table 10: Exceedances recorded for July 2016
Parameter Time Period Value of
Exceedance Date of
Exceedance
SO2 1 hour none none
5.3. Data Summary Tables Tables 11 to 13 provide statistical summaries for the SO2 5 minute, 1 hour and 24 hour data at the
Borroloola Caravan and Devils Spring stations.
Table 11: SO2 5 Minute Data Summary Table
SO2 Borroloola Caravan Devils Spring
Maximum (ppb) 113 65
Minimum (ppb) 0 0
Average (ppb) 0 2
Time of Maximum 21/07/2016 07:45 5/07/2016 06:10
Time of Minimum 1/07/2016 12:45 17/07/2016 02:45
99.9th Percentile 44 51
99th Percentile 7 29
90th Percentile 0 4
Capture Percent (%) 95 95
Notes: any negative values have been presented as 0.
‘Nearest rank percentiles’ are used to calculate percentile values.
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Table 12: SO2 1 Hour Data Summary Table
SO2 Borroloola Caravan Devils Spring
Maximum (ppb) 113 49
Minimum (ppb) 0 0
Average (ppb) 0 2
Time of Maximum 21/07/2016 08:00 5/07/2016 07:00
Time of Minimum 1/07/2016 14:00 17/07/2016 19:00
No. of readings >200ppb
0 0
99.9th Percentile 53 49
99th Percentile 7 25
90th Percentile 0 5
Capture Percent (%) 95 95
Table 13: SO2 24 Hour Data Summary Table
SO2 Borroloola Caravan Devils Spring
Maximum (ppb) 5 6
Minimum (ppb) 0 0
Average (ppb) 0 2
Date of Maximum 21/07/2016 5/07/2016
Date of Minimum 26/07/2016 12/07/2016
No. of readings > 80 ppb
0 0
99.9th Percentile 5 6
99th Percentile 5 6
90th Percentile 0 5
Capture Percent (%) 100 100
*Notes: any negative values have been presented as 0.
‘Nearest rank percentiles’ are used to calculate percentile values.
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5.4 . Graphic Representations Validated 5 minute data for all parameters were used to construct the following monthly graphic
representations.
Figure 2: Borroloola Caravan Station SO2 1 Hour Averages for July 2016
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Figure 3: Borroloola Caravan station SO2 24 Hour Averages for July 2016
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Figure 4: Borroloola Caravan Station Wind Rose for July 2016
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Figure 5: Devils Spring SO2 1 Hour Averages for July 2016
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Figure 6: Devils Spring SO2 24 Hour Averages for July 2016
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Figure 7: Devils Spring Station Wind Rose July 2016
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6. Valid Data Exception Tables The tables below detail all changes made to the raw data set during the validation process. An
explanation of reasons given in the table can be found in Appendix 2.
Table 14: MRM Borroloola Caravan Valid Data Exception Table
Start Date End Date Reason Change
Details
User
Name
Change
Date
01/07/2016 00:00 31/07/2016 23:55
Automatic internal reference checks
occurring every night between 23:50 and
23:55
SO2 CK 8/8/16
01/07/2016 01:00 31/07/2016 01:35 Automatic calibration checks occurring
every night between 01:00 and 01:35 SO2 CK 8/8/16
01/07/2016 01:40 31/07/2016 01:40 Intermittent stabilisation following
automatic calibration checks SO2 CK 8/8/16
01/07/2016 09:05 01/07/2016 10:05 Remote calibration SO2 CK 8/8/16
01/07/2016 09:25 01/07/2016 09:25 Data transmission error due to
maintenance All parameters CK 8/8/16
01/07/2016 13:10 31/07/2016 16:00
Intermittent shadow on sensor occurring
between approximately 13:00 and 16:00
throughout the month
SRAD CK 8/8/16
04/07/2016 06:15 04/07/2016 06:25 Intermittent data transmission errors SO2 CK 8/8/16
21/07/2016 13:55 21/07/2016 14:00 Maintenance performed by MRM staff -
filter change and instrument check
SO2 CK 8/8/16
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Table 15: MRM Devils Spring Valid Data Exception Table
Start Date End Date Reason Change
Details
User
Name
Change
Date
01/07/2016 00:00 31/07/2016 23:55
Automatic internal reference checks
occurring every night between 23:50 and
00:00
SO2 CK 8/08/16
01/07/2016 01:00 31/07/2016 01:40 Automatic calibration checks occurring
every night between 01:00 and 01:40 SO2 CK 8/08/16
01/07/2016 01:45 30/07/2016 02:15 Intermittent instrument stabilisation
following automatic calibration checks SO2 CK 8/08/16
01/07/2016 10:20 01/07/2016 10:40 Remote calibration SO2 CK 8/08/16
05/07/2016 01:55 06/07/2016 00:00 Offset +0.002ppm applied to data to correct
baseline SO2 CK 8/08/16
18/07/2016 01:55 18/07/2016 10:20 Offset +0.008ppm applied to data to correct
baseline SO2 CK 8/08/16
18/07/2016 10:25 18/07/2016 11:10 Power interruption and subsequent SO2
stabilisations following power interruptions
WS, WD,
SO2 CK 8/08/16
27/07/2016 08:55 27/07/2016 09:30 Power interruption and subsequent SO2
stabilisations following power interruptions
WS, WD,
SO2 CK 8/08/16
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7. Report Summary Data capture for SO2 at Devils Spring was 95% for SO2 and 100% capture for wind speed and wind
direction.
