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HomeMy WebLinkAboutDAQ-2024-0047961 DAQC-130-24 Site ID 10795 (B4) MEMORANDUM TO: STACK TEST FILE – UTAH MUNICIPAL POWER AGENCY – Provo Power Plant THROUGH: Rik Ombach, Minor Source Oil and Gas Compliance Section Manager FROM: Paul Bushman, Environmental Scientist DATE: February 9, 2024 SUBJECT: Sources: Five (5) Caterpillar G3520H engines Contact: Kevin Garlick: (801) 798-7489 Location: 702 North 300 West, Provo, Utah County, Utah Test Contractor: TETCO Permit/AO#: DAQE-AN107950015-16 dated August 3, 2016 Action Code: TR Subject: Review of stack test report dated February 2, 2024 On February 2, 2024, Utah Division of Air Quality (DAQ) received a test report for five (5) Caterpillar G3520H engines at Provo Power Plant, Utah County, Utah. Testing was performed December 9-16, 2023, to demonstrate compliance with the emission limits found in condition II.B.1.c of Approval Order DAQE-AN1079500015-16. The calculated test results are: Source Test Date Pollutant Method Tester Results DAQ Results Limits Engine 1 January 12, 2024 NOx 7E 0.070 lb/hr 0.0697 lb/hr 0.53 lb/hr 0.010 g/hp-hr 0.010 g/hp-hr 0.07 g/hp-hr Engine 2 January 11, 2024 NOx 7E 0.094 lb/hr 0.0949 lb/hr 0.53 lb/hr 0.014 g/hp-hr 0.0136 g/hp-hr 0.07 g/hp-hr Engine 3 January 15- 16, 2024 NOx 7E 0.188 lb/hr 0.1841 lb/hr 0.53 lb/hr 0.028 g/hp-hr 0.0278 g/hp-hr 0.07 g/hp-hr Engine 4 January 10, 2024 NOx 7E 0.077 lb/hr 0.0774 lb/hr 0.53 lb/hr 0.011 g/hp-hr 0.0112 g/hp-hr 0.07 g/hp-hr Engine 5 January 9- 10, 2024 NOx 7E 0.195 lb/hr 0.1940 lb/hr 0.53 lb/hr 0.029 g/hp-hr 0.0284 g/hp-hr 0.07 g/hp-hr DEVIATIONS: None. CONCLUSION: The stack test report appears to be acceptable. RECOMMENDATION: The emissions from the five (5) Caterpillar G3520H engines should be considered to have been in compliance with the emission limits of condition II.B.1.c of the Approval Order during testing. ATTACHMENTS: DAQ stack test review excel spreadsheets, Utah Municipal Power Agency stack test report. Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #1 Test Date: 1/12/2024 Run #1 2 3 Average Start Time 8:02 9:21 10:42 Stop Time 9:05 10:25 11:45 Sample Duration (minutes)60 60 60 BHP Engine Load - bhp 3170 3165 3170 3168 DS Stack Diameter (inches)21.75 21.75 21.75 21.75 PAVG Average (Delta P)½ (" H2O)½1.3254 1.3061 1.2971 1.3095 CP Pitot Tube Constant (unitless)0.84 0.84 0.84 0.84 TS Stack Temperature (°F)701.3 700.7 701.3 701.1 Pbar Barometric Pressure (" Hg)25.25 25.25 25.25 25.25 Ps Stack Pressure ('' H2O)-0.60 -0.60 -0.60 -0.60 Yd Meter Y Factor (unitless)0.9940 0.9940 0.9940 0.9940 Tm Meter Temperature (°F)83.5 86.3 83.6 84.5 Vm Sample Volume (ft3)37.225 38.252 36.898 37.458 H Orifice Pressure Delta H (" H2O)0.9 0.9 0.9 0.9 Vlc Moisture (g)74.3 70.7 75.0 73.3 O2%vd O2 (%vd)9.8 9.8 9.8 9.8 CO2%vd CO2 (%vd)6.5 6.4 6.4 6.4 N2%vd N2 (%vd)83.8 83.9 83.8 83.8 dry NOX (ppmvd)1.4 1.4 1.7 1.5 Run #1 2 3 Average Vmstd Sample Volume (dscf)30.396 31.075 30.124 30.532 Vwstd Moisture Volume (scf)3.50 3.33 3.54 3.46 Bws Measured Moisture Content (%/100)0.103 0.097 0.105 0.102 Bws Saturated Moisture Content (%/100)239.523 238.672 239.523 239.239 Bws Actual Moisture Content (%/100)0.103 0.097 0.105 0.102 MD Molecular Weight Dry (lb/lb-mole)29.42 29.41 29.41 29.41 MA Molecular Weight Wet (lb/lb-mole)28.24 28.31 28.21 28.25 VS Gas Velocity (ft/sec)121.6 119.6 119.0 120.1 FACFM Gas Flow (acfm)18819 18520 18427 18589 FDSCFM Gas Flow (dscfm)6459 6405 6312 6392 FWSCFM Gas Flow (wscfm)7208 7097 7058 7121 FKWSCFH Gas Flow (kwscfh)432 426 423 427 FKWSCFM Gas Flow (kwscfm)7 7 7 7 lb/hr Gas Flow (lb/hr) 31703 31283 31009 31332 Fo Fo (unitless)1.722 1.747 1.746 1.738 wet O2 (%vw)8.8 8.8 8.8 8.8 wet CO2 (%vw)5.8 5.8 5.7 5.7 wet NOX (ppmvw)1.3 1.3 1.5 1.4 15 NOX (ppmvd @ 15% O2)0.8 0.8 0.9 0.8 lb/hr NOX (lb/hr)0.0668 0.0651 0.0772 0.0697 0.53 g/bhp-hr NOX (g/bhp-hr)0.0096 0.0093 0.0110 0.0100 0.07 Permit Limits Field Reference Method Data Reference Method Calculations Page 1 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #1 Test Date: 1/12/2024 O2 CO2 NOX 20.7 20.4 22.3 9.77 9.75 11.2 0.0 0.0 0.1 9.6 9.7 10.9 Linearity Bias (Zero) 0.0 0.0 0.0 Linearity Bias (Span) 9.8 9.8 11.2 % % (ppm) 0.00 0.00 0.0 9.8 9.8 11.2 20.73 20.41 22.3 0.0 0.0 0.0 9.8 9.8 11.2 20.6 20.2 22.6 0.0 0.0 0.0 0.0 0.1 0.0 0.1 0.3 0.3 0.0 0.0 0.0 0.05% 0.00% 0.45% 0.82% 0.69% 1.35% 0.53% 1.27% 1.35% Span Bias Max Calibration Error Bias Check (Zero) Bias Check (Span) 2 3 4 Results 3 Zero Bias 4 Difference 1 4 Response 1 Linearity Information Gas Span Gas Value/Range Bias Gas Value 2 Gas Concentration 1 2 3 Page 2 of 5 Utah Municipal Power Agency Run 1 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 8:02 Engine #1 Run Length 60 Test Date: 1/12/2024 Stop Time 9:05 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.0 0.0 0.1 9.6 9.7 10.9 0.0 0.1 0.1 9.6 9.7 11.0 0.1% 0.5% 0.4% 0.0 0.0 0.0 0.0% 0.5% 0.0% 0.1% 0.1% 0.4% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.8 6.5 1.4 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.6 6.4 1.5 Post Test Calibration Calibration Information Instrument Range Span Gas Value Gas Calibration Pretest Calibration Zero% Span% Zero% Span% Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Results Page 3 of 5 Utah Municipal Power Agency Run 2 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 9:21 Engine #1 Run Length 60 