stack emissions monitoring reportsocotec uk ltd species socotec ukas lab mcerts limit of calculated...
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SOCOTEC Job Number:Report Date:Version: 1Report By: Cameron RussellMCERTS Number: MM 18 1481MCERTS Level: MCERTS Level 1 Technical Endorsements: TE1,TE3
Report Approved By: Enda FloodMCERTS Number: MM 12 1170 Business Title: MCERTS Level 2 - Team LeaderTechnical Endorsements: 1, 2, 3 & 4
Signature:
Sampling Date(s):18-20/Feb/2020
23-Mar-20LEK 12100 / Q1
Release Point: A2-15
Your contact at SOCOTEC LTD
Ireland
Clonmel
Medite Europe Ltd
Co. Tipperary
Operator & Address:
Redmonstown
2-4 Langlands PlaceKelvin South Business Park
East KilbrideG75 0YF
Tel: 01355 246 730Fax: 01355 249 669
Permit Reference:IE Licence: P0027-04
David HayBusiness Manager - North
Tel: 01355 246 730Email: [email protected]
STACK EMISSIONS MONITORING REPORT
SOCOTEC UK Reporting Template v5 Page 1 of 39
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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
A2-15
Operator
Medite Europe Ltd
Redmonstown
Clonmel
Co. Tipperary
Ireland
IE Licence: P0027-04
Stack Emissions Monitoring Test House
SOCOTEC - 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 SOCOTEC LTD.
MONITORING OBJECTIVES
SOCOTEC LTD were commissioned by Medite Europe Ltd to carry out stack emissions monitoring to determine the release of prescribed pollutantsfrom the following Plant under normal operating conditions.
Medite Europe Ltd operates a wood fibre board manufacturing process at Clonmel which is subject to IE Licence P0027-04, under the EPA Act 1992.
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 thePlant's IE Licence, P0027-04.
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Parameter Units Result Calculated Uncertainty
+/-Total Particulate Matter mg/m³ 3.9 0.50 15Particulate Emission Rate g/hr 174 22.3 -Isocyanates mg/m³ 0.0001 0.0001 0.06Isocyanates Emission Rate g/hr 0.0045 0.004 -Formaldehydes mg/m³ 6.92 0.650 10Formaldehydes Emission Rate g/hr 285.38 26.826 -Total Volatile Organic Compounds mg/m³ 5.15 1.33 20Total Volatile Organic Compounds Emission Rate g/hr 201.96 52.31 -Oxides of Nitrogen (as NO2) mg/m³ 0.8 4.14 100Oxides of Nitrogen (as NO2) Emission Rate g/hr 31 162.6 -Carbon Monoxide mg/m³ 1.47 2.67 100Carbon Monoxide Emission Rate g/hr 57.61 104.67 -Oxygen % v/v 20.9 0.909 - P
Moisture % 2.77 0.09 - P
Stack Gas Temperature oC 55 - -Stack Gas Velocity m/s 11.9 0.29 -Gas Volumetric Flow Rate (Actual) m³/hr 48472 2497 -Gas Volumetric Flow Rate (STP, Wet) m³/hr 40370 2080 -Gas Volumetric Flow Rate (STP, Dry) m³/hr 39252 2022 -Gas Volumetric Flow Rate at Reference Conditions m³/hr 39252 2022 43200
Emission Limit Value (ELV)
P
P
Reference conditions are 273K, 101.3kPa, dry gas .
P
P
P
EXECUTIVE SUMMARY
EMISSIONS SUMMARY
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.
P
MCERTS accredited
result
P
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Total Particulate Matter Run 1Isocyanates Run 1Formaldehydes Run 1Total Volatile Organic Compounds Run 1Combustion Gases 60 minutes
13:32 - 14:32
MONITORING TIMES
60 minutes19 February 2020 12:05 - 13:05
Sampling TimesSampling Date(s)Parameter
EXECUTIVE SUMMARY
Sampling Duration
19 February 202019 February 2020 60 minutes
12:05 - 13:05 60 minutes
09:56-10:10
60 minutes
-10:45 - 11:45
19 February 202019 February 2020
10:45 - 11:45
Preliminary Stack Traverse
19 February 2020
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Description of process Wood Fibre Board Manufacturing
Continuous or batch Continuous
Product Details Wood Fibre Board
Part of batch to be monitored (if applicable) Normal Operation
Normal load, throughput or continuous rating Normal Load
Fuel used during monitoring N/A
Abatement N/A
Plume Appearance Slight Moisture plume Visible
Process Details
EXECUTIVE SUMMARY
PROCESS DETAILS
Parameter
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Species SOCOTEC UKAS Lab MCERTS Limit of Calculated CalculatedTechnical Number Accredited Detection MU MUProcedure Method (LOD) +/- % Result +/- % ELV
Total Particulate Matter
AE 104 1015 Yes 0.24 mg/m³ 12.8% 3.4%
Isocyanates AE 116 1015 Yes 0.0001 mg/m³ 89.7% 0.2%
Formaldehydes AE 114 1015 Yes 0.02 mg/m³ 9.4% 6.51%
Total Volatile Organic Compounds AE 102 1015 Yes 0.66 mg/m³ 25.9% 6.7%
Oxides of Nitrogen
AE 102 1015 Yes 0.51 mg/m³ 527.6% 4.1%
Carbon Monoxide AE 102 1015 Yes 0.28 mg/m³ 181.7% 2.7%
Oxygen AE 102 1015 Yes 0.01% 4.4% N/A - No ELV
Moisture AE 105 1015 Yes 0.02% 3.42% N/A - No ELV
Velocity AE 154 1015 Yes 5 Pa 2.5% N/A - No ELV
Volumetric Flow Rate
AE 154 1015 Yes - 5.2% 468.13%
MONITORING METHODS
SRM - EN ISO 16911-1
Method
AM - EN 14789:2017
SRM - EN 14792:2017
Standard Reference Method / Alternative Method
SRM - EN 15058:2017
SRM - BS EN 14790
The selection of standard reference / alternative methods employed by SOCOTEC is determined, wherever possible by the hierarchy of methodselection outlined in Environmental Protection Agency Technical Guidance Note (Monitoring) AG2.
