stack emissions monitoring report · arsenic mg/m³ 0.00040 0.00011 1 ... 1 yes bs en 15259 mean...
TRANSCRIPT
ESG Job Number:Report Date:Version: 1Report By: Hugh McmahonMCERTS Number: MM 15 1347MCERTS Level: MCERTS Level 2 - Team LeaderTechnical Endorsements: TE1, TE2 & TE4
Report Approved By: David HayMCERTS Number: MM 04 552Business Title: MCERTS Level 2 - Business ManagerTechnical Endorsements: 1, 2, 3 & 4
Signature:
2-4 Langlands PlaceKelvin South Business Park
East KilbrideG75 0YF
Tel: 01355 246 730Fax: 01355 249 669
Permit:IE Licence: P0401-01
Your contact at ESG
Clondalkin
Metal Processors Ltd
Dublin 22
Release Point: AE1 - Bag House Filter Exhaust
David HayBusiness Manager - North
Tel: 01355 246 730Email: [email protected]
Operator & Address:
Station Rd
Ireland
Sampling Date(s):22nd May 2017
10th July 2017LEK 10709
STACK EMISSIONS MONITORING REPORT
Report Template Version 26 Nov 16 Page 1 of 32
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EXECUTIVE SUMMARY
Stack Emissions Monitoring Objectives
- Plant
- Operator
- Stack Emissions Monitoring Test House
Emissions Summary
Monitoring Times
Process Details
Monitoring Methods
Analytical Methods
- Sampling Methods with Subsequent Analysis
- On-Site Testing
Sampling Location
- Sampling Plane Validation Criteria
- Duct Characteristics
- Sampling Lines & Sample Points
- Sampling Platform
- Sampling Location / Platform Improvement Recommendations
Sampling and Analytical Method Deviations
APPENDICES
APPENDIX 1 - Monitoring Schedule, Calibration Checklist & Monitoring Team
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
APPENDIX 3 - Measurement Uncertainty Budget Calculations
CONTENTS
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Plant
AE1 - Bag House Filter Exhaust
Operator
Metal Processors Ltd
Station Rd
Clondalkin
Dublin 22
Ireland
IE Licence: P0401-01
Stack Emissions Monitoring Test House
ESG - East Kilbride Laboratory2-4 Langlands PlaceKelvin South Business ParkEast KilbrideG75 0YFUKAS and MCERTS Accreditation Number: 1015
Opinions and interpretations expressed herein are outside the scope of UKAS accreditation.MCERTS accredited results will only be claimed where both the sampling and analytical stages are UKAS accredited.This test report shall not be reproduced, except in full, without written approval of ESG.
MONITORING OBJECTIVES
ESG were commissioned by Metal Processors Ltd to carry out stack emissions monitoring to determine the release of prescribed pollutants from thefollowing Plant under normal operating conditions.
Metal Processors Ltd operates a recycling of non ferrous waste process at Clondalkin which is subject to IE Licence P0401-01, under the EU (IndustrialEmissions) Regulations 2013.
EXECUTIVE SUMMARY
The results of these tests shall be used to demonstrate compliance with a set of emission limit values for prescribed pollutants as specified in the Plant's IE Licence, P0401-01.
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Parameter Units Result Calculated Uncertainty
Limit
+/-Total Particulate Matter mg/m³ 2.33 0.24 10Particulate Emission Rate g/hr 35.3 3.56 -Arsenic mg/m³ 0.00040 0.00011 1Arsenic Emission Rate g/hr 0.0058 0.0016 -Cadmium mg/m³ 0.00040 0.00078 0.5Cadmium Emission Rate g/hr 0.0057 0.0113 -Copper mg/m³ 0.0016 0.00043 5Copper Emission Rate g/hr 0.023 0.0063 -Nickel mg/m³ 0.0014 0.00038 5Nickel Emission Rate g/hr 0.020 0.0055 -Lead mg/m³ 0.0095 0.0026 2Lead Emission Rate g/hr 0.138 0.038 -Antimony mg/m³ 0.00031 0.00008 2Antimony Emission Rate g/hr 0.0044 0.0012 -Tin mg/m³ 0.00052 0.00014 5Tin Emission Rate g/hr 0.0075 0.0021 -Zinc mg/m³ 0.064 0.0178 5Zinc Emission Rate g/hr 0.932 0.257 -Moisture % 0.9 0.03 - P
Stack Gas Temperature oC 44 - -Stack Gas Velocity m/s 10.0 0.21 -Gas Volumetric Flow Rate (Actual) m³/hr 17721 886 -Gas Volumetric Flow Rate (STP, Wet) m³/hr 15065 753 -Gas Volumetric Flow Rate (STP, Dry) m³/hr 14926 746 -Gas Volumetric Flow Rate at Reference Conditions m³/hr 15065 753 -
P
P
P
P
P
P
MCERTS accredited
result
P
P
P
ND = None Detected,Results at or below the limit of detection are highlighted by bold italic text.The above volumetric flow rate is calculated using data from the preliminary survey. Mass emissions for non isokinetic tests are calculated using these values. For all isokinetic testing the mass emission is calculated using test specific flow data and not the above values.