Test Date: 1/12/2024 Stop Time 10:25 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.0 0.1 0.1 9.6 9.7 11.0 0.0 0.4 0.1 9.7 9.9 11.3 0.2% 2.0% 0.4% 0.0 0.0 0.0 0.1% 1.4% 0.0% 0.4% 0.6% 1.3% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.8 6.4 1.4 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.7 6.5 1.5 Span Gas Value Calibration Pretest Calibration Zero% Calibration Information Results Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Span% Span% Gas Instrument Range Post Test Calibration Zero% Page 4 of 5 Utah Municipal Power Agency Run 3 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 10:42 Engine #1 Run Length 60 Test Date: 1/12/2024 Stop Time 11:45 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.0 0.4 0.1 9.7 9.9 11.3 0.0 0.2 0.1 9.7 9.8 11.2 0.2% 0.7% 0.4% 0.0 0.0 0.0 0.0% 1.2% 0.0% 0.1% 0.2% 0.4% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.8 6.4 1.7 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.7 6.5 1.8 Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Calibration Information Span Gas Value Calibration Pretest Calibration Gas Post Test Calibration Instrument Range Zero% Results Absolute Bias (Zero) Span% Span% Zero% Page 5 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #2 Test Date: 1/11/2024 Run #1 2 3 Average Start Time 8:25 9:42 10:42 Stop Time 9:27 10:57 11:45 Sample Duration (minutes)60 60 60 BHP Engine Load - bhp 3149 3150 3170 3156 DS Stack Diameter (inches)21.75 21.75 21.75 21.75 PAVG Average (Delta P)½ (" H2O)½1.3575 1.3879 1.3102 1.3519 CP Pitot Tube Constant (unitless)0.84 0.84 0.84 0.84 TS Stack Temperature (°F)703.5 705.3 706.8 705.2 Pbar Barometric Pressure (" Hg)25.20 25.20 25.20 25.20 Ps Stack Pressure ('' H2O)-0.75 -0.75 -0.75 -0.75 Yd Meter Y Factor (unitless)0.9940 0.9940 0.9940 0.9940 Tm Meter Temperature (°F)80.2 86.9 88.7 85.3 Vm Sample Volume (ft3)37.022 37.637 37.608 37.422 H Orifice Pressure Delta H (" H2O)0.9 0.9 0.9 0.9 Vlc Moisture (g)77.1 73.4 76.6 75.7 O2%vd O2 (%vd)8.9 9.8 9.4 9.3 CO2%vd CO2 (%vd)6.6 6.4 6.4 6.4 N2%vd N2 (%vd)84.6 83.8 84.2 84.2 dry NOX (ppmvd)1.6 2.4 2.1 2.0 Run #1 2 3 Average Vmstd Sample Volume (dscf)30.355 30.481 30.358 30.398 Vwstd Moisture Volume (scf)3.64 3.46 3.61 3.57 Bws Measured Moisture Content (%/100)0.107 0.102 0.106 0.105 Bws Saturated Moisture Content (%/100)243.251 245.847 248.025 245.708 Bws Actual Moisture Content (%/100)0.107 0.102 0.106 0.105 MD Molecular Weight Dry (lb/lb-mole)29.41 29.41 29.39 29.40 MA Molecular Weight Wet (lb/lb-mole)28.19 28.25 28.18 28.21 VS Gas Velocity (ft/sec)124.9 127.7 120.7 124.4 FACFM Gas Flow (acfm)19335 19762 18690 19262 FDSCFM Gas Flow (dscfm)6581 6753 6348 6561 FWSCFM Gas Flow (wscfm)7374 7525 7107 7335 FKWSCFH Gas Flow (kwscfh)442 452 426 440 FKWSCFM Gas Flow (kwscfm)7 8 7 7 lb/hr Gas Flow (lb/hr) 32369 33104 31194 32222 Fo Fo (unitless)1.828 1.744 1.808 1.794 wet O2 (%vw)7.9 8.8 8.4 8.4 wet CO2 (%vw)5.9 5.7 5.7 5.8 wet NOX (ppmvw)1.4 2.1 1.8 1.8 15 NOX (ppmvd @ 15% O2)0.8 1.3 1.1 1.0 lb/hr NOX (lb/hr)0.0761 0.1145 0.0940 0.0949 0.53 g/bhp-hr NOX (g/bhp-hr)0.0110 0.0165 0.0135 0.0136 0.07 Permit Limits Field Reference Method Data Reference Method Calculations Page 1 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #2 Test Date: 1/11/2024 O2 CO2 NOX 20.7 20.4 22.3 9.77 9.75 11.2 0.2 0.2 -0.1 9.9 9.7 10.9 Linearity Bias (Zero) 0.1 0.0 0.0 Linearity Bias (Span) 9.9 9.9 11.3 % % (ppm) 0.00 0.00 0.0 9.8 9.8 11.2 20.73 20.41 22.3 0.1 0.0 0.0 9.9 9.9 11.3 20.6 20.2 22.6 0.1 0.0 0.0 0.2 0.1 0.1 0.2 0.2 0.3 0.0 0.0 0.0 0.77% 0.69% 0.45% 0.05% 1.08% 1.79% 0.87% 0.83% 1.35% Linearity Information Gas Span Gas Value/Range Bias Gas Value 2 Gas Concentration 1 2 3 Span Bias Max Calibration Error Bias Check (Zero) Bias Check (Span) 2 3 4 Results 3 Zero Bias 4 Difference 1 4 Response 1 Page 2 of 5 Utah Municipal Power Agency Run 1 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 8:25 Engine #2 Run Length 60 Test Date: 1/11/2024 Stop Time 9:27 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.2 0.2 -0.1 9.9 9.7 10.9 -0.01 0.03 0.10 9.84 9.61 11.30 0.3% 0.1% 0.4% 0.0 0.0 0.0 1.1% 0.6% 0.9% 0.3% 0.2% 1.8% Corrected O2 % Corrected CO2 % Corrected NOX ppm 8.9 6.6 1.6 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.0 6.5 1.6 Zero% Span% Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Results Post Test Calibration Calibration Information Instrument Range Span Gas Value Gas Calibration Pretest Calibration Zero% Span% Page 3 of 5 Utah Municipal Power Agency Run 2 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 9:42 Engine #2 Run Length 60 Test Date: 1/11/2024 Stop Time 10:57 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.0 0.0 0.1 9.8 9.6 11.3 0.21 0.15 -0.10 9.90 9.55 11.40 0.8% 0.7% 0.4% 0.0 0.0 0.0 1.1% 0.6% 0.9% 0.3% 0.3% 0.4% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.8 6.4 2.4 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.9 6.3 2.4 Pretest Calibration Zero% Calibration Information Results Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Span% Span% Gas Instrument Range Post Test Calibration Zero% Span Gas Value Calibration Page 4 of 5 Utah Municipal Power Agency Run 3 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 10:42 Engine #2 Run Length 60 Test Date: 1/11/2024 Stop Time 11:45 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.2 0.2 -0.1 9.9 9.6 11.4 0.25 0.20 0.20 9.95 9.52 10.90 1.0% 