Monitoring Methods
SRM - EN ISO 16911-1
EXECUTIVE SUMMARY
SRM - US EPA CTM 036
SRM - EN 12619:2013
USEPA M316
SRM - EN 13284-1
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Total Particulate Matter
AE 106 1015 YesSOCOTEC (East
Kilbride)N/A 8 Weeks
Isocyanates AE 027 0605 Yes RPS WK20-03375 8 Weeks
Formaldehydes M103 0605 Yes RPS WK20-03334 8 Weeks
Species Analytical UKAS Lab MCERTS Laboratory Data ArchiveProcedure Number Accredited Archive Period
Analysis LocationTotal Volatile Orangic
Compounds AE 102 1015 YesSOCOTEC (East
Kilbride)SOCOTEC (East
Kilbride)5 years
Oxides of Nitrogen
AE 102 1015 YesSOCOTEC (East
Kilbride)SOCOTEC (East
Kilbride)5 years
Carbon Monoxide AE 102 1015 YesSOCOTEC (East
Kilbride)SOCOTEC (East
Kilbride)5 years
Oxygen AE 102 1015 YesSOCOTEC (East
Kilbride)SOCOTEC (East
Kilbride)5 years
Moisture AE 105 1015 YesSOCOTEC (East
Kilbride)- -
ON-SITE TESTING
Analysis Report number
UKAS Accredited Lab Analysis
Zirconia Cell
The following tables list the analytical methods employed together with the custody details. Unless otherwise stated the samples are archived at the analysis lab location.
Analysis LabArchivePeriod
UKAS Lab Number
Analytical Procedure
Analytical TechniqueSpecies
Non Dispersive Infra Red
SAMPLING METHODS WITH SUBSEQUENT ANALYSIS
Gravimetric
Flame Ionisation Detection
Spectrophotometry
High performance Liquid Chromatography - Ultra Violet
Chemiluminescence
Gravimetric
Analytical Technique
EXECUTIVE SUMMARY
Analytical Methods
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Sampling Plane Validation Criteria Value Units Requirement Compliant Method
Lowest Differential Pressure 76 Pa >= 5 Pa Yes EN 15259
Lowest Gas Velocity 10.5 m/s - - -
Highest Gas Velocity 13.5 m/s - - -
Ratio of Gas Velocities 1.3 : 1 < 3 : 1 Yes EN 15259
Mean Velocity 11.9 m/s - - -
Maximum angle of flow with regard to duct axis <15 o < 15o Yes EN 15259
No local negative flow Yes - - Yes EN 15259
Value Units Isokinetic
Shape Circular -
Depth 1.20 m Sample port size 4" BSP 4" BSP
Width 0.00 m Number of lines used 2 1
Area 1.13 m2 Number of points / line 4 1
Port Depth - mm Duct orientation Vertical VerticalIn 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)
Yes
Outside
No
Yes
Filtration for TPM
No
SAMPLING LINES & POINTSDUCT CHARACTERISTICS
EXECUTIVE SUMMARY
Permanent
Where possible the clearance behind sample line two should be extended to a minimum of 2m or Probe length plus 1m
SAMPLING LOCATION
Yes
No
SAMPLING PLATFORM
Non-Iso & Gases
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Sampling Nozzle
Due to high stack velocities a samlping nozzle smaller than the recommended minimum size of 6mm has been used.
EXECUTIVE SUMMARY
Sampling & Analytical Method Deviations
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APPENDIX 1 - Monitoring Schedule, Calibration Checklist & Monitoring Team
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
APPENDIX 3 - Measurement Uncertainty Budget Calculations
APPENDICES
CONTENTS
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SOCOTEC UKAS Lab MCERTSTechnical Number AccreditedProcedure Method
AE 104 1015 Yes 1AE 116 1015 Yes 1AE 114 1015 Yes 1
AE 102 1015 Yes 1
AE 102 1015 Yes 1AE 102 1015 Yes 1AE 102 1015 Yes 1AE 105 1015 Yes 1AE 154 1015 Yes 1
Method
Formaldehydes
SRM - EN 14792:2017
APPENDIX 1 - Monitoring Schedule, Calibration Checklist & Monitoring Team
Number of Samples
Standard Reference Method / Alternative Method
Isocyanates
OxygenMoistureVelocity
SRM - US EPA CTM 036USEPA M316
SRM - EN 15058:2017
SRM - EN 12619:2013
SRM - EN ISO 16911-1SRM - BS EN 14790
Oxides of NitrogenCarbon Monoxide
AM - EN 14789:2017
SRM - EN 13284-1
Total Volatile Organic Compounds
Species
MONITORING SCHEDULE
Total Particulate Matter
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Equipment I.D. Equipment I.D. Equipment I.D.
LEK 9.30 LEK 12.18 -
LEK 9.31 - LEK 20.2
LEK 9.31 - -
LEK 9.31 - -
LEK 17.17 - LEK 16.9
- - -
LEK 6.43 LEK 13.21A LEK 2.16
- LEK 8.27 -
- - -
- - -
LEK 6.43 - -
- - -
LEK 23.20 LEK 12.8 -
- LEK 8.22 -
- LEK 8.21 -
LEK 15.1r - -
- - LEK 8.22
- - LEK 8.25
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.
Cylinder I.D Number
Supplier ppm %Analytical
Tolerance +/- %
Oxygen Fresh air BOC - 20.96 2.0
Propane LEK 192 BOC 80.2 - 2.0
Nitric Oxide LEK 201 BOC 192 - 2.0
Carbon Monoxide LEK 201 BOC 163 - 2.0- - - - -
Level Expiry TE1 TE2 TE3 TE4 H&S
Enda Flood MM 12 1170 MCERTS Level
2Apr-23 Mar-24 Mar-24 Jun-23 Nov-23 Apr-23
Daniel Scully MM 19 1563MCERTS Trainee
Oct-24 - - - - Oct-24
Site Balance
5m Heated Line (1)
Small DGM
Heated Line Controller (1)
Site temperature Logger
Inclinometer (Swirl Device)
STACK EMISSIONS MONITORING TEAM
Chiller (JCT/MAK 10)
1m Heated Line (2)
Mass Flow Controller
Thermo FID
Digital Temperature Meter
Servomex
Probe Thermocouple
MFC Display module
Box Thermocouples Tape Measure
Extractive Sampling
Equipment Equipment
Horiba PG-250 AnalyserControl Box DGM Laboratory Balance
Instrumental Analyser/s
APPENDIX 1 - Monitoring Schedule, Calibration Checklist & Monitoring Team
CALIBRATEABLE EQUIPMENT CHECKLISTMiscellaneous
Personnel
CALIBRATION GASES
FTIR Heater Box for Heated Line
1m Heated Line (3)
Callipers
20m Heated Line (2)
Anemometer
Dioxins Cond. Thermocouple 10m Heated Line (1)
MONITORING TEAM
Heated Line Controller (2)
Meter In Thermocouple Stopwatch
MCERTS Number
TE / H&S Qualifications and Expiry DateMCERTS
Probe
Probe Thermocouple
Stackmaster
Meter Out Thermocouple
Control Box Timer
Stack Thermocouple
1m Heated Line (1)
L-Pitot
Oven Box
Probe JCT Heated Head Filter
Digital Micromanometer
Bernath 3006 FID Protractor
FT-IR Oven Box
Signal 3030 FID
-
FT-IR Gasmet
Barometer
Equipment
Ecophysics NOx Analyser
Heater Controller
Last Impinger Arm
S-Pitot
Gas (traceable to ISO 17025)
10m Heated Line (2)
15m Heated Line (1)
20m Heated Line (1)
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Uncertainty ELV Emissionmg/m³ mg/m³ Rate g/hr
0.51 15 174
Blank - - -Reference conditions are 273K, 101.3kPa, dry gas .