EXECUTIVE SUMMARY
EMISSIONS SUMMARY
Reference conditions are 273K, 101.3kPa without correction for water vapour
P
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Total Particulate Matter Run 1Cadmium Run 1Heavy Metals Run 1 22 May 2017 10:10 - 11:23Preliminary Stack Traverse 22 May 2017 09:45 -
10:10 - 11:23 60 minutes60 minutes
22 May 2017 11:54 - 12:54
Sampling TimesSampling Date(s)Parameter
EXECUTIVE SUMMARY
Sampling DurationMONITORING TIMES
60 minutes22 May 2017
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Description of process Recycling of non Ferrous Waste
Continuous or batch Continuous
Product Details Lead Products
Part of batch to be monitored (if applicable) N/A
Normal load, throughput or continuous rating Normal Operation
Fuel used during monitoring N/A
Abatement Bag Filter with Lime Injection
Plume Appearance None
Parameter Process Details
EXECUTIVE SUMMARY
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Species ESG UKAS Lab MCERTS Limit of CalculatedTechnical Number Accredited Detection MUProcedure Method (LOD) +/- %
TPM AE 104 1015 Yes 0.11 mg/m³ 10.1%Cd AE 108 1015 Yes 0.00039 mg/m³ 197.2%
Heavy Metals AE 108 1015 Yes 0.002 mg/m³ 27.6%H2O AE 105 1015 Yes 0.01% 3.27%
Velocity AE 154 1015 Yes 5 Pa 2.1%Volumetric Flow
RateAE 154 1015 Yes - 5%
SRM - EN 13284-1
Method
SRM - EN ISO 16911-1
EXECUTIVE SUMMARY
SRM - EN ISO 16911-1
The selection of standard reference / alternative methods employed by ESG is determined, wherever possible by the hierarchy of method selectionoutlined in Environment Protection Agency Technical Guidance Note (Monitoring) AG2. i.e. CEN, ISO, US EPA etc.
SRM - EN 14385
Monitoring Methods
SRM - EN 14385
MONITORING METHODS
Standard Reference Method / Alternative Method
EN 14790 has been validated over a range of 4 - 40%. It is however the prefered method of the Environment Agency for concentrations below 4%
SRM - EN 14790
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The following tables list the analytical methods employed together with the custody and archiving details:
Species Analytical UKAS Lab Analysis Lab Sample ArchiveProcedure Number Archive Period
Location
TPM AE 106 1015 Yes ESG East Kilbride ESG East Kilbride 8 Weeks
Cd ASC/SOP/117 ESG - Bretby Yes ESG - Bretby ESG - Bretby 8 Weeks
Heavy Metals ASC/SOP/117 ESG - Bretby Yes ESG - Bretby ESG - Bretby 8 Weeks
Species Analytical UKAS Lab MCERTS Laboratory Data ArchiveProcedure Number Accredited Archive Period
Analysis LocationH2O AE 105 1015 Yes ESG East Kilbride - -
Inductively coupled Plasma - Mass Spectrometry
Analytical Technique
EXECUTIVE SUMMARY
Analytical Technique
Gravimetric
Analytical Methods
Inductively coupled Plasma - Mass Spectrometry
Gravimetric
SAMPLING METHODS WITH SUBSEQUENT ANALYSIS
ON-SITE TESTING
UKAS Accredited Lab Analysis
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Sampling Plane Validation Criteria Value Units Requirement Compliant Method
Lowest Differential Pressure 4 Pa >= 5 Pa No BS EN 15259
Lowest Gas Velocity 8.3 m/s - - -
Highest Gas Velocity 11.8 m/s - - -
Ratio of Gas Velocities 1.4 : 1 < 3 : 1 Yes BS EN 15259
Mean Velocity 10.0 m/s - - -
Maximum angle of flow with regard to duct axis <15 o < 15o Yes BS EN 15259
No local negative flow Yes - - Yes BS EN 15259
Value Units Isokinetic
Shape Circular -
Depth 0.79 m Sample port size 4" BSP -
Width - m Number of lines used 1 -
Area 0.49 m2 Number of points / line 4 -
Port Depth 90 mm Duct orientation Vertical -In Stack -
General Platform Information
Permanent / Temporary Platform / Ground level / Floor Level / Roof
Inside / Outside
AG1 Platform requirements
Is there a sufficient working area so work can be performed in a compliant manner
Platform has 2 levels of handrails (approximately 0.5 m & 1.0 m high)
Platform has vertical base boards (approximately 0.25 m high)
Platform has removable chains / self closing gates at the top of ladders
Handrail / obstructions do not hamper insertion of sampling equipmentDepth of Platform = >Stack depth / diameter + wall and port thickness + 1.5m
Sampling Platform Improvement Recommendations (if applicable)
SAMPLING PLATFORM
Non-Iso & Gases
Filtration for TPM
Yes
Yes
DUCT CHARACTERISTICS
EXECUTIVE SUMMARY
Permanent
Yes
Yes
A self closing gate or chain should be installed at the top of the ladder. Furthermore the platform should ideally be extended so that Line A is accessible.
SAMPLING LOCATION
Yes
No
Outside
SAMPLING LINES & POINTS
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Sample Points
Lowest Differential Pressure
Sampling & Analytical Method Deviations
The sampling point requirements of EN 13284-1 could not be met as It is only possible to access line B as there is no platform behind line A.As required in MID 13284-1 for such situations the number of sampling points has been doubled on the available line.
EXECUTIVE SUMMARY
The lowest differential pressure measured across the single sample line is slightly below the minimum 5Pa stated in the standard.
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APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
APPENDIX 3 - Measurement Uncertainty Budget Calculations
APPENDIX 1 - Monitoring Schedule, Calibration Checklist & Monitoring Team
CONTENTS
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Species ESG UKAS Lab MCERTSTechnical Number AccreditedProcedure Method
TPM AE 104 1015 Yes 1Cd AE 108 1015 Yes 1
Heavy Metals AE 108 1015 Yes 1H2O AE 105 1015 Yes 1
Velocity AE 154 1015 Yes 1
SRM - EN 13284-1
SRM - EN ISO 16911-1SRM - EN 14790 SRM - EN 14385
MONITORING SCHEDULE
APPENDIX 1 - Monitoring Schedule, Calibration Checklist & Monitoring Team
SRM - EN 14385
Standard Reference Method / Alternative Method
Number of Samples
Method
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Equipment I.D. Equipment I.D. Equipment I.D.