0.9% 0.9% 0.0 0.0 0.0 0.2% 0.2% 1.3% 0.2% 0.1% 2.2% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.4 6.4 2.1 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.5 6.3 2.1 Post Test Calibration Instrument Range Zero% Results Absolute Bias (Zero) Span% Span% Zero% Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Calibration Information Span Gas Value Calibration Pretest Calibration Gas Page 5 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #3 Test Date: Run 1 1/15/2024, Runs 2 &3 1/16/2024 Run #1 2 3 Average Start Time 8:52 8:07 9:28 Stop Time 9:53 9:10 10:30 Sample Duration (minutes)60 60 60 BHP Engine Load - bhp 2964 3090 3140 3064 DS Stack Diameter (inches)21.75 21.75 21.75 21.75 PAVG Average (Delta P)½ (" H2O)½1.2568 1.3038 1.3268 1.2958 CP Pitot Tube Constant (unitless)0.84 0.84 0.84 0.84 TS Stack Temperature (°F)722.0 709.4 708.1 713.2 Pbar Barometric Pressure (" Hg)25.35 25.55 25.55 25.48 Ps Stack Pressure ('' H2O)-0.85 -0.85 -0.85 -0.85 Yd Meter Y Factor (unitless)0.9940 0.9940 0.9940 0.9940 Tm Meter Temperature (°F)80.5 75.5 90.0 82.0 Vm Sample Volume (ft3)37.271 36.734 37.652 37.219 H Orifice Pressure Delta H (" H2O)0.9 0.9 0.9 0.9 Vlc Moisture (g)76.3 79.3 74.3 76.6 O2%vd O2 (%vd)9.8 9.8 9.7 9.8 CO2%vd CO2 (%vd)6.6 6.5 6.5 6.5 N2%vd N2 (%vd)83.7 83.7 83.8 83.7 dry NOX (ppmvd)9.1 1.5 2.0 4.2 Run #1 2 3 Average Vmstd Sample Volume (dscf)30.724 30.804 30.742 30.756 Vwstd Moisture Volume (scf)3.60 3.74 3.50 3.61 Bws Measured Moisture Content (%/100)0.105 0.108 0.102 0.105 Bws Saturated Moisture Content (%/100)269.314 248.445 246.563 254.774 Bws Actual Moisture Content (%/100)0.105 0.108 0.102 0.105 MD Molecular Weight Dry (lb/lb-mole)29.44 29.43 29.43 29.43 MA Molecular Weight Wet (lb/lb-mole)28.24 28.19 28.26 28.23 VS Gas Velocity (ft/sec)116.1 119.4 121.3 119.0 FACFM Gas Flow (acfm)17975 18490 18785 18417 FDSCFM Gas Flow (dscfm)6071 6338 6489 6299 FWSCFM Gas Flow (wscfm)6786 7111 7233 7043 FKWSCFH Gas Flow (kwscfh)407 427 434 423 FKWSCFM Gas Flow (kwscfm)7 7 7 7 lb/hr Gas Flow (lb/hr) 29844 31224 31828 30965 Fo Fo (unitless)1.699 1.712 1.723 1.711 wet O2 (%vw)8.7 8.7 8.7 8.7 wet CO2 (%vw)5.9 5.8 5.8 5.8 wet NOX (ppmvw)8.1 1.3 1.8 3.7 15 NOX (ppmvd @ 15% O2)4.8 0.8 1.0 2.2 lb/hr NOX (lb/hr)0.3937 0.0670 0.0915 0.1841 0.53 g/bhp-hr NOX (g/bhp-hr)0.0603 0.0098 0.0132 0.0278 0.07 Permit Limits Field Reference Method Data Reference Method Calculations Page 1 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #3 Test Date: Run 1 1/15/2024, Runs 2 &3 1/16/2024 O2 CO2 NOX 20.7 20.4 22.3 9.77 9.75 11.2 0.0 0.1 0.0 9.8 9.7 11.3 Linearity Bias (Zero) 0.1 0.2 0.0 Linearity Bias (Span) 9.8 9.9 11.3 % % (ppm) 0.00 0.00 0.0 9.8 9.8 11.2 20.73 20.41 22.3 0.1 0.2 0.0 9.8 9.9 11.3 20.8 20.3 22.5 0.1 0.2 0.0 0.0 0.1 0.1 0.1 0.1 0.2 0.0 0.0 0.0 0.29% 0.24% 0.04% 0.29% 0.83% 0.00% 0.34% 0.73% 0.90% Span Bias Max Calibration Error Bias Check (Zero) Bias Check (Span) 2 3 4 Results 3 Zero Bias 4 Difference 1 4 Response 1 Linearity Information Gas Span Gas Value/Range Bias Gas Value 2 Gas Concentration 1 2 3 Page 2 of 5 Utah Municipal Power Agency Run 1 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 8:52 Engine #3 Run Length 60 Test Date: Run 1 1/15/2024, Runs 2 &3 1/16/2024 Stop Time 9:53 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.0 0.1 0.0 9.8 9.7 11.3 0.04 0.28 0.00 9.73 9.72 11.20 0.0% 0.6% 0.0% 0.0 0.0 0.0 0.2% 0.9% 0.0% 0.1% 0.2% 0.4% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.8 6.6 9.1 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.7 6.6 9.1 Post Test Calibration Calibration Information Instrument Range Span Gas Value Gas Calibration Pretest Calibration Zero% Span% Zero% Span% Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Results Page 3 of 5 Utah Municipal Power Agency Run 2 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 8:07 Engine #3 Run Length 60 Test Date: Run 1 1/15/2024, Runs 2 &3 1/16/2024 Stop Time 9:10 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.0 0.3 0.0 9.7 9.7 11.2 0.00 0.20 0.10 9.61 9.67 10.90 0.2% 0.2% 0.4% 0.0 0.0 0.0 0.2% 0.4% 0.4% 0.6% 0.2% 1.3% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.8 6.5 1.5 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.7 6.5 1.5 Span Gas Value Calibration Pretest Calibration Zero% Calibration Information Results Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Span% Span% Gas Instrument Range Post Test Calibration Zero% Page 4 of 5 Utah Municipal Power Agency Run 3 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 9:28 Engine #3 Run Length 60 Test Date: Run 1 1/15/2024, Runs 2 &3 1/16/2024 Stop Time 10:30 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.0 0.2 0.1 9.6 9.7 10.9 0.00 0.20 0.10 9.61 9.67 10.90 0.2% 0.2% 0.4% 0.0 0.0 0.0 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.7 6.5 2.0 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.6 6.5 2.0 Calibration Information Span Gas Value Calibration Pretest Calibration Gas Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Post Test Calibration Instrument Range Zero% Results Absolute Bias (Zero) Span% Span% Zero% Page 5 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #4 Test Date: 1/10/2024 Run #1 2 3 Average Start Time 12:30 13:47 15:07 Stop Time 13:31 14:49 16:08 Sample Duration (minutes)60 60 60 BHP Engine Load - bhp 3141 3132 3132 3135 DS Stack Diameter (inches)21.75 21.75 21.75 21.75 PAVG Average (Delta P)½ (" H2O)½1.2670 1.2803 1.3361 1.2945 CP Pitot Tube Constant (unitless)0.84 0.84 0.84 0.84 TS Stack Temperature (°F)699.0 706.4 704.8 703.4 Pbar Barometric Pressure (" Hg)25.15 25.15 25.15 25.15 Ps Stack Pressure ('' H2O)-0.98 -0.98 -0.98 -0.98 Yd Meter Y Factor (unitless)0.9940 0.9940 0.9940 0.9940 Tm Meter Temperature (°F)85.3 87.6 86.6 86.5 Vm Sample Volume (ft3)37.583 38.648 38.473 38.235 H Orifice Pressure Delta H (" H2O)0.9 0.9 0.9 0.9 Vlc Moisture (g)78.2 77.7 81.8 79.2 O2%vd O2 (%vd)9.9 9.7 8.3 9.3 CO2%vd CO2 (%vd)6.6 6.6 6.5 6.6 N2%vd N2 (%vd)83.5 83.8 85.2 84.2 dry NOX (ppmvd)1.6 1.8 1.8 1.7 Run #1 2 3 Average Vmstd Sample Volume (dscf)30.466 31.198 31.114 30.926 Vwstd Moisture Volume (scf)3.69 3.66 3.86 3.74 Bws Measured Moisture Content (%/100)0.108 0.105 0.110 0.108 Bws Saturated Moisture Content (%/100)237.476 248.103 245.778 243.785 Bws Actual Moisture Content (%/100)0.108 0.105 0.110 0.108 MD Molecular Weight Dry (lb/lb-mole)29.45 29.44 29.38 29.42 MA Molecular Weight Wet (lb/lb-mole)28.22 28.24 28.12 28.19 VS Gas Velocity (ft/sec)116.4 118.0 123.3 119.2 FACFM Gas Flow (acfm)18026 18267 19088 18461 FDSCFM Gas Flow (dscfm)6136 6198 6448 6261 FWSCFM Gas Flow (wscfm)6883 6931 7252 7022 FKWSCFH Gas Flow (kwscfh)413 416 435 421 FKWSCFM Gas Flow (kwscfm)7 7 7 7 lb/hr Gas Flow (lb/hr) 30244 30476 31762 30827 Fo Fo (unitless)1.671 1.709 1.930 1.770 wet O2 (%vw)8.8 8.7 7.4 8.3 wet CO2 (%vw)5.9 5.9 5.8 5.9 wet NOX (ppmvw)1.4 1.6 1.6 1.5 15 NOX (ppmvd @ 15% O2)0.9 0.9 0.8 0.9 lb/hr NOX (lb/hr)0.0700 0.0787 0.0835 0.0774 0.53 g/bhp-hr NOX (g/bhp-hr)0.0101 0.0114 0.0121 0.0112 0.07 Permit Limits Field Reference Method Data Reference Method Calculations Page 1 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #4 Test Date: 1/10/2024 O2 CO2 NOX 20.7 20.4 22.3 9.77 9.75 11.2 0.2 0.1 0.2 9.9 9.5 11.1 Linearity Bias (Zero) 0.1 0.0 0.1 Linearity Bias (Span) 9.7 9.8 11.1 % % (ppm) 0.00 0.00 0.0 9.8 9.8 11.2 20.73 20.41 22.3 0.1 0.0 0.1 9.7 9.8 11.1 20.5 20.2 22.6 0.1 0.0 0.1 0.0 0.1 0.1 0.3 0.2 0.3 0.0 0.0 0.0 0.82% 0.49% 0.45% 0.77% 1.71% 0.00% 1.21% 1.08% 1.35% Linearity Information Gas Span Gas Value/Range Bias Gas Value 2 Gas Concentration 1 2 3 Span Bias Max Calibration Error Bias Check (Zero) Bias Check (Span) 2 3 4 Results 3 Zero Bias 4 Difference 1 4 Response 1 Page 2 of 5 Utah Municipal Power Agency Run 1 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 12:30 Engine #4 Run Length 60 Test Date: 1/10/2024 Stop Time 13:31 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.2 0.1 0.2 9.9 9.5 11.1 0.26 0.00 -0.10 9.90 9.45 10.80 1.0% 0.0% 0.9% 0.0 0.0 0.0 0.2% 0.5% 1.3% 0.0% 0.0% 1.3% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.9 6.6 1.6 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 10.0 6.4 1.6 Zero% Span% Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Results Post Test Calibration Calibration Information Instrument Range Span Gas Value Gas Calibration Pretest Calibration Zero% Span% Page 3 of 5 Utah Municipal Power Agency Run 2 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 13:47 Engine #4 Run Length 60 Test Date: 1/10/2024 Stop Time 14:49 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.3 0.0 -0.1 9.9 9.5 10.8 0.29 0.06 0.00 9.62 9.47 11.20 1.2% 0.3% 0.4% 0.0 0.0 0.0 0.1% 0.3% 0.4% 1.4% 0.1% 1.8% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.7 6.6 1.8 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.7 6.4 1.7 Pretest Calibration Zero% Calibration Information Results Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Span% Span% Gas Instrument Range Post Test Calibration Zero% Span Gas Value Calibration Page 4 of 5 Utah Municipal Power Agency Run 3 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 15:07 Engine #4 Run Length 60 Test Date: 1/10/2024 Stop Time 16:08 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.3 0.1 0.0 9.6 9.5 11.2 0.20 0.05 0.00 9.60 9.50 11.10 0.7% 0.2% 0.4% 0.0 0.0 0.0 0.4% 0.0% 0.0% 0.1% 0.1% 0.4% Corrected O2 % Corrected CO2 % Corrected NOX ppm 8.3 6.5 1.8 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 8.2 6.4 1.8 Post Test Calibration Instrument Range Zero% Results Absolute Bias (Zero) Span% Span% Zero% Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Calibration Information Span Gas Value Calibration Pretest Calibration Gas Page 5 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #5 Test Date: Runs 1&2 1/09/2024, Run 3 1/10/2024 Run #1 2 3 Average Start Time 8:15 9:50 8:23 Stop Time 9:20 10:53 16:08 Sample Duration (minutes)60 60 60 BHP Engine Load - bhp 3086 3085 3130 3100 DS Stack Diameter (inches)21.75 21.75 21.75 21.75 PAVG Average (Delta P)½ (" H2O)½1.2701 1.2656 1.3498 1.2952 CP Pitot Tube Constant (unitless)0.84 0.84 0.84 0.84 TS Stack Temperature (°F)712.7 710.3 705.5 709.5 Pbar Barometric Pressure (" Hg)25.50 25.50 25.15 25.38 Ps Stack Pressure ('' H2O)-1.31 -1.31 -1.31 -1.31 Yd Meter Y Factor (unitless)0.9940 0.9940 0.9940 0.9940 Tm Meter Temperature (°F)82.3 83.8 70.8 79.0 Vm Sample Volume (ft3)37.816 37.570 37.098 37.495 H Orifice Pressure Delta H (" H2O)0.9 0.9 0.9 0.9 Vlc Moisture (g)80.5 79.4 77.9 79.3 O2%vd O2 (%vd)10.4 9.5 9.2 9.7 CO2%vd CO2 (%vd)6.6 6.5 7.5 6.9 N2%vd N2 (%vd)83.0 83.9 83.3 83.4 dry NOX (ppmvd)4.6 5.2 3.2 4.3 Run #1 2 3 Average Vmstd Sample Volume (dscf)31.253 30.964 30.895 31.037 Vwstd Moisture Volume (scf)3.80 3.74 3.67 3.74 Bws Measured Moisture