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 AC0724 0.09770 0.09789 0.00019 167.83970 167.84240 0.00270 0.00289If 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 AC0723 0.09735 0.09738 0.00003 185.61200 185.60980 -0.00220 0.00018If total mass gained is less than the LOD then the LOD is reported
mg/l
BLANKS
SAMPLES
Sampling Times
2.0 10
FILTER INFORMATION
12:05 - 13:0519 February 2020
3.9
TOTAL PARTICULATE MATTER SUMMARYParameter
mg/lAcceptable Value
mg/m³
0.24
Concentration
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Run 1
-
Acetone Blank Value
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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 Kpa 101.4 CO2 % 0.03Stack static pressure, Pstatic pa -190 O2 % 20.90Ps = Pb + Pstatic Kpa 101.2 Total % 20.93
N2 (100 -Total) % 79.07Vol. of water vapour collected, Vwstd Md = 0.44(%CO2)+0.32(%O2)+0.28(%N2) 28.84
g 16.8 Molecular weight of wet gas, Ms
Vwstd = (0.001246)(Vlc) m3 0.0209328 Ms = Md(1 - Bwo) + 18(Bwo) g/gmol 28.54Volume of gas metered dry, Vmstd Actual flow of stack gas, Qa
Volume of gas sample through gas meter, Vm m3 0.827 Area of stack, As m2 1.13
Gas meter correction factor, Yd 0.944 Qa = (60)(As)(Vs) m³/min 878.9Mean dry gas meter temperature, Tm K 291 Total flow of stack gas, QMean pressure drop across orifice, DH mmH2O 19.799 Conversion factor (K/mm.Hg) 0.3592Vmstd = (0.3592)(Vm)(Pb+(DH/13.6))(Yd) m3 0.735 Qstd = (Qa)Ps(0.3592)(1-Bwo) Dry 737.7
(Ts)Volume of gas metered wet, Vmstw @O2ref No O2 RefVmstw = Vmstd + Vwstd m3 0.7559 (Ts)
Qstw = (Qa)Ps(0.3592) Wet 758.68 (Ts)
No Percent isokinetic, %INozzle diameter, Dn mm 4.85
% oxygen measured in gas stream, act%O2 20.9 Nozzle area, An mm2 18.50% oxygen reference condition 21 Total sampling time, q min 60
No O2 Ref %I = (4.6398E6)(Ts)(Vmstd) % 101.5 (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 0.0277 Mass collected on filter, Mf g 0.00019
% 2.77 Mass collected in probe, Mp g 0.00270Moisture by FTIR % - Total mass collected, Mn g 0.00289Velocity of stack gas, Vs Cwet = Mn mg/m³ 3.823Velocity pressure coefficient, Cp 0.90 Vmstw
Mean of velocity heads, DPavg Pa 115.15 Cdry = Mn mg/m³ 3.932Mean stack gas temperature, Ts K 316 Vmstd
Gas density (wet, ambient), p Cdry@X%O2 = Mn mg/m³ No O2 Refp=(Ms*Ps)/(8.314*Ts) kg/m3 1.100Stack Velocity, Vs Particulate Emission Rates, E
m/s 12.95 E = [(Cwet)(Qstw)(60)] / 1000 174.04
Vmstd + Vwstd
O2 Ref = 21.0 - act%O2
21.0 - ref%O2
Vol. of gas metered at O2 Ref. Cond., Vmstd@X%O2
Moisture trap weight increase,Vlc
Tm
QstdO2 = (Qa)Ps(0.3592)(1-Bwo)(O2REF)
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Is the process burning hazardous waste? (If yes, no favourable oxygen correction)
O2 Reference Factor
Vmstd@X%oxygen
𝑉𝑠 = 𝐶𝑝∆𝐷𝑃𝑎𝑣𝑔
𝑝
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litre/min litre/min litre/min mm Hg litre/minRun 1 13.00 0.20 0.00 -406.4 0.26 Yes
% mg/m³ mg/m³Run 1 101.51 Yes Run 1 0.24 0.8 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 43
15
LOD < 5% ELV
Overall Blank Value
Run
Overall Blank Acceptable
Pre-sampling Leak Rate
Mean Sampling Rate
TOTAL PARTICULATE MATTER QUALITY ASSURANCE CHECKLIST
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Result
FILTERS
Daily Emission Limit Value
Isokinetic Variation
LEAK RATEPost-sampling
Leak Rate
°C
1.5
Acceptable Leak Rate
Blank 1
Leak Tests Acceptable?
Run
Post-use Filter Conditioning Temperature
Run
Filter SizeFilter Material Pre-use Filter Conditioning Temperature
Max Filtration Temperature
°C
BLANK VALUE
0.24
WEIGHING BALANCE UNCERTAINTYISOKINETICITYAcceptable Isokineticity
Run
180
Maximum Vacuum
Run
5% ELV
160
Yes
Acceptable Blank Value
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LOD ELV Emissionmg/m³ mg/m³ Rate g/hr
0.0001 0.06 0.0
Field Blank - - -Reference conditions are 273K, 101.3kPa, dry gas .
Lab Result LOD Emissionug mg/m³ Rate g/hr
MDI 0.07 0.0001 0.005MDI 0.07 0.0001 0.005
Reference conditions are 273K, 101.3kPa, dry gas .