Data capture at Borroloola Caravan was 95% for SO2 and 100% for wind speed, wind direction,
ambient temperature, relative humidity, barometric pressure and rainfall. Percentage data
capture for solar radiation during July 2016 was 96%.
There were no recorded exceedances over the SO2 air quality goals for either station during July
2016.
------------------------------------------------END OF REPORT-------------------------------------
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Appendix 1 - Definitions & Abbreviations deg Degrees (True North)
m/s Metres per second
ppb Parts per billion
Sigma
Sigma Theta is the standard deviation of the horizontal wind direction fluctuations
over the averaging period.
SO2 Sulfur dioxide
WD Vector Wind Direction
WS Vector Wind Speed
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Appendix 2 - Explanation of Exception Table Automatic background check refers to when analyser samples zero air and measures the level of the
concentration voltage. This voltage is taken as the zero signal level and this value is subtracted from
any subsequent readings as an active zero compensation. This is the analyser’s fine zero
measurement.
Calibration check outside tolerance refers to when the calibration values are outside the tolerance
limits set for the precision check.
Calibration correction factor applied to data refers to an offset or multiplier applied to the data. This
operation may be performed for a number of reasons including: (a) when a clear trend / drift outside
the tolerance limit can be demonstrated by repeated operation precision checks, (b) when a
correction is required on previously logged data due to a calibration check being outside the allowable
tolerance
Commissioning refers to the initial setup and calibration of the instrument when it is first installed.
For some instruments there may be a stabilisation period before normal operation commences.
Data affected by environmental conditions – wind speed / wind speed gust spike refers to when a
one-off high reading occurs due to a natural occurrence such as a bird sitting on the wind sensor, or
some other event causing the readings to spike.
Data transmission error refers to a period of time when the instrument could not transmit data. This
may be due to interference, or a problem with the phone line or modem.
Equipment malfunction/instrument fault refers to a period of time when the instrument was not in
the normal operating mode and did not measure a representative value of the existing conditions.
Gap in data/data not available refers to a period of time when either data has been lost or could not
be collected.
Instrument Alarm refers to an alarm produced by the instrument. A range of alarms can be produced
depending on how operation of the instrument is being affected.
Instrument out of service refers to a lack of data due to an instrument being shut down for repair,
maintenance, or factory calibration.
Linear offset or multiplier refers to when an offset or multiplier has been applied between two points
where the values of the offset or multiplier are different and the correction is interpolated between
the two points.
Borroloola Caravan and Devils Spring Stations
Report No: DAT10991
McArthur River Mining
Page 31 of 31
Logger error refers to when an error occurs and instrument readings are not correctly recorded by
the logger.
Maintenance refers to a period of time when the logger / instrument was switched off due to
maintenance.
Overnight span/zero out of tolerance refers to when the span/zero reading measured by the analyser
during an automatic precision check falls outside of the expected concentration limits.
Overnight zero out of tolerance refers to when the automatic zero reading measured by the analyser
falls outside the expected limits.
Power Interruption refers to no power to the station therefore no data was collected at this time.
Remote Calibration refers to when a technician remotely connects to the station and manually
performs a span check.
Static offset or multiplier refers to when a single offset or multiplier has been applied to the data
between two points either to increase or decrease the measured value.
Warm up after power interruption refers to the startup period of an instrument after power has been
restored.