Content (%/100)0.108 0.108 0.106 0.107 Bws Saturated Moisture Content (%/100)254.102 250.577 247.032 250.570 Bws Actual Moisture Content (%/100)0.108 0.108 0.106 0.107 MD Molecular Weight Dry (lb/lb-mole)29.47 29.43 29.57 29.49 MA Molecular Weight Wet (lb/lb-mole)28.23 28.19 28.34 28.26 VS Gas Velocity (ft/sec)116.6 116.2 124.2 119.0 FACFM Gas Flow (acfm)18055 17985 19225 18422 FDSCFM Gas Flow (dscfm)6150 6142 6513 6269 FWSCFM Gas Flow (wscfm)6902 6889 7293 7028 FKWSCFH Gas Flow (kwscfh)414 413 438 422 FKWSCFM Gas Flow (kwscfm)7 7 7 7 lb/hr Gas Flow (lb/hr) 30344 30247 32187 30926 Fo Fo (unitless)1.586 1.742 1.560 1.629 wet O2 (%vw)9.3 8.5 8.2 8.7 wet CO2 (%vw)5.9 5.8 6.7 6.1 wet NOX (ppmvw)4.1 4.7 2.8 3.9 15 NOX (ppmvd @ 15% O2)2.6 2.7 1.6 2.3 lb/hr NOX (lb/hr)0.2045 0.2292 0.1482 0.1940 0.53 g/bhp-hr NOX (g/bhp-hr)0.0301 0.0337 0.0215 0.0284 0.07 Permit Limits Field Reference Method Data Reference Method Calculations Page 1 of 5 Utah Municipal Power Agency Prove Power Plant. Site ID: 10795 Utah County, Utah Engine #5 Test Date: Runs 1&2 1/09/2024, Run 3 1/10/2024 O2 CO2 NOX 20.7 20.4 22.3 9.77 9.75 11.2 0.0 0.0 0.0 9.7 9.7 11.0 Linearity Bias (Zero) 0.0 0.0 0.2 Linearity Bias (Span) 9.9 9.8 11.3 % % (ppm) 0.00 0.00 0.0 9.8 9.8 11.2 20.73 20.41 22.3 0.0 0.0 0.2 9.9 9.8 11.3 20.5 20.2 22.4 0.0 0.0 0.2 0.1 0.1 0.1 0.3 0.2 0.1 0.0 0.0 0.0 0.00% 0.15% 0.90% 0.82% 0.64% 1.35% 1.25% 1.03% 0.90% Linearity Information Gas Span Gas Value/Range Bias Gas Value 2 Gas Concentration 1 2 3 Span Bias Max Calibration Error Bias Check (Zero) Bias Check (Span) 2 3 4 Results 3 Zero Bias 4 Difference 1 4 Response 1 Page 2 of 5 Utah Municipal Power Agency Run 1 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 8:15 Engine #5 Run Length 60 Test Date: Runs 1&2 1/09/2024, Run 3 1/10/2024 Stop Time 9:20 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.0 0.0 0.0 9.7 9.7 11.0 0.20 0.10 0.20 9.88 9.69 10.90 1.0% 0.3% 0.0% 0.0 0.0 0.0 1.0% 0.5% 0.9% 1.0% 0.0% 0.4% Corrected O2 % Corrected CO2 % Corrected NOX ppm 10.4 6.6 4.6 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 10.4 6.6 4.6 Zero% Span% Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Results Post Test Calibration Calibration Information Instrument Range Span Gas Value Gas Calibration Pretest Calibration Zero% Span% Page 3 of 5 Utah Municipal Power Agency Run 2 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 9:50 Engine #5 Run Length 60 Test Date: Runs 1&2 1/09/2024, Run 3 1/10/2024 Stop Time 10:53 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.2 0.1 0.2 9.9 9.7 10.9 0.15 0.06 -0.10 9.69 9.56 10.90 0.8% 0.1% 1.3% 0.0 0.0 0.0 0.2% 0.2% 1.3% 0.9% 0.6% 0.0% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.5 6.5 5.2 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.6 6.5 5.1 Pretest Calibration Zero% Calibration Information Results Absolute Bias (Zero) Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Span% Span% Gas Instrument Range Post Test Calibration Zero% Span Gas Value Calibration Page 4 of 5 Utah Municipal Power Agency Run 3 Prove Power Plant. Site ID: 10795 Utah County, Utah Start Time 8:23 Engine #5 Run Length 60 Test Date: Runs 1&2 1/09/2024, Run 3 1/10/2024 Stop Time 16:08 O2 CO2 NOX 20.7 20.4 22 9.77 9.75 11.2 0.3 0.0 0.1 9.8 9.8 11.1 0.24 0.18 0.00 10.05 9.99 11.20 1.2% 0.7% 0.9% 0.0 0.0 0.0 0.0% 0.7% 0.4% 1.1% 1.0% 0.4% Corrected O2 % Corrected CO2 % Corrected NOX ppm 9.2 7.5 3.2 Run Length (Minutes) Uncorrected O2 % Uncorrected CO2 % Uncorrected NOX ppm 60 9.3 7.7 3.2 Post Test Calibration Instrument Range Zero% Results Absolute Bias (Zero) Span% Span% Zero% Absolute Bias (Span) Absolute Drift (Zero) Absolute Drift (Span) Calibration Information Span Gas Value Calibration Pretest Calibration Gas Page 5 of 5 February 2, 2024 Mr. Bryce Bird Division Director Attn: Chad Gilgen Minor Source Compliance Section Manager Utah Division of Air Quality P.O. Box 144820 Salt Lake City, Utah 84114-4820 RE: Provo Power Plant Compliance Test Report Utah Municipal Power Agency (UMPA) is submitting a compliance test report for its engines located at the Provo Power Plant. Testing was completed January 9-16, 2024 to demonstrate compliance with NOx emission limits outlined in DAQE-AN107950015-16. If you have any questions concerning this notification please contact me at (801) 798-7489 or Melissa Armer of Trinity Consultants, Inc. at (208) 472-8837. Sincerely, Kevin Garlick SVP- Generation Utah Municipal Power Agency Enclosure: Provo Power Plant Compliance Test Report Cc: Trinity Consultants Inc. NOX COMPLIANCE TESTS CONDUCTED AT UTAH MUNICIPAL POWER AGENCY (UMPA) - PROVO FACILITY CATERPILLAR G3520H ENGINES 1 - 5 January 9-16, 2024 by: TETCO 391 East 620 South • American Fork, UT 84003 Phone: (801) 492-9106 • Fax: (801) 492-9107 Prepared for: Utah Municipal Power Agency 702 N 300 W Provo, UT 84601 Date of report: January 22, 2024 CERTIFICA TJON OF REPORT 1NTEGR1TY Technical Emissions T esti ng Company (TET CO) certifies tha t thi s report represents the truth as well as can be derived by the methods empl oyed. Every effort was made to obtain accurate and representative data a nd to comply w ith procedures set fo rth in the Federal Regis ter. R eviewer: X uan Dang ~---- Date : Dean Kitch en Reviewer: I ..... '-'(--?