mg/m³
0.0001
Sampling Times
0.0001
INDIVIDUAL ISOCYANATES SUMMARY
Run 1
ISOCYANATES SUMMARY
-
Test
0.0001
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
TestConcentration
13:32 - 14:32 19 February 2020
0.000
Concentrationmg/m³
Blank 1 Run 1
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ISOKINETIC SAMPLING EQUATIONS 1 ISOCYANATES
Absolute pressure of stack gas, Ps Velocity of stack gas, Vs
Barometric pressure, Pb kPa 101.4 Velocity pressure coefficient, Cp 0.90Stack static pressure, Pstatic Pa -190 Mean of velocity heads, DPavg Pa 111Ps = Pb + (Pstatic) KPa 101 Mean stack gas temperature, Ts K 316
Gas density (wet, ambient), pp=(Ms*Ps)/(8.314*Ts) kg/m3 1.101
g - Stack Velocity, VsVwstd = (0.001246)(Vlc) m3 - m/s 12.68
Volume of gas metered dry, Vmstd Actual flow of stack gas, Qa
Volume of gas sample through gas meter, Vm m3 0.8178 Area of stack, As 1.13
Gas meter correction factor, Yd 0.9438 Qa = (60)(As)(Vs) m3/min 861
Mean dry gas meter temperature, Tm K 316 Dry total flow of stack gas, Qstd
Mean pressure drop across orifice, DH mmH2O 19.388 Conversion factor (K/mm.Hg) 0.3592Vmstd = (0.3592)(Vm)(Pb+(DH/13.6))(Yd) m30.670 Qstd = (Qa)Ps(0.3592)(1-Bwo) m3/min 723.24 Tm + 273 (Ts) +273Volume of gas metered wet, Vmstw Wet total flow of stack gas, Qstw
Vmstw = Vmstd + Vwstd m3 0.6886 Qstw = (Qa)Ps(0.3592) m3/min 743.8 (Ts) +273
NoQstdO2 = (Qa)Ps(0.3592)(1-Bwo)(O2REF) m3/min No O2 Ref
% oxygen measured in gas stream, act%O2 20.9 (Ts) +273% oxygen reference condition 21 Percent isokinetic, %I
O2 Ref = 21.0 - act%O2 No O2 Ref Nozzle diameter, Dn mm 4.85 21.0 - ref%O2 Nozzle area, An mm2 18.50
Vmstd@X%oxygen = (Vmstd) (O2 Ref) m3 No O2 Ref Total sampling time, q min 60Moisture content, Bwo %I = (4.6398E6)(Ts)(Vmstw) % 97Bwo = Vwstd 0.0277 (Ps)(Vs)(An)(q)(1-Bwo)
% 2.77 Acceptable isokinetic range 95% to 115% YesMoisture by FTIR % - Isocyanates Concentration, CMolecular weight of dry gas, Md Mass of isocyanates collected , M ug 0.0700CO2 % 0.03 Cwet = Mn mg/m³ 0.0001O2 % 20.90 Vmstw
Total % 20.93 Cdry = Mn mg/m³ 0.0001N2 (100 -Total) % 79.07 Vmstd
Cdry@X%O2 = Mn mg/m³ No O2 RefMd = 0.44(%CO2)+0.32(%O2)+0.28(%N2) 28.84Molecular weight of wet gas, Ms Isocayanates Emission Rates, EMs = Md(1 - Bwo) + 18(Bwo) g/gmol 28.5 E = [(Cwet)(Qstw)(60)] / 1000 g/hr 0.005
O2 Reference Factor
Vmstd@X%oxygen
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Vol. of water vapour collected, Vwstd
Dry total flow of stack gas at X% O2, QstdO2
13.6
Moisture trap weight increase,Vlc
Vmstd + Vwstd
Is the process burning hazardous waste? (If yes, no favourable oxygen correction)
Vol. of gas metered at O2 Ref. Cond., Vmstd@X%O2
𝑉𝑠 = 𝐶𝑝∆𝐷𝑃𝑎𝑣𝑔
𝑝
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Leak Test Results Mean Sampling Rate
Pre-sampling Leak Rate
Post-sampling Leak Rate
Acceptable Leak Rate
Leak Tests Acceptable
litre/min litre/min litre/min mm Hg litre/min
12.9 0.10 0.10 -381 0.26 Yes
Isokinetic Criterion Compliance
mm °C
Glass Fibre 47 43Run 1
%
Maximum Filtration
Temperature
Filtration
Run 1
Filter Size
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Run 1
ISOCYANATES QUALITY ASSURANCE CHECKLIST
Isokinetic Variation
Yes
Acceptable Isokineticity
Maximum Vacuum
Filter Material
97.0
Filters Coated with
1-(2-pyridyl)piperazine
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LOD ELV Emissionmg/m³ mg/m³ Rate g/hr
0.02 10 285.38
Field Blank - - -
Reference conditions are 273K, 101.3kPa, dry gas .
Leak Test Results
m³ l/min l/min l/min l/min
Run 1 0.7 13.0 0.20 0.00 0.26 Yes
Filter Material Filter Sizemm
°C
Run 1 Glass Fibre 47 43 N/A Glass
Parameter Total IMP C Absorptionug ug Efficiency %
5085.35 4616.3 9Run 1
12:05 - 13:0519 February 2020
Temperature during storage / transit <25°C
Concentration
Mean Sampling Rate
mg/m³
No
6.92
0.06
FORMALDEHYDES SUMMARY
Leak Tests Acceptable?
Absorption Solutions
ND - None Detected
Sampling Times
Acceptable ?Efficiency %
HPLC Water
-
Acceptable leak rate
Run 1
Type of Absorbers
Acceptable Absorption
95
Post sampling leak rate
FORMALDEHYDES QUALITY ASSURANCE CHECKLIST
Total Sample Volume @ ref
Conditions
Max. Filtration Temp.
Pre sampling leak rate
Test
Absorption Efficiency
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
FORMALDEHYDES ABSORPTION EFFICIENCY
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ISOKINETIC SAMPLING EQUATIONS 1 Formaldehydes
Absolute pressure of stack gas, Ps Velocity of stack gas, Vs
Barometric pressure, Pb kPa 101.4 Velocity pressure coefficient, Cp 0.834Stack static pressure, Pstatic Pa -190 Mean of velocity heads, DPavg Pa 115.15Ps = Pb + (Pstatic) kPa 101.21 Mean stack gas temperature, Ts K 315.88
Gas density (wet, ambient), pVol. of water vapour collected, Vwstd p=(Ms*Ps)/(8.314*Ts) kg/m3 1.100
g - Stack Velocity, VsVwstd = (0.001246)(Vlc) m3 - m/s 12.07
Volume of gas metered dry, Vmstd Actual flow of stack gas, Qa
Volume of gas sample through gas meter, Vm m3 0.8267 Area of stack, As m2 1.13
Gas meter correction factor, Yd 0.9438 Qa = (60)(As)(Vs) m³/min 819Mean dry gas meter temperature, Tm K 290.56 Dry total flow of stack gas, Qstd
Mean pressure drop across orifice, DH mmH2O 19.80 Conversion factor (K/mm.Hg) 0.3592Vmstd = (0.3592)(Vm)(Pb+(DH/13.6))(Yd) m3 0.73 Qstd = (Qa)Ps(0.3592)(1-Bwo) m³/min 687
(Ts)Volume of gas metered wet, Vmstw Wet total flow of stack gas, Qstw
Vmstw = Vmstd + Vwstd m3 0.7559 Qstw = (Qa)Ps(0.3592) m³/min 707 (Ts)
Nom³/min No O2 Ref
% oxygen measured in gas stream, act%O2 20.90 (Ts)% oxygen reference condition 21 Percent isokinetic, %I
O2 Ref = 21.0 - act%O2 No O2 Ref Nozzle diameter, Dn mm 4.85 21.0 - ref%O2 Nozzle area, An mm2 18.50
Vmstd@X%oxygen = (Vmstd) (O2 Ref) m3 No O2 Ref Total sampling time, q min 60Moisture content, Bwo %I = (4.6398E6)(Ts)(Vmstd) % 109Bwo = Vwstd 0.0277 (Ps)(Vs)(An)(q)(1-Bwo)
% 2.77 Acceptable isokinetic range 95% to 115% YesMoisture by FTIR % -Molecular weight of dry gas, Md Mass collected , M ug 5085CO2 0.03 Cwet = Mn mg/m³ 6.728O2 20.90 Vmstw
Total 20.93 Cdry = Mn mg/m³ 6.919N2 (100 -Total) 79.07 Vmstd
Cdry@X%O2 = Mn mg/m³ No O2 RefMd = 0.44(%CO2)+0.32(%O2)+0.28(%N2) 28.84Molecular weight of wet gas, Ms Formaldehydes Emission Rates, EMs = Md(1 - Bwo) + 18(Bwo) g/gmol 28.5 E = [(Cwet)(Qstw)(60)] / 1000 g/hr 285.38
QstdO2 = (Qa)Ps(0.3592)(1-Bwo)(O2REF)
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Formaldehydes Concentration, C
Dry total flow of stack gas at X% O2, QstdO2
Vol. of gas metered at O2 Ref. Cond., Vmstd@X%O2
Is the process burning hazardous waste? (If yes, no favourable oxygen correction)
Vmstd@X%oxygen
Vmstd + Vwstd
Tm
O2 Reference Factor
Moisture trap weight increase,Vlc𝑉𝑠 = 𝐶𝑝
∆𝐷𝑃𝑎𝑣𝑔
𝑝
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LOD ELV Emissionmg/m³ mg/m³ Rate g/hr
0.40 20 201.96
Reference conditions are 273K, 101.3kPa, dry gas .