LEK 9.30 LEK LEK 15.21
LEK 9.31 LEK LEK 20.2
- LEK -
- - -
LEK 17.17 - LEK 16.5
- - LEK 1.11
LEK 6.29 - LEK 2.12
- - LEK 3.15
- - -
- - -
LEK 6.29 - -
- - -
LEK 23.17 LEK -
- LEK -
- - -
LEK 15-1G - -
- - -
- - LEK 8.18
LEK 24.7 - -
NOTE: If the equipment I.D is represented by a dash (-), then this piece of equipment has not been used for this test.
Level Expiry TE1 TE2 TE3 TE4 H&S
Hugh Mcmahon MM 15 1347MCERTS Level
2Sep-20 Feb-22 May-22 - Feb-22 Sep-20
Shane Thompstone
MM 16 1395MCERTS Trainee
Oct-21 N/A N/A N/A N/A Oct-21
Dioxins Cond. Thermocouple
CALIBRATEABLE EQUIPMENT CHECKLIST
Tape Measure
Equipment
10m Heated Line (2)
15m Heated Line (1)
Control Box DGM
10m Heated Line (1)
APPENDIX 1 - Monitoring Schedule, Calibration Checklist & Monitoring Team
Barometer
Miscellaneous
Equipment
20m Heated Line (1)
S-Pitot
Ecophysics NOx Analyser
Heater Controller
Last Impinger Arm
FT-IR Gasmet
Anemometer
Personnel
Box Thermocouples
Horiba PG-250 Analyser
Extractive Sampling
Equipment
Instrumental Analyser/s
Laboratory Balance
1m Heated Line (2)
Mass Flow Controller
Thermo FID
Digital Temperature Meter
Servomex
Probe Thermocouple
FT-IR Oven Box
1m Heated Line (3)
Callipers
20m Heated Line (2)
MFC Display module
Probe
Probe Thermocouple
Stackmaster
FTIR Heater Box for Heated Line
Meter Out Thermocouple
Control Box Timer
Stack Thermocouple
1m Heated Line (1)
L-Pitot
Oven Box
Probe JCT Heated Head Filter
Protractor
Digital Micromanometer
Heated Line Controller (2)
Meter In Thermocouple Stopwatch
Bernath 3006 FID
Signal 3030 FID
MCERTS Number
TE / H&S Qualifications and Expiry DateMCERTS
Site Balance
5m Heated Line (1)
Small DGM
Heated Line Controller (1)
0
Inclinometer (Swirl Device)
Chiller (JCT/MAK 10)
MONITORING TEAM
STACK EMISSIONS MONITORING TEAM
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Uncertainty Limit Emissionmg/m³ mg/m³ Rate g/hr
0.23 10 35
Blank - - -Reference conditions are 273K, 101.3kPa without correction for water vapour
TestFilter & Probe Rinse Number
Filter Start Weight
Filter End Weight
Mass Gained on Filter
Probe Rinse Start Weight
Probe Rinse End Weight
Mass Gained on Probe
Combined Total Mass Gained
g g g g g g gRun 1 AC7988 0.09561 0.09722 0.00161 156.14150 156.14360 0.00210 0.00371If total mass gained is less than the LOD then the LOD is reported
TestFilter & Probe
NumberFilter Start
WeightFilter End
WeightMass Gained
FilterProbe Start
WeightProbe End
WeightMass Gained
ProbeCombined Total
Mass Gained
g g g g g g gRun 1 AC8002 0.09518 0.09523 0.00005 202.72750 202.72780 0.00030 0.00035If total mass gained is less than the LOD then the LOD is reported
Concentration
-
Acetone Blank Value
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Run 1
0.22
Sampling Times
mg/l
BLANKS
SAMPLES
11:54 - 12:5422 May 2017
2.33
TOTAL PARTICULATE MATTER SUMMARYParameter
mg/m³
Acceptable Value
2.0 10mg/l
FILTER INFORMATION
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ISOKINETIC SAMPLING EQUATIONS - RUN 1 TPM
Absolute pressure of stack gas, Ps Molecular weight of dry gas, Md
Barometric pressure, Pb mm Hg 769.51 CO2 % 0.03Stack static pressure, Pstatic mm H2O -275.32 O2 % 20.95Ps = Pb + (Pstatic) mm Hg 749.26 Total % 20.98
N2 (100 -Total) % 79.02Vol. of water vapour collected, Vwstd Md = 0.44(%CO2)+0.32(%O2)+0.28(%N2) 28.84
g 11.8 Molecular weight of wet gas, Ms
Vwstd = (0.001246)(Vlc) m3 0.0147028 Ms = Md(1 - Bwo) + 18(Bwo) g/gmol 28.74Volume of gas metered dry, Vmstd Actual flow of stack gas, Qa
Volume of gas sample through gas meter, Vm m3 1.686 Area of stack, As m2 0.49
Gas meter correction factor, Yd 0.9910 Qa = (60)(As)(Vs) m³/min 306.4Mean dry gas meter temperature, Tm
oC 22.208 Total flow of stack gas, Q73.589 Conversion factor (K/mm.Hg) 0.3592
Vmstd = (0.3592)(Vm)(Pb+(DH/13.6))(Yd) m3 1.575 Qstd = (Qa)Ps(0.3592)(1-Bwo) Dry 249.4 (Ts) +273
Volume of gas metered wet, Vmstw @O2ref No O2 RefVmstw = Vmstd + Vwstd m3 1.5897 (Ts) +273
Qstw = (Qa)Ps(0.3592) Wet 251.76 (Ts) +273
No Percent isokinetic, %INozzle diameter, Dn mm 8.00
% oxygen measured in gas stream, act%O2 21.0 Nozzle area, An mm2 50.27% oxygen reference condition 21 Total sampling time, q min 60