~J Date: _________ r _ __;;_r_J_,__ _____ _ II iii TABLE OF CONTENTS PAGE Introduction Test Purpose .........................................................................................................................1 Test Location, Type of Process ............................................................................................1 Test Dates.............................................................................................................................1 Pollutant Tested and Methods Applied ................................................................................1 Test Participants ...................................................................................................................1 Discussion of Errors or Irregularities ...................................................................................2 Quality Assurance ................................................................................................................2 Summary of Results Emission Results ..................................................................................................................3 Process Data .........................................................................................................................3 Gas Analyzer Performance Criteria .....................................................................................3 Source Operation Sampling Port Location .......................................................................................................4 Sampling Point Location......................................................................................................4 Sampling Train Description .................................................................................................4 Sampling and Analytical Procedures ...................................................................................5 Quality Assurance ................................................................................................................5 Appendices A: Complete Results and Sample Equations B: Raw Field Data C: Laboratory Data and Chain of Custody D: Raw Production and Control Equipment Data E: Calibration Procedures and Results F: Related Correspondence iv LIST OF TABLES Table Page I Measured and Allowable NOx Emissions ............................................................................3 II Sample Point Location .........................................................................................................4 III Complete Results - Caterpillar G3520H Engine 1 ............................................. Appendix A IV Complete Results - Caterpillar G3520H Engine 2 ............................................. Appendix A V Complete Results - Caterpillar G3520H Engine 3 ............................................. Appendix A VI Complete Results - Caterpillar G3520H Engine 4 ............................................. Appendix A VII Complete Results - Caterpillar G3520H Engine 5 ............................................. Appendix A LIST OF FIGURES Figure 1 Facility Schematic Representation (Caterpillar G3520H Engines 1 - 5) ........... Appendix D 2 Schematic of Method 4 Sampling Train ............................................................ Appendix E 3 Schematic of Gas Analyzer Sampling Train ...................................................... Appendix E 1 INTRODUCTION Test Purpose This test was conducted to determine the NOx emissions from Utah Municipal Power Agency’s (UMPA), Provo facility, Caterpillar G3520H Engines 1 - 5. Emissions are expressed in parts per million (ppm), grams per horsepower-hour (g/hp-hr), and pounds per hour (lb/hr). Results are used to determine compliance with the facility’s Approval Order, DAQE-AN107950015-16. Test Location, Type of Process All testing was conducted at UMPA’s power generating facility located in Provo, Utah. The five Caterpillar G3520H engines’ exhaust stacks were identical in configuration. A schematic representation of the stacks is found in Appendix D as Figure 1. Test Dates Two runs were completed on Engine 5 January 9, 2024. The final run on Engine 5 and three runs on Engine 4 were completed January 10, 2024. Engine two was tested January 11, 2024. Engine 1 was tested January 12, 2024, and Engine 3 was completed January 16, 2024. Pollutant Tested and Methods Applied The tests were for NOx emissions in accordance with EPA Methods 1-4, and 7E. Test Participants Test Facility (UMPA) Kevin Garlick, Power Resource Manager Thomas Sorrells, Technician Daniel Thompson, Technician TETCO Dean Kitchen Xuan Dang Joseph Wells State Agency None 2 Discussion of Errors or Irregularities There were no errors or irregularities. Quality Assurance Testing procedures and sample recovery techniques were performed according to those outlined in the Federal Register and the Quality Assurance Handbook for Air Pollution Measurement Systems. 