DateStart TimeEnd Time
Gas Gas Conc Range Instrument Instrument Instrument Zero Down Span down Leak Rate(ppm) Zero Reading Span Reading Zero Reading line reading line reading (%)
Propane 80.2 100 0.41 80.2 0.65 0.05 78.4 2.28Zero and Span gas contained 19.98% Oxygen
DateStart TimeEnd Time
GasMean Raw
Value Zero down Span down Zero Drift Span Drift Corrected Values
ppm line reading line reading (%) (%) ppm / %
Propane 3.11 0.48 80.6 -0.25 0.67 O ON/A - not corrected
Reference conditions are 273K, 101.3kPa, dry gas .
INSTRUMENTAL SPAN & ZERO CHECKS
10:23
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
ConcentrationSampling Times
PRE-SAMPLING CALIBRATION CHECKS
5.1
Corrected for Zero Drift
Run 1
09:59
10:45 - 11:45 19 February 2020
19 February 2020
Test
Corrected for Span Drift
TOTAL VOLATILE ORGANIC COMPOUNDS EMISSIONS CHART
POST-SAMPLING CALIBRATION CHECKS19 February 202014:4014:51
TOTAL VOLATILE ORGANIC COMPOUNDS SUMMARY
mg/m³
0.0
5.0
10.0
15.0
20.0
25.0
10
:45
10
:47
10
:49
10
:51
10
:53
10
:55
10
:57
10
:59
11
:01
11
:03
11
:05
11
:07
11
:09
11
:11
11
:13
11
:15
11
:17
11
:19
11
:21
11
:23
11
:25
11
:27
11
:29
11
:31
11
:33
11
:35
11
:37
11
:39
11
:41
11
:43
11
:45
Co
nce
ntr
atio
n m
g/m
³
Time
Concentration ELV
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LOD ELV Emissionmg/m³ mg/m³ Rate g/hr
0.51 100 30.8
0.28 100 57.61
LOD%
0.01
Reference conditions are 273K, 101.3kPa, dry gas .
Date Chiller Temperature (°C) 2.8
Start Time Requirement < 4°C
End Time Compliant Yes
Gas Range Zero Reading Span Reading Zero Check Zero Check Span Check Response Leak Rate(ppm / %) at analyser at analyser at analyser down line down line Time (Secs) %
Nitric Oxide 250 0.03 193.3 0.16 0.01 189.7 100 1.85
Carbon Monoxide 200 0.28 163.2 0.37 -0.18 163.9 100 -0.45
Oxygen 25 -0.01 21.00 0.01 0.37 20.89 100 0.51
Date Chiller Temperature (°C) 2.8
Start Time Requirement < 4°C
End Time Compliant Yes
Zero Check Span Check Zero Drift Span Drift Corrected Valuesat Analyser at Analyser (%) (%) ppm / %
0.01 191.5 -0.08 -0.85 O ON/A - not corrected
0.09 161.9 -0.17 -0.60 O ON/A - not corrected
-0.01 20.81 -0.11 -0.76 O ON/A - not corrected
COMBUSTION GASES SUMMARY
Test
Concentration
20.87Oxygen
15:03
19 February 2020
mg/m³
Corrected for Span Drift
10:45 - 11:45 19 February 2020
Concentration
POST-SAMPLING CALIBRATION DATA
Gas
Nitric Oxide
Carbon Monoxide
Oxygen
Oxides of Nitrogen 0.8
Sampling Time and Date
09:45
%Test
PRE-SAMPLING CALIBRATION DATA
14:51
10:45 - 11:45 19 February 2020
19 February 2020
12:43
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Carbon Monoxide
Sampling Time and Date
1.47
10:45 - 11:45 19 February 2020
Corrected for Zero Drift
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APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
CARBON MONOXIDE EMISSIONS CHART
OXIDES OF NITROGEN (as NO2) EMISSIONS CHART
0.0
20.0
40.0
60.0
80.0
100.0
120.0
10
:45
10
:47
10
:49
10
:51
10
:53
10
:55
10
:57
10
:59
11
:01
11
:03
11
:05
11
:07
11
:09
11
:11
11
:13
11
:15
11
:17
11
:19
11
:21
11
:23
11
:25
11
:27
11
:29
11
:31
11
:33
11
:35
11
:37
11
:39
11
:41
11
:43
11
:45
Co
nce
ntr
atio
n m
g/m
³
Time
Oxides of Nitrogen NOx
ELV
0.0
20.0
40.0
60.0
80.0
100.0
120.0
10
:45
10
:47
10
:49
10
:51
10
:53
10
:55
10
:57
10
:59
11
:01
11
:03
11
:05
11
:07
11
:09
11
:11
11
:13
11
:15
11
:17
11
:19
11
:21
11
:23
11
:25
11
:27
11
:29
11
:31
11
:33
11
:35
11
:37
11
:39
11
:41
11
:43
11
:45
Co
nce
ntr
atio
n m
g/m
³
Time
Carbon Monoxide CO
ELV
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APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
OXYGEN EMISSIONS CHART
0.0
5.0
10.0
15.0
20.0
25.0
10
:45
10
:47
10
:49
10
:51
10
:53
10
:55
10
:57
10
:59
11
:01
11
:03
11
:05
11
:07
11
:09
11
:11
11
:13
11
:15
11
:17
11
:19
11
:21
11
:23
11
:25
11
:27
11
:29
11
:31
11
:33
11
:35
11
:37
11
:39
11
:41
11
:43
11
:45
Co
nce
ntr
atio
n %
v/v
Time
O2
O2
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Test Number Start Weight End Weight Total gain Concentration LOD Uncertainty
kg kg kg % % %
Run 1 3.0923 3.1091 0.0168 2.8 0.02 3.4
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 60 756 13.0 0.20 0.00 0.26 Yes
Stack Diameter / Depth, D 1.20 m
Stack Width, W 0 m
Stack Area, A 1.13 m2
Average stack gas temperature 55 oC
Stack static pressure -0.1905 kPa
Barometric Pressure 101.4 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 0.028571 0.000286 0.000561 0.027780 0.000278 0.000545
O2 32 1.427679 20.867008 0.208670 0.297914 20.289136 0.202891 0.289664
N2 28 1.249219 79.104420 0.791044 0.988188 76.913772 0.769138 0.960822
H2O 18 0.803070 - - - 2.769312 0.027693 0.022239
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)
PRELIMINARY STACK SURVEY
Leak Tests Acceptable?