No O2 Ref %I = (4.6398E6)(Ts+273)(Vmstd) % 102.6 (Ps)(Vs)(An)(q)(1-Bwo)
Vmstd@X%oxygen = (Vmstd) (O2 Ref) m3 No O2 Ref Acceptable isokinetic range 95% to 115% YesMoisture content, Bwo Particulate Concentration, CBwo = Vwstd 0.0092 Mass collected on filter, Mf g 0.00161
% 0.92 Mass collected in probe, Mp g 0.00210Moisture by FTIR % - Total mass collected, Mn g 0.00371Velocity of stack gas, Vs Cwet = Mn mg/m³ 2.334Pitot tube velocity constant, Kp 34.97 Vmstw
Velocity pressure coefficient, Cp 0.843 Cdry = Mn mg/m³ 2.355Mean of velocity heads, DPavg mm H2O 8.21 Vmstd
Mean square root of velocity heads, ÖDP 2.87 Cdry@X%O2 = Mn mg/m³ No O2 RefMean stack gas temperature, Ts
oC 55Vs = (Kp)(Cp)(ÖDP)(Ö(Ts + 273)) m/s 10.42 Particulate Emission Rates, E (Ms)(Ps) E = [(Cwet)(Qstw)(60)] / 1000 35.25
Vmstd@X%oxygen
Is the process burning hazardous waste? (If yes, no favourable oxygen correction)
O2 Reference Factor
QstdO2 = (Qa)Ps(0.3592)(1-Bwo)(O2REF)
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
O2 Ref = 21.0 - act%O2
21.0 - ref%O2
Moisture trap weight increase,Vlc
13.6
Tm + 273
Vol. of gas metered at O2 Ref. Cond., Vmstd@X%O2
Vmstd + Vwstd
Mean pressure drop across orifice, DH mmH2O
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litre/min litre/min litre/min mm Hg litre/minRun 1 27.84 0.02 0.02 -254 0.56 Yes
% mg/m³ mg/m³Run 1 102.62 Yes Run 1 0.11 0.5 Yes
Acceptable isokinetic range 95% to 115% The above is based on both the Filter and rinse uncertainty
mg/m3 mg/m3 mg/m3 mg/m3
mm °CRun 1 Glass Fibre 47 55
BLANK VALUE
Pre-sampling Leak Rate
Acceptable Leak Rate
Overall Blank Value
Filter SizeFilter Material
WEIGHING BALANCE UNCERTAINTYISOKINETICITY
Acceptable Blank Value
160
Daily Emission Limit Value
Overall Blank Acceptable
Isokinetic Variation
LOD < 5% ELVRun
Result
FILTERS
°C
Run
Mean Sampling Rate
Maximum Vacuum
Run
180
Acceptable Isokineticity
°C
TOTAL PARTICULATE MATTER QUALITY ASSURANCE CHECKLIST
LEAK RATELeak Tests
Acceptable?
Run
1.0
Max Filtration Temperature
10 Yes
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
5% ELV
Blank 1
Pre-use Filter Conditioning Temperature
0.22
Post-sampling Leak RateRun
Post-use Filter Conditioning Temperature
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LOD Limit Emissionmg/m³ mg/m³ Rate g/hr
0.0004 0.50 0.0057
- - -
LOD Limit Emissionmg/m³ mg/m³ Rate g/hr
0.0023 - 1.130
- - -Reference conditions are 273K, 101.3kPa without correction for water vapour
Metals LOD Concentration Emission UKASmg/m³ mg/m³ Rate g/hr Accredited
0.00039 0.00040 0.00574 147% P
LOD Concentration Emission UKASmg/m³ mg/m³ Rate g/hr Accredited
0.00026 0.00040 0.006 109% P
0.00026 0.00031 0.004 197% P
0.00033 0.00157 0.023 51% P
0.00033 0.00953 0.138 20% P
0.00034 0.00137 0.020 51% P
0.00020 0.00052 0.008 100% P
0.00059 0.06437 0.932 18% P
Total Other Heavy Metals 0.00230 0.07806 1.130 27.6% -Reference conditions are 273K, 101.3kPa without correction for water vapour
Uncertainty (%)
Arsenic
Field Blank
10:10 - 11:23 22 May 2017
Test
Concentration
Sampling Times
CADMIUM
TOTAL HEAVY METALS COMBINED
Testmg/m³
Nickel
0.0003
mg/m³
Sampling Times
-
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Antimony
Concentration
Metals
INDIVIDUAL METALS SUMMARY - SOLID & VAPOUR PHASES COMBINED
0.0031-
Cadmium
Uncertainty (%)
Zinc
Copper
Field Blank
Run 1
Tin
10:10 - 11:23 22 May 2017
Run 1 0.0004
HEAVY METALS SOLID & VAPOUR PHASES COMBINED
Lead
0.0781
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MetalsStack LOD Concentration Stack LOD Concentration
mg/m³ mg/m³ug mg/m³ ug mg/m³
0.0004 0.60 0.0004 0.00001 0.02 0.00001Volume Sampled m3
Reference conditions are 273K, 101.3kPa without correction for water vapour
Stack LOD Concentration Stack LOD Concentrationmg/m³ mg/m³
ug mg/m³ ug mg/m³0.00026 0.40000 0.00026 0.00001 0.22656 0.000140.00026 0.40000 0.00026 0.00001 0.08020 0.000050.00032 2.00000 0.00128 0.00001 0.45932 0.000290.00032 9.00000 0.00575 0.00001 5.92300 0.003780.00032 2.00000 0.00128 0.00002 0.14076 0.000090.00019 0.60000 0.00038 0.00001 0.21437 0.000140.00032 100.00000 0.06384 0.00027 0.83560 0.00053