3 SUMMARY OF RESULTS Emission Results Table I presents the results of the compliance test. More detailed test data can be found on the Complete Results tables found in Appendix A. Table I. Measured and Allowable NOx Emissions Source Units Measured Emissions Emission Limits 1 Engine 1 g/hp-hr 0.010 0.07 lb/hr 0.070 0.53 Engine 2 g/hp-hr 0.014 0.07 lb/hr 0.094 0.53 Engine 3 g/hp-hr 0.028 0.07 lb/hr 0.188 0.53 Engine 4 g/hp-hr 0.011 0.07 lb/hr 0.077 0.53 Engine 5 g/hp-hr 0.029 0.07 lb/hr 0.195 0.53 1 As stated in the facility’s approval order DAQE-AN107950015-16 Process Data The process was operated according to standard procedures. All pertinent process data was available for recording by agency personnel. Copies of the kilowatt output of each engine being tested are found in Appendix D. The kilowatt outputs were recorded at 15-minutes intervals. Gas Analyzer Performance Criteria The NOx gas analyzer met all bias and calibration checks criteria as specified in the Federal Register. Bias and calibration values are found on the Gas Analyzer Field Data sheets in Appendix B. 4 SOURCE OPERATION Sampling Port Location The inside diameters of the Caterpillar G3520H engines exhaust stacks were 21.75 inches. Port location is depicted in Figure 1 in Appendix D. The ports were located 11.59 diameters (252 inches) downstream from the last disturbance and 7.45 diameters (162 inches) upstream from the next disturbance. Two, two-inch diameter ports were available for testing on each stack. The port reference measured 2.75 inches. Sampling Point Location Table II shows the distance of each sampling point for Method 4 from the inside wall. Each point was marked with a glass tape wrapping and numbered. These points were determined by measuring the distance from the inside wall and adding the reference (port) measurement. Table II. Sample Point Location Sample Point # Point Location from Inside Wall (inches) 1 0.96 2 3.18 3 6.44 4 15.31 5 18.57 6 20.79 Sampling Train Description To determine the actual emission rates for these stacks 40 CFR Part 60 Appendix A, Methods 1-4 and 7E were followed. All sampling trains were made of inert materials (Teflon, stainless steel, and glass) to prevent interference of the sampled gas. The stack analyzer used to conduct Methods 1-4 was constructed to meet the specifications outlined in the CFR. The temperature sensors were K-type thermocouples. Heater, vacuum, and 5 pitot line connections were designed to be interchangeable with all units used by the tester. The probe liner was made of 316 stainless steel. A sampling train sketch is found as Figure 2 in Appendix E. Sample boxes were prepared for testing by following the prescribed procedure outlined in Method 4. The NOx analyzer was an Horiba VIA 510SS Chemiluminescence unit. The analyzer was spanned at 22.3 ppm for all tests. EPA Protocol 1 gases were used as the span and mid-range for the NOx analyzer during all tests; their concentrations were 11.2 and 22.3 ppm. Dry nitrogen was used as the zero gas for the machine. The CO2 /O2 dual gas analyzer was a CAI ZRE unit. The CO2 detector was nondispersive infared and the O2 detector was an electrochemical cell. The CO2 analyzer was spanned at 20.41 percent for all tests and calibrated with EPA Protocol 1 gases of 20.41 and 9.75 percent CO2. The O2 analyzer was spanned at 20.73 percent for all tests and calibrated with EPA Protocol 1 gases of 20.73 and 9.77 percent O2. Dry nitrogen was used as the zero gas for both gases. The sampling train for Method 7E was constructed with a heated stainless steel sampling probe about 3 feet long. The sample line between the sampling probe and gas conditioner was heated Teflon. Both were maintained above 220 degrees Fahrenheit. The sample conditioner used Peltier plates to remove moisture. Sample lines from the gas conditioner to the analyzer were Teflon. A sampling train sketch for this method appears as Figure 3 in Appendix E. Sampling and Analytical Procedures All test procedures employed were as specified in 40 CFR 60, Appendix A. Quality Assurance All equipment set-up, sampling procedures, sample recovery, and equipment calibrations were carried out according to the procedures specified in 40 CFR 60, Appendix A. and the Quality Assurance Handbook for Air Pollution Measurement Systems. A APPENDIX A Complete Results and Sample Equations Table III Complete Results - Caterpillar G3520H Engine 1 Table IV Complete Results - Caterpillar G3520H Engine 2 Table V Complete Results - Caterpillar G3520H Engine 3 Table VI Complete Results - Caterpillar G3520H Engine 4 Table VII Complete Results - Caterpillar G3520H Engine 5 Nomenclature Sample Equations TABLE III COMPLETE RESULTS UTAH MUNICIPAL POWER AGENCY (UMPA), PROVO POWER PLANT CATERPILLER G3520H ENGINE 1 Symbol Description Dimensions Run #1 Run #2 Run #3 Date Date 1/12/2024 1/12/2024 1/12/2024 Begin Time Test Began 8:02 9:21 10:42 End Time Test Ended 9:05 10:25 11:45 Pbm Meter Barometric Pressure In. Hg. Abs 25.25 25.25 25.25 DH Orifice Pressure Drop In. H2O 0.900 0.900 0.900 Y Meter Calibration Y Factor dimensionless 0.994 0.994 0.994 Vm Volume Gas Sampled--Meter Conditions cf 37.225 38.252 36.898 Tm Avg Meter Temperature oF 83.5 86.3 83.6 DP Sq Root Velocity Head Root In. H2O 1.3254 1.3061 1.2971 Wtwc Weight Water Collected Grams 74.3 70.7 75.0 Tt Duration of Test Minutes 60.00 60.00 60.00 Cp Pitot Tube Coefficient Dimensionless 0.84 0.84 0.84 CO2 Volume % Carbon Dioxide Percent 6.45 6.42 6.41 O2 Volume % Oxygen Percent 9.79 9.77 9.78 N2 & CO Volume % Nitrogen and Carbon Monoxide Percent 83.76 83.81 83.81 Vmstd Volume Gas Sampled (Standard)dscf 30.415 31.094 30.142 Vw Volume Water Vapor scf 3.504 3.334 3.537 Bws Fraction H2O in Stack Gas Fraction 0.103 0.097 0.105 Xd Fraction of Dry Gas Fraction 0.897 0.903 0.895 Md Molecular Wt. Dry Gas lb/lbmol 29.42 29.42 29.42 Ms Molecular Wt. Stack Gas lb/lbmol 28.24 28.31 28.22 Ts Avg Stack Temperature oF 701.3 