1.060
kg/m3
Units
Calculation of Stack Gas Densities
Sampling Time and Date
1.0716
Stack Gas Composition & Molecular Weights
Moisture Determination - Isokinetic
Moisture Quality Assurance
Stack Characteristics
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
1.2733
kg/m31.2867
kg/m3
MOISTURE CALCULATIONS
12:05 - 13:0519 February 2020
Result
kg/m3
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TRAVERSE 1
Traverse Distance DP pt DP pt Temp Velocity O2 Angle
Point into Pa mmH2O oC m/s % of Swirl
duct (m)(average of 3
readings)(average of 3
readings)m³/s Vol o
1 0.08 83.3 8.5 54 10.5 11.8 - <152 0.30 91.5 9.3 54 11.0 12.4 - <153 0.90 139.5 14.2 54 13.5 15.3 - <154 1.12 130.3 13.3 54 13.1 14.8 - <15- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -
Mean - 111.1 11.3 54 12.0 13.6 - -
Traverse Distance DP pt DP pt Temp Velocity O2 Angle
Point into Pa mmH2O oC m/s % of Swirl
duct (m)(average of 3
readings)(average of 3
readings)m³/s Vol o
1 0.08 84.9 8.7 55 10.6 11.9 - <152 0.30 94.7 9.7 55 11.1 12.6 - <153 0.90 118.9 12.1 55 12.5 14.1 - <154 1.12 129.7 13.2 55 13.0 14.8 - <15- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -- - - - - - - - -
Mean - 107.1 10.9 55 11.8 13.4 - -
Start Value End Value Difference Start Value End Value DifferencemmH2O mmH2O % mmH2O mmH2O %
Run 1 112 111 0.9 Pass 122 120 1.6 Pass
RunStagnation
(Pa)Reference
(Pa)Difference
(Pa)
Outcome(Permitted +/- 10 Pa)
Run 1 -195 -201 6.0 Pass
Sampling Line B
09:56-10:1019 February 2020
Volumetric Flow Rate
(actual)
PRELIMINARY STACK SURVEY
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.
S-Type Pitot Stagnation Check
Date of Survey
OutcomePre Traverse Leak Rate
Time of Survey
Run
PITOT LEAK CHECKPost Traverse Leak Rate
Sampling Line A
Outcome
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Velocity Measurement Device: S-Type Pitot
Volumetric Flow Rate
(actual)
PRELIMINARY STACK SURVEY QUALITY ASSURANCE CHECKLIST
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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 11.9 m/s
Duct gas flow conditions Actual Reference UnitsTemperature 55 0 oCTotal Pressure 101.2095 101.3 kPaOxygen 20.9 21 %Moisture 2.77 0.00 %Pitot tube calibration coefficient, Kpt 0.83
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 ((21 - O2a) / (21 - 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
11.90
39252
<15
Calculation of Stack Gas Velocity, V
Calculation of Stack Gas Volumetric Flowrate, Q
4847240370
39252
APPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Sampling Plane Validation Criteria
1.13
Result
10.5
1.3
PRELIMINARY STACK SURVEY (CONTINUED)
Yes
13.5
83
Result
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Value UnitsStack Depth 1.20 m Sampling Distance Distance into UnitsStack Width 0.00 m Point (% of Depth) StackArea 1.13 m2 A 50 0.60 m
Sampling Distance Distance into SwirlPoint (% of Depth) Stack (m) o
1 6.7 0.08 < 152 25.0 0.30 < 153 75.0 0.90 < 154 93.3 1.12 < 15
5 6.7 0.08 < 15
6 25.0 0.30 < 15
7 75.0 0.90 < 15
8 93.3 1.12 < 15- - - -- - - -- - - -- - - -
- - - -
- - - -- - - -- - - -
Isokinetic sampling point - - - -Isokinetic sampling points not used - - - -Non Isokinetic/Gases sampling point - - - -
- - - -
SAMPLING LOCATION
Non-Isokinetic/Gases Sampling
Isokinetic Sampling
STACK DIAGRAMAPPENDIX 2 - Summaries, Calculations, Raw Data and Charts
Sampling Line A
1
2
3
4
Sampling Line B
Gas Point
5
6
7
8
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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 % 0.14 0.63 0.49 1.0 N/A 1.63276 1.54 0.001compliant? Yes Yes Yes Yes N/A Yes Yes Yes
Run UncollectedMass
m³ mg - mg/m³ mgRun 1 0.64 2.8900 1.0 0.035 0.0001 -MU as mg/m3 0.05 0.2449 - 0.035 0.0001 0.25MU as % 1.29 6.2284 - 0.888 0.0036 -
0.51 mg/m³ 12.85 % Result 3.37 % ELV
(k is a coverage factor which gives a 95% confidence in the quoted figures)Reference – SOCOTEC Technical Procedure AE150 Estimation of Uncertainty of Measurement
R1 - Uncertainty expressed at a 95% confidence level (where k = 2)
Combined uncertainty
Volume (STP) Mass of particulate
O2 Correction
APPENDIX 3 - Measurement Uncertainty Budget Calculations
MEASUREMENT UNCERTAINTY BUDGET - TOTAL PARTICULATE MATTER
Leak
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Run Sampled Volume
Sampled Gas Temp
Sampled Gas Pressure
Sampled Gas Humidity
Oxygen Content
Leak Uncollected Mass
m³ K kPa % by volume % by volume % mgMU required < 2% < 2% < 1% < 1% < 10% < 2% < 10% of ELVRun 1 0.001 2 0.5 1 N/A - -as a % 0.15 0.69 0.49 1.00 N/A 0.78 0.00compliant? Yes Yes Yes Yes N/A Yes Yes
Run UncollectedMass
m³ mg - mg/m³ mgRun 1 0.63 0.0001 1.00 0.000 0.0000 -MU as mg/m3 0.00 0.0000 - 0.000 0.0000 1.39MU as % 1.32 0.0045 - 0.449 0.00 -
0.000 mg/m³ 89.70 % Result 0.16 % ELV
(k is a coverage factor which gives a 95% confidence in the quoted figures)Reference – SOCOTEC Technical Procedure AE150 Estimation of Uncertainty of Measurement
APPENDIX 3 - Measurement Uncertainty Budget Calculations
O2 Correction Leak
R1 - Uncertainty expressed at a 95% confidence level (where k = 2)
Volume (STP) Mass of Isocyanates
MEASUREMENT UNCERTAINTY BUDGET - ISOCYANATES
Combined uncertainty
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Run Sampled Volume
Sampled Gas Temp
Sampled Gas Pressure
Sampled Gas Humidity
Oxygen Content
Limit of Detection
Leak