Total Other Heavy Metals 0.00198 114.40000 0.07303 0.00032 7.87981 0.00503Volume Sampled m3
Reference conditions are 273K, 101.3kPa without correction for water vapour
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Arsenic
PARTICULATE PHASE
HEAVY METALS - RUN 1 SUMMARY
VAPOUR PHASE
Laboratory Result
Cadmium
Metals
PARTICULATE PHASE
1.56641.5664
VAPOUR PHASE
Copper
Zinc
Lead
Laboratory Result
Tin
1.5664
Antimony
1.5664
Laboratory Result
Laboratory Result
Nickel
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MetalsStack LOD Concentration Stack LOD Concentration
mg/m³ mg/m³ug mg/m³ ug mg/m³
0.00038 0.5 0.00032 0.00001 0.02050 0.00001Volume Sampled m3
Reference conditions are 273K, 101.3kPa without correction for water vapour
Stack LOD Concentration Stack LOD Concentrationmg/m³ mg/m³
ug mg/m³ ug mg/m³0.00026 0.40000 0.00026 0.00001 0.02050 0.000010.00026 0.40000 0.00026 0.00001 0.02050 0.000010.00032 0.50000 0.00032 0.00001 0.47150 0.000300.00032 0.50000 0.00032 0.00001 0.22550 0.000140.00032 0.50000 0.00032 0.00002 0.16400 0.000100.00019 0.30000 0.00019 0.00001 0.02050 0.000010.00032 0.50000 0.00032 0.00027 0.82000 0.00052
Total Other Heavy Metals 0.00198 3.10000 0.00198 0.00032 1.74250 0.00111Volume Sampled m3
Reference conditions are 273K, 101.3kPa without correction for water vapour
HEAVY METALS - BLANK SUMMARY
Nickel
1.5664
Arsenic
Lead
1.5664Cadmium
VAPOUR PHASE
VAPOUR PHASE
Antimony
1.5664
Zinc
Copper
Metals
1.5664
Laboratory Result
Laboratory Result
Tin
Laboratory Result
PARTICULATE PHASE
Laboratory Result
PARTICULATE PHASE
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
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ISOKINETIC SAMPLING EQUATIONS RUN 1 Cd, Tl & Heavy Metals
Absolute pressure of stack gas, Ps Molecular weight of dry gas, Md
Barometric pressure, Pb mm Hg 770.3 CO2 % 0.03Stack static pressure, Pstatic mm H2O -410.1 O2 % 20.95Ps = Pb + (Pstatic) mm Hg Total % 20.98
740.1 N2 (100 -Total) % 79.02Md = 0.44(%CO2)+0.32(%O2)+0.28(%N2) 28.84
Vol. of water vapour collected, Vwstd Molecular weight of wet gas, Ms
g - Ms = Md(1 - Bwo) + 18(Bwo) g/gmol 28.74Vwstd = (0.001246)(Vlc) m3 - Velocity of stack gas, Vs
Volume of gas metered dry, Vmstd Pitot tube velocity constant, Kp 34.97Velocity pressure coefficient, Cp 0.843
Volume of gas sample through gas meter, Vm m3 1.6467 Mean of velocity heads, DPavg mm H2O 7.58
Gas meter correction factor, Yd 0.9910 Mean square root of velocity heads, ÖDP 2.75Mean dry gas meter temperature, Tm
oC 19.79 Mean stack gas temperature, TsoC 53
Mean pressure drop across orifice, DH mmH2O 66.89 Vs = (Kp)(Cp)(ÖDP)(Ö(Ts + 273)) m/s 10.04 (Ms)(Ps)
Vmstd = (0.3592)(Vm)(Pb+(DH/13.6))(Yd) m3 1.55 Actual flow of stack gas, Qa
Area of stack, As m2 0.49Volume of gas metered wet, Vmstw Qa = (60)(As)(Vs) m³/min 295.4
Total flow of stack gas, QVmstw = Vmstd + Vwstd m3 1.5664 Conversion factor (K/mm.Hg) 0.3592
Qstd = (Qa)Ps(0.3592)(1-Bwo) Dry 238.9 (Ts) +273
No @O2ref No O2 Ref (Ts) +273
% oxygen measured in gas stream, act%O2 21.0 Qstw = (Qa)Ps(0.3592) Wet 241.2% oxygen reference condition 21 (Ts) +273
O2 Ref = 21.0 - act%O2 No O2 Ref Percent isokinetic, %I 21.0 - ref%O2 Nozzle diameter, Dn mm 8.00
Vmstd@X%oxygen = (Vmstd) (O2 Ref) m3 No O2 Ref Nozzle area, An mm2 50.27Moisture content, Bwo Total sampling time, q min 60
%I = (4.6398E6)(Ts+273)(Vmstd) % 105.6Bwo = Vwstd 0.0092 (Ps)(Vs)(An)(q)(1-Bwo)
% 0.92Moisture by FTIR % - Acceptable isokinetic range 95% to 115% Yes
Moisture trap weight increase,Vlc
QstdO2 = (Qa)Ps(0.3592)(1-Bwo)(O2REF)
Tm + 273
Vmstd + Vwstd
Vol. of gas metered at O2 Ref. Cond., Vmstd@X%O2
O2 Reference Factor
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
13.6
Is the process burning hazardous waste? (If yes, no favourable oxygen correction)
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Leak Tests AcceptableAcceptable
litre/min litre/min litre/min mm Hg litre/min litre/min27.2 0.04 0.04 -330.2 0.54 Yes
Isokinetic Criterion Compliance
mm °C °CQuartz Fibre 47 180 20
Filter Size
Type of Absorbers - Metals
Run 1
Glass
Leak Test Results