m³ K kPa % by volume % by volume % by mass %MU required <=2% <2.5 k <=1% <=1% <=5% < 5% of ELV <=2%Run 1 0.73495171 290.56 99.5 1.0 - 14.45178 -as a % 0.14 0.69 0.50 1.0 - 0.26 0.00compliant? Yes Yes Yes Yes N/A Yes Yes
Run LabUncertainty
m³ mg - mg/m³ mgRun 1 0.6783 14.4518 - 0.0000 - -MU as mg/m3
0.0915 0.0258 - 0.0000 0.3114 0.3256MU as % 1.3221 0.3729 - 0.0000 4.5 -
0.65 mg/m³ 9.41 % Result 6.51 % ELV
(k is a coverage factor which gives a 95% confidence in the quoted figures)Reference – SOCOTEC Technical Procedure AE150 Estimation of Uncertainty of Measurement
MEASUREMENT UNCERTAINTY BUDGET - ISOKINETIC FORMALDEHYDES
O2 Correction
APPENDIX 3 - Measurement Uncertainty Budget Calculations
Volume (STP)
R1 - Uncertainty expressed at a 95% confidence level (where k = 2)
Mass of Formaldehyde
s
Leak Combined uncertainty
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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 % 0.14 0.63 0.49 1.0 N/A 1.54compliant? Yes Yes Yes Yes N/A Yes
Run UncollectedMass
m³ mg - mg/m³ mgRun 1 0.64 16800 1.0 202.98 58 -MU as % v/v 0.04 0.02 - 0.03 0.010 0.05MU as % 1.29 0.60 - 0.89 0.34 -
0.10 % v/v 3.42 %R1 - Uncertainty expressed at a 95% confidence level (where k = 2)
APPENDIX 3 - Measurement Uncertainty Budget Calculations
MEASUREMENT UNCERTAINTY BUDGET - MOISTURE
Volume (STP) Mass Gained O2 Correction Leak Combined uncertainty
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5.1 mg/m3
20 mg/m3
128.32 mg/m3
160 mg/m3
Performance characteristics Value MU Met?60 Yes60 -60 -60 -
0.25 Yes0.15 Yes0.70 Yes-0.25 Yes0.67 Yes0.02 Yes0.80 Yes0.01 Yes0.10 Yes2.28 No1.0 Yes
Uncertaintyur0ursufit
u0druspresuapresutempuvoltuleakucalib
uf
5.15 mg/m3
0.68 mg/m3
1.33 mg/m3
6.66 % ELV
1.33 mg/m3
25.87 % valueReference – SOCOTEC Technical Procedure AE150 Estimation of Uncertainty of Measurement
-0.13
0.03
0.02
Expanded uncertainty expressed with a level of confidence of 95%
0.04
0.65
Value of uncertainty quantity
Uncertainty of calibration gas
ambient temperature dependence
Combined uncertainty
0.00Dependence on voltage 0.14
0.07
Measurement uncertainty Measured Concentration
% full scale
volume or pressure flow dependence
Measurement period-
<2 % range
Calibration Gas ConcentrationLimit
-
Span drift
% full scale
0.02Standard deviation of repeatability at span level
% full scale
0.00
secondsResponse time
atmopsheric pressure dependence
% of value
Standard deviation of repeatability at zero
<2% range / 24hr% full scale
<2 % / 3 kPa
% of valuedependence on voltage
<3% range / 10 K% of full scale/2 kPaatmospheric pressure dependence
-
Logger sampling interval
Repeatability at span levelDeviation from linearity
<2% range / 24hr
<180
Range
Lack of fit
APPENDIX 3 - Measurement Uncertainty Budget Calculations
% full scale/10V
<3% / 2 kPa
minutes
Expanded uncertainty expressed with a level of confidence of 95%
< 2% of valueUncertainty of calibration gaslosses in the line (leak) < 2% of span gas value
-
% of value
<1 % range
MEASUREMENT UNCERTAINTY BUDGET - VOLATILE ORGANIC COMPOUNDS RUN 1
losses in the line (leak)
ambient temperature dependence
seconds
Zero drift
Repeatability at zero
Performance characteristic
volume or pressure flow dependence
0.01
Measured Concentration
Expanded uncertainty expressed with a level of confidence of 95%
Uncertainty in factor
% full scale/10K
Expanded uncertainty
Units specification
< 0.1%vol /10 volt
Number of readings in measurement
<2 % range
% of full scale/3 kPa
Drift
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100 mg/m3
0.8 mg/m3
394 mg/m3
513 mg/m3
Value MU Met?100 Yes60 -60 -60 -
0.11 Yes0.1 Yes
-0.40 Yes-0.08 Yes-0.85 Yes0.25 Yes0.25 Yes0.00 Yes-1.30 Yes0.00 YesN/A -0.00 Yes
UncertaintyU r = S r
U lof
U d,z
U d,s
U t,z
U t,s
U p
U fit
U v
U i
U adj
0.79 mg/m3
2.11 mg/m3
4.14 mg/m3
4.1 % ELV
4.1 mg/m3
527.6 % value
Performance characteristic
<2 % range
% of upper limit of Cal range
short term zero drift -0.045
% full scale/10K
APPENDIX 3 - Measurement Uncertainty Budget Calculations
MEASUREMENT UNCERTAINTY BUDGET - OXIDES OF NITROGEN
Units specification
Limit value
Cal gas conc
Response time
ambient temperature dependence zero / span
Analyser Full Scale
% of full scale/3 kPa <2 % / 3 kPa
<2% range / 24hr
<2 % range
Logger sampling interval
Repeatability at zero % full scale
<2% range/24hr
-
-0.002Uncertainty of Cal gas 1.920
<3% range / 10 K
short term span drift
Deviation from linearity
% full scale
% full scale/10V<4% of Range
Number of readings in measurementMeasurement period
-
<3% / 2 kPa
< 2% of value
repeatability
seconds
< 0.1%vol /10 volt
Repeatability at span level
losses in the line (leak) % of value
dependence on voltage
<1 % range
-
Expanded uncertainty expressed with a level of confidence of 95%
influence of Ambient Temp at Zero
-
volume or pressure flow dependence
Developed for the STA by R Robinson, NPL
influence of sample gas pressure
Span drift
minutes
Expanded uncertainty expressed with a level of confidence of 95%
% range
% full scale
Combined interference
180
0.675
seconds
Value of uncertainty quantity0.004
0.173
% full scale
Measurement uncertainty (Concentration Measured)
% of full scale/2 kPa
Influence of Vibration
Combined uncertaintyExpanded at a 95% confidence interval
influence of supply voltageinfluence of sample gas flow
Expanded uncertainty expressed with a level of confidence of 95%
lack of fit
0.001
-0.231
-0.491
Concentration @ Ref conditions
% of value
Combined Interfence
atmospheric pressure dependence
Zero drift
<2%
influence of Ambient Temp at Span0.000