HEAVY METALS QA CHECKLIST
Pre-sampling Leak Rate
Maximum Vacuum
Mean Sampling Rate
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Acceptable Leak Rate
Run 1
105.6
Run 1
Metals
Isokinetic Variation Acceptable Isokineticity
Post-sampling Leak Rate
Filter Material
%
Filtration / Temp
Run 1 Yes
Maximum storage / transit
Temperature
Maximum Filtration
Temperature
3.3% Nitric Acid, 1.5% Hydrogen Peroxide
Absorption Solutions - Metals
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Parameter Total 3rd Absorber Absorption Required Pass / Failug ug Efficiency (%) %
Cadmium Run 1 0.62089 ND 100 90 N/A <30% ELVArsenic Run 1 0.62656 0.03 96 90 N/A <30% ELVAntimony Run 1 0.48020 0.07 86 90 N/A <30% ELVCopper Run 1 2.45932 0.32 87 90 N/A <30% ELVLead Run 1 14.92300 4.68 69 90 N/A <30% ELVNickel Run 1 2.14076 0.03 99 90 N/A <30% ELVTin Run 1 0.81437 0.09 89 90 N/A <30% ELVZinc Run 1 100.83560 ND 100 90 N/A <30% ELV
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
HEAVY METALS ABSORBTION EFFICIENCY
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Test Number Start Weight End Weight Total gain Concentration LOD Uncertainty
kg kg kg % % %
Run 1 3.6031 3.6149 0.0118 0.9 0.008 3.3
Test NumberSampling Duration
Total Volume Sampled
Sampling Rate Start Leak Rate End Leak RateAcceptable Leak Rate
mins l l/min l/min l/min l/min
Run 1 60 1590 27.8 0.02 0.02 0.56 Yes
Stack Diameter / Depth, D 0.79 m
Stack Width, W - m
Stack Area, A 0.49 m2
Average stack gas temperature 44 oC
Stack static pressure -2.7 kPa
Barometric Pressure 102.7 kPa
Component Molar Density Conc Dry Volume Dry Conc Conc Wet Volume Wet ConcMass kg/m3 Dry Fraction kg/m3 Wet Fraction kg/m3
M p % Vol r pi % Vol r pi
CO2 44 1.963059 0.030000 0.000300 0.000589 0.029723 0.000297 0.000583
O2 32 1.427679 20.950000 0.209500 0.299099 20.756243 0.207562 0.296333
N2 28 1.249219 79.020000 0.790200 0.987133 78.289181 0.782892 0.978004
H2O 18 0.803070 - - - 0.924853 0.009249 0.007427
Where: p = M / 22.41 pi = r x p
Determinand
Dry Density (STP), P STD
Wet Density (STP), P STW
Dry Density (Actual), P Actual
Average Wet Density (Actual), P ActualW
Where:
P STD = sum of component concentrations, kg/m3 (not including water vapour) P Actual = P STD x (Ts / Ps) x (Pa / Ta)
P STW = (P STD + pi of H2O) / (1 + (pi of H2O / 0.8036)) P ActualW = P STW x (Ts / Ps) x (Pa / Ta)
Result
kg/m3
Moisture Quality Assurance
11:54 - 12:5422 May 2017
Stack Gas Composition & Molecular Weights
Moisture Determination - Isokinetic
MOISTURE CALCULATIONS
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
1.2823
kg/m31.2868
kg/m3
1.0940
Sampling Time and Date
PRELIMINARY STACK SURVEY
Leak Tests Acceptable?
1.090
kg/m3
Units
Calculation of Stack Gas Densities
Stack Characteristics
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TRAVERSE 1
Traverse Distance DP pt DP pt Temp Velocity O2 Angle
Point into mmH2O Pa oC m/s % of Swirl
duct (m)(average of 3
readings)(average of 3
readings)m³/s Vol o
- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -
Mean - - - - - - - -
Traverse Distance DP pt DP pt Temp Velocity O2 Angle
Point into mmH2O Pa oC m/s % of Swirl
duct (m)(average of 3
readings)(average of 3
readings)m³/s Vol o
1 0.02 5.0 49 44 9.3 4.6 - <152 0.06 6.0 59 44 10.2 5.0 - <153 0.12 7.0 69 44 11.0 5.4 - <154 0.18 6.0 59 44 10.2 5.0 - <155 0.27 6.0 59 44 10.2 5.0 - <156 0.52 8.0 78 44 11.8 5.8 - <157 0.61 6.0 59 44 10.2 5.0 - <158 0.67 7.0 69 44 11.0 5.4 - <159 0.73 4.0 39 44 8.3 4.1 - <15
10 0.77 4.0 39 44 8.3 4.1 - <15Mean - 5.9 58 44 10.0 4.9 - -
Start Value End Value Difference Start Value End Value DifferencePa Pa % Pa Pa %
Run 1 131 130 0.8 Pass 144 144 0.0 Pass
Time of Survey
PRELIMINARY STACK SURVEY QUALITY ASSURANCE CHECKLIST
Velocity Measurement Device: L-Type Pitot
Volumetric Flow Rate
(actual)
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Post Traverse Leak Rate
Sampling Line A
Date of Survey
Volumetric Flow Rate
(actual)
To complete a compliant pitot leak check a pressure of over 80 mmH₂O (or 800 Pa) is applied and the pressure drop monitored over 5 mins. A drop of less than 5% must be observed.