0.000
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100 mg/m3
1.5 mg/m3
203.8 mg/m3
250 mg/m3
Value MU Met?100 Yes60 -60 -60 -0.1 Yes0.2 Yes
0.61 Yes-0.17 Yes-0.60 Yes0.2 Yes
0.44 Yes-0.8 Yes
-0.01 Yes-0.06 YesN/A N/A0.00 Yes1.00 Yes
N/A - Horiba's are not effected by Vibration
UncertaintyU r = S r
U lof
U d,z U d,s
U t,z
U t,s
U p
U fit
U v
U i
U adj
1.5 mg/m3
1.4 mg/m3
2.7 mg/m3
2.7 % ELV
2.7 mg/m3
181.7 % value
Number of readings in measurement--
specification
% full scale
% full scale/10V
Span drift
<2 % range
minutes
% full scale
180
-
Units
<3% range / 10 KCombined interferencedependence on voltage
<2 % range
secondsLogger sampling interval
Analyser Full Scale
Limit value
MEASUREMENT UNCERTAINTY BUDGET - CARBON MONOXIDE
% of Range% full scale/10K
% full scale
Deviation from linearity
volume or pressure flow dependence<2% range/24hr
-<1 % rangeRepeatability at zero
Concentration @ Ref conditions
Measurement period
% of full scale/2 kPa
secondsPerformance characteristicsResponse time
APPENDIX 3 - Measurement Uncertainty Budget Calculations
Zero drift
Uncertainty of calibration gas
0.000.14
% of value
<2% range / 24hr
Performance characteristic0.003
influence of sample gas flow
% of upper limit of Cal rangelosses in the line (leak)
<2 % / 3 kPa
< 0.1%vol /10 volt<4% of Range
0.12
short term span drift
Influence of Vibration
atmospheric pressure dependenceambient temperature dependence zero / span
repeatability
% of full scale/3 kPa
<2%
<3% / 2 kPa
Value of uncertainty quantity
-0.10
% of value < 2% of value< 2% of value
lack of fitshort term zero drift
% full scale
0.35
-0.09influence of supply voltage
Combined uncertaintyExpanded uncertainty
influence of Ambient Temp span
Measurement uncertainty (Concentration Measured)
Expanded uncertainty expressed with a level of confidence of 95%
-0.01
Combined Interfence
influence of sample gas pressure0.05
influence of Ambient Temp zero
Reference – SOCOTEC Technical Procedure AE150 Estimation of Uncertainty of MeasurementDeveloped for the STA by R Robinson, NPL
Repeatability at span level
Cal gas conc
% of value
-1.00Uncertainty of Cal gas 0.82
Expanded uncertainty expressed with a level of confidence of 95%
Expanded uncertainty expressed with a level of confidence of 95%
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N/A %vol20.87 %vol20.96 %vol
25 %vol
Value MU Met?100 Yes60 -60 -60 -
0.25 Yes0.15 Yes0.13 Yes-0.11 Yes-0.76 Yes0.03 Yes0.05 Yes-0.05 Yes0.01 Yes0.00 Yes0.01 Yes0.0 Yes
UncertaintyU r = S r
U lof
U d,z
U d,s
U t,z
U t,s
U p
U fit
U v
U i
U adj
20.87 %0.46 %0.91 %
0.9 %
4.36 % vol
0.0173
% full scale/10V < 0.1%vol /10 volt
0.1048
% of valuedependence on voltage
<2% range/24hr
Value of uncertainty quantity
influence of supply voltageCombined Interfence
0.0083
APPENDIX 3 - Measurement Uncertainty Budget Calculations
% of full scale/3 kPavolume or pressure flow dependence
% full scale/10K <3% range / 10 K
lack of fit
Expanded uncertainty expressed with a level of confidence of 95%
Combined uncertainty
Expanded uncertainty expressed with a level of confidence of 95%
0.0017
0.00510.0000influence of sample gas pressure
influence of Ambient Temp at Span
ambient temperature dependence
< 2% of value
Performance characteristicrepeatability
influence of sample gas flow
Developed for the STA by R Robinson, NPL
-0.0030
0.0751
short term span drift
% range <4% of Range
< 2% of value% of value
minutesMeasurement period -
seconds
Reference
Reported ConcentrationCalibration gas
Span drift % full scale
Deviation from linearityRepeatability at span level
Number of readings in measurement
specification
secondsLogger sampling interval
MEASUREMENT UNCERTAINTY BUDGET - OXYGEN
Units
<3% / 2 kPa
-0.0634-0.4407
atmospheric pressure dependence
short term zero drift
Expanded uncertainty
Combined interference
Uncertainty of Cal gas
0.0001
influence of Ambient Temp at Zero
Response time 180
% of value
% full scale
% of full scale/2 kPa
losses in the line (leak)Uncertainty of calibration gas
Measurement uncertainty (Concentration Measured)
Zero drift % full scale
<2 % / 3 kPa
% full scale <2 % rangeRepeatability at zero
-
-
<2 % range
<1 % range-
Analyser Full Scale
<2% range / 24hr
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11.9 m/s48472 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 - 0.96
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 17.68<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 1.67 <1% of value Yes
Uncertainty of absolute pressure in the duct pa 516
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 - 0.0002
m/s0.150.29
%1.32.5
m³/hr12742497
%2.65.2
Reference – SOCOTEC Technical Procedure AE150 Estimation of Uncertainty of Measurement
Combined uncertainty
Note - The expanded uncertainty uses a coverage factor of k = 2.
MEASUREMENT UNCERTAINTY BUDGET - VELOCITY & VOLUMETRIC FLOW RATE
Expanded Measurement Uncertainty of Volumetric Flow Rate at a 95% Confidence IntervalExpressed as a % of the Measured Volumetric Flow RateExpanded 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.
Expanded Measurement Uncertainty of Velocity at a 95% Confidence IntervalExpressed as a % of the Measured VelocityExpanded uncertainty at a 95% Confidence Interval
Measurement Uncertainty Volumetric Flow Rate
Expanded uncertainty at a 95% Confidence Interval
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END OF REPORT
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