Run Outcome
PRELIMINARY STACK SURVEY
Sampling Line B
09:4522 May 2017
Outcome
PITOT LEAK CHECKPre Traverse Leak Rate
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EA Technical Guidance Note (Monitoring) M1 Units Requirement Compliant
Lowest Differential Pressure Pa >= 5 Pa Yes
Lowest Gas Velocity m/s - -
Highest Gas Velocity m/s - -
Ratio of Gas Velocities - < 3 : 1 Yes
Maximum angle of flow with regard to duct axis o < 15o Yes
No local negative flow - - Yes
Velocity at Traverse Point, V = Kpt x (1-e) * Ö(2 * DP pt / P ActualW)
Where:Kpt = Pitot tube calibration coefficient(1-e) = Compressibility correction factor, assumed at a constant 0.998
Average Stack Gas Velocity, Va 10.0 m/s
Duct gas flow conditions Actual Reference UnitsTemperature 44 0 oCTotal Pressure 100 101.3 kPaOxygen 21.0 21 %Moisture 0.92 0.92 %Pitot tube calibration coefficient, Kpt 0.98
Gas Volumetric Flowrate UnitsAverage Stack Gas Velocity (Va) m/sStack Area (A) m2
Gas Volumetric Flowrate (Actual), QActual m3/hr
Gas Volumetric Flowrate (STP, Wet), QSTP m3/hr
Gas Volumetric Flowrate (STP, Dry), QSTP,Dry m3/hr
Gas Volumetric Flowrate (REF), QRef m3/hr
Where:QActual = Va x A x 3600QSTP = Q (Actual) x (Ts / Ta) x (Pa / Ps) x 3600QSTP,Dry = Q (STP) / (100 - (100 / Ma)) x 3600QRef = Q (STP) x ((100 - Ma) / (100 - Ms)) x ((20.9 - O2a) / (20.9 - O2s))
Nomenclature:Ts = Absolute Temperature, Standard Conditions, 273 KPs = Absolute Pressure, Standard Conditions, 101.3 kPaTa = Absolute Temperature, Actual Conditions, KPa = Absolute Pressure, Actual Conditions, kPaMa = Water vapour, Actual Conditions, % VolMs = Water vapour, Reference Conditions, % VolO2a = Oxygen, Actual Conditions, % VolO2s = Oxygen, Reference Conditions, % Vol
8.3
1.4
PRELIMINARY STACK SURVEY (CONTINUED)
15065
15065
Calculation of Stack Gas Velocity, V
10.040.49
Result
Result
Calculation of Stack Gas Volumetric Flowrate, Q
17721
14926
Yes
11.8
39
<15
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Sampling Plane Validation Criteria
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Value UnitsStack Depth 0.79 m Sampling Distance Distance into UnitsStack Width - m Point (% of Depth) StackArea 0.49 m2 - - - -
Sampling Distance Distance into SwirlPoint (% of Depth) Stack (m) o
1 6.7 0.05 < 152 25.0 0.20 < 153 75.0 0.59 < 154 93.3 0.74 < 15
- - - -
- - - -
- - - -
- - - -- - - -- - - -- - - -- - - -
- - - -
- - - -- - - -- - - -
Isokinetic sampling point - - - -Isokinetic sampling points not used - - - -Non Isokinetic/Gases sampling point - - - -
- - - -
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Isokinetic Sampling
Non-Isokinetic/Gases Sampling
SAMPLING LOCATION
STACK DIAGRAM
Sampling Line
1
2
3
4
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Run Sampled Volume
Sampled Gas Temp
Sampled Gas Pressure
Sampled Gas Humidity
Oxygen Content
Limit of Detection
Leak Uncollected Mass
m³ K kPa % by volume % by volume % by mass % mgMU required < 2% < 2% < 1% < 1% < 10% < 5% of ELV < 2% < 10% of ELVRun 1 0.001 2.0 0.50 1.0 N/A 0.1800 - -as a % 0.06 0.68 0.50 1.0 N/A 1.1323 0.07 0.004compliant? Yes Yes Yes Yes N/A Yes Yes Yes
Run UncollectedMass
m³ mg - mg/m³ mgRun 1 1.45 3.7100 1.0 0.001 0.0002 -MU as mg/m3 0.03 0.1132 - 0.001 0.0001 0.12MU as % 1.31 4.8518 - 0.041 0.0054 -
0.23 mg/m³ 10.05 %(k is a coverage factor which gives a 95% confidence in the quoted figures)Developed for the STA by R Robinson, NPL
R1 - Uncertainty expressed at a 95% confidence level (where k = 2)
Leak Combined uncertainty
Volume (STP)
MEASUREMENT UNCERTAINTY BUDGET - TOTAL PARTICULATE MATTER
Mass of particulate
O2 Correction
APPENDIX 3 - Measurement Uncertainty Budget Calculations
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Run Sampled Volume
Sampled Gas Temp
Sampled Gas Pressure
Sampled Gas Humidity
Oxygen Content
Concentration in impinger
Leak
m³ K kPa % by volume % by volume mg %MU required <=2% <2.5 k <=1% <=1% <=5% <5% <=2%Run 1 0.001 2.0 0.50 1.0 0.1 0.000003 -as a % 0.06 0.7 0.80 1.0 - 3.00 0.15compliant? Yes Yes Yes Yes N/A Yes Yes
Run LabUncertainty
m³ - mg mg/m³ mgRun 1 0.9008 - 0.6209 0.000000 - -MU as mg 0.00001 - 0.0004 0.000000 0.00003 0.0004MU as % 1.4558 - 98.3177 0.0849 7.50000 -
0.001 mg/m³ 197.23 %
(k is a coverage factor which gives a 95% confidence in the quoted figures)Developed for the STA by R Robinson, NPL
Mass of Cadmium &
Thallium
Leak
R1 - Uncertainty expressed at a 95% confidence level (where k = 2)
MEASUREMENT UNCERTAINTY BUDGET - CADMIUM
APPENDIX 3 - Measurement Uncertainty Budget Calculations
O2 Correction Combined uncertainty
Volume (STP)
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Run Sampled Volume
Sampled Gas Temp
Sampled Gas Pressure
Sampled Gas Humidity
Oxygen Content
Concentration in impinger
Leak
m³ K kPa % by volume % by volume mg %MU required <=2% <2.5 k <=1% <=1% <=5% <5% <=2%Run 1 0.001 2.0 0.50 1.0 0.10 0.0011 -as a % 0.06 0.73 0.80 1.0 - 3.00 0.15compliant? Yes Yes Yes Yes N/A Yes Yes
Run LabUncertainty
m³ - mg mg/m³ mgRun 1 0.9661 - 20.6298 0.0001 - -MU as mg/m3
0.0012 - 0.0090 0.0001 0.00585 0.0108MU as % 1.4791 - 11.5033 0.0849 7.50000 -
0.02 mg/m³ 27.62 %
(k is a coverage factor which gives a 95% confidence in the quoted figures)Developed for the STA by R Robinson, NPL
Volume (STP)
R1 - Uncertainty expressed at a 95% confidence level (where k = 2)
O2 Correction Leak Combined uncertainty
APPENDIX 3 - Measurement Uncertainty Budget Calculations
Mass of Heavy Metals
MEASUREMENT UNCERTAINTY BUDGET - HEAVY METALS
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Run Sampled Volume
Sampled Gas Temp
Sampled Gas Pressure
Sampled Gas Humidity
Oxygen Content
Leak
m³ K kPa % by volume % by volume %MU required < 2% < 2% < 1% < 1% < 10% < 2%Run 1 0.001 2.0 0.50 1.0 N/A -as a % 0.06 0.68 0.50 1.0 N/A 0.07compliant? Yes Yes Yes Yes N/A Yes
Run UncollectedMass
m³ mg - mg/m³ mgRun 1 1.45 11800 1.0 3.08 57.7 -MU as % v/v 0.01 0.01 - 0.0004 0.005 0.02MU as % 1.31 0.85 - 0.04 0.49 -
0.03 % v/v 3.27 %
(k is a coverage factor which gives a 95% confidence in the quoted figures)Developed for the STA by R Robinson, NPL
MEASUREMENT UNCERTAINTY BUDGET - MOISTURE
Combined uncertainty
Leak
R1 - Uncertainty expressed at a 95% confidence level (where k = 2)
APPENDIX 3 - Measurement Uncertainty Budget Calculations
O2 CorrectionMass GainedVolume (STP)
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10.0 m/s17721 m³/hr
Performance Characteristics & Source of Value Units Values Requirement CompliantUncertainty of Local Gas Velocity Determination
Uncertainty of pitot tube coefficient - 0.010
Uncertainty of mean local dynamic pressures - 0.35
Factor loading, function of the number of measurements. 3 readings 0.591 minimum 3 Yes
Range of measurment device pa 1000
Resolution pa 1.00
Calibration uncertainty pa 2.81<1% of Value or 20
Pa whichever is greater
Yes
Drift % range 0.10
Linearity % range 0.06 <2% of value Yes
Uncertainty of gas density determination
Uncertainty of molar mass determination kg/mol 0.00003Uncertainty of temperature measurement K 1.62 <1% of value Yes
Uncertainty of absolute pressure in the duct pa 510
Uncertainty associated with the estimate of density - 0.007
Uncertainty associated with the measurement of local velocity - 0.0001Uncertainty associated with the measurement of mean velocity - 0.0001
m/s0.110.21
%1.12.1
m³/hr452886
%2.55.0
Expanded Measurement Uncertainty of Velocity at a 95% Confidence IntervalExpressed as a % of the Measured ConcentrationExpanded uncertainty at a 95% Confidence Interval
Measurement Uncertainty Volumetric Flow RateCombined uncertainty
Note - The expanded uncertainty uses a coverage factor of k = 2.
Expanded uncertainty at a 95% Confidence Interval
Expanded Measurement Uncertainty of Volumetric Flow Rate at a 95% Confidence IntervalExpressed as a % of the Measured ConcentrationExpanded uncertainty at a 95% Confidence Interval
Measured Velocity at Actual Conditions Measured Volumetric Flow rate at Actual Conditions
Measurement Uncertainty - VelocityCombined uncertaintyExpanded uncertainty at a 95% Confidence Interval
Note - The expanded uncertainty uses a coverage factor of k = 2.
APPENDIX 3 - Measurement Uncertainty Budget Calculations
MEASUREMENT UNCERTAINTY BUDGET - VELOCITY & VOLUMETRIC FLOW RATE
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