700.7 701.3 As Stack Cross Sectional Area Sq. Ft.2.580 2.580 2.580 PG Stack Static Pressure In. H2O -0.60 -0.60 -0.60 Pbp Sample Port Barometric Pressure In. Hg. Abs 25.22 25.22 25.22 Ps Stack Pressure In. Hg. Abs 25.176 25.176 25.176 Qs Stack Gas Volumetric Flow Rate (Std) dscfm 6.46E+03 6.40E+03 6.31E+03 Qa Stack Gas Volumetric Flow Rate (Actual) cfm 1.88E+04 1.85E+04 1.84E+04 Vs Velocity of Stack Gas fpm 7.30E+03 7.18E+03 7.14E+03 Ave. CNOx Concentration of NOx ppmdv 1.4 1.5 1.7 1.5 ERNOx Emission Rate of NOx lb / hr 0.066 0.067 0.076 0.070 Prod Engine Production Kw 2363.8 2360.4 2363.6 2362.6 ERNOx Emission Rate of NOx g/hp-hr 0.010 0.010 0.011 0.010 TABLE IV COMPLETE RESULTS UTAH MUNICIPAL POWER AGENCY (UMPA), PROVO POWER PLANT CATERPILLER G3520H ENGINE 2 Symbol Description Dimensions Run #1 Run #2 Run #3 Date Date 1/11/2024 1/11/2024 1/11/2024 Begin Time Test Began 8:25 9:42 11:12 End Time Test Ended 9:27 10:57 12:14 Pbm Meter Barometric Pressure In. Hg. Abs 25.20 25.20 25.20 DH Orifice Pressure Drop In. H2O 0.900 0.900 0.900 Y Meter Calibration Y Factor dimensionless 0.994 0.994 0.994 Vm Volume Gas Sampled--Meter Conditions cf 37.022 37.637 37.608 Tm Avg Meter Temperature oF 80.2 86.9 88.7 DP Sq Root Velocity Head Root In. H2O 1.3575 1.3879 1.3102 Wtwc Weight Water Collected Grams 77.1 73.4 76.6 Tt Duration of Test Minutes 60.00 60.00 60.00 Cp Pitot Tube Coefficient Dimensionless 0.84 0.84 0.84 CO2 Volume % Carbon Dioxide Percent 6.58 6.38 6.37 O2 Volume % Oxygen Percent 8.87 9.77 9.38 N2 & CO Volume % Nitrogen and Carbon Monoxide Percent 84.55 83.86 84.25 Vmstd Volume Gas Sampled (Standard)dscf 30.374 30.500 30.376 Vw Volume Water Vapor scf 3.636 3.462 3.612 Bws Fraction H2O in Stack Gas Fraction 0.107 0.102 0.106 Xd Fraction of Dry Gas Fraction 0.893 0.898 0.894 Md Molecular Wt. Dry Gas lb/lbmol 29.41 29.41 29.39 Ms Molecular Wt. Stack Gas lb/lbmol 28.19 28.25 28.18 Ts Avg Stack Temperature oF 703.5 705.3 706.8 As Stack Cross Sectional Area Sq. Ft.2.580 2.580 2.580 PG Stack Static Pressure In. H2O -0.75 -0.75 -0.75 Pbp Sample Port Barometric Pressure In. Hg. Abs 25.17 25.17 25.17 Ps Stack Pressure In. Hg. Abs 25.115 25.115 25.115 Qs Stack Gas Volumetric Flow Rate (Std) dscfm 6.58E+03 6.75E+03 6.35E+03 Qa Stack Gas Volumetric Flow Rate (Actual) cfm 1.93E+04 1.98E+04 1.87E+04 Vs Velocity of Stack Gas fpm 7.50E+03 7.66E+03 7.25E+03 Ave. CNOx Concentration of NOx ppmdv 1.6 2.4 2.0 2.0 ERNOx Emission Rate of NOx lb / hr 0.076 0.114 0.093 0.094 Prod Engine Production Kw 2348.0 2349.5 2363.8 2353.8 ERNOx Emission Rate of NOx g/hp-hr 0.011 0.016 0.013 0.014 TABLE V COMPLETE RESULTS UTAH MUNICIPAL POWER AGENCY (UMPA), PROVO POWER PLANT CATERPILLER G3520H ENGINE 3 Symbol Description Dimensions Run #1 Run #2 Run #3 Date Date 1/15/2024 1/16/2024 1/16/2024 Begin Time Test Began 8:52 8:07 9:28 End Time Test Ended 9:53 9:10 10:30 Pbm Meter Barometric Pressure In. Hg. Abs 25.35 25.55 25.55 DH Orifice Pressure Drop In. H2O 0.900 0.900 0.900 Y Meter Calibration Y Factor dimensionless 0.994 0.994 0.994 Vm Volume Gas Sampled--Meter Conditions cf 37.271 36.734 37.652 Tm Avg Meter Temperature oF 80.5 75.5 90.0 DP Sq Root Velocity Head Root In. H2O 1.2568 1.3038 1.3268 Wtwc Weight Water Collected Grams 76.3 79.3 74.3 Tt Duration of Test Minutes 60.00 60.00 60.00 Cp Pitot Tube Coefficient Dimensionless 0.84 0.84 0.84 CO2 Volume % Carbon Dioxide Percent 6.58 6.51 6.42 O2 Volume % Oxygen Percent 9.79 9.71 9.68 N2 & CO Volume % Nitrogen and Carbon Monoxide Percent 83.63 83.78 83.89 Vmstd Volume Gas Sampled (Standard)dscf 30.742 30.823 30.760 Vw Volume Water Vapor scf 3.598 3.740 3.504 Bws Fraction H2O in Stack Gas Fraction 0.105 0.108 0.102 Xd Fraction of Dry Gas Fraction 0.895 0.892 0.898 Md Molecular Wt. Dry Gas lb/lbmol 29.44 29.43 29.42 Ms Molecular Wt. Stack Gas lb/lbmol 28.25 28.19 28.25 Ts Avg Stack Temperature oF 722.0 709.4 708.1 As Stack Cross Sectional Area Sq. Ft.2.580 2.580 2.580 PG Stack Static Pressure In. H2O -0.85 -0.85 -0.85 Pbp Sample Port Barometric Pressure In. Hg. Abs 25.32 25.32 25.32 Ps Stack Pressure In. Hg. Abs 25.258 25.258 25.258 Qs Stack Gas Volumetric Flow Rate (Std) dscfm 6.07E+03 6.31E+03 6.46E+03 Qa Stack Gas Volumetric Flow Rate (Actual) cfm 1.80E+04 1.86E+04 1.89E+04 Vs Velocity of Stack Gas fpm 6.97E+03 7.20E+03 7.31E+03 Ave. CNOx Concentration of NOx ppmdv 9.3 1.5 2.0 4.3 ERNOx Emission Rate of NOx lb / hr 0.404 0.067 0.093 0.188 Prod Engine Production Kw 2210.0 2304.0 2341.4 2285.1 ERNOx Emission Rate of NOx g/hp-hr 0.062 0.010 0.013 0.028 TABLE VI COMPLETE RESULTS UTAH MUNICIPAL POWER AGENCY (UMPA), PROVO POWER PLANT CATERPILLER G3520H ENGINE 4 Symbol Description Dimensions Run #1 Run #2 Run #3 Date Date 1/10/2024 1/10/2024 1/10/2024 Begin Time Test Began 12:30 13:47 15:07 End Time Test Ended 13:31 14:49 16:08 Pbm Meter Barometric Pressure In. Hg. Abs 25.15 25.15 25.15 DH Orifice Pressure Drop In. H2O 0.900 0.900 0.900 Y Meter Calibration Y Factor dimensionless 0.994 0.994 0.994 Vm Volume Gas Sampled--Meter Conditions cf 37.583 38.648 38.473 Tm Avg Meter Temperature oF 85.3 87.6 86.6 DP Sq Root Velocity Head Root In. H2O 1.2670 1.2803 1.3361 Wtwc Weight Water Collected Grams 78.2 77.7 81.8 Tt Duration of Test Minutes 60.00 60.00 60.00 Cp Pitot Tube Coefficient Dimensionless 0.84 0.84 0.84 CO2 Volume % Carbon Dioxide Percent 6.54 6.56 6.54 O2 Volume % Oxygen Percent 9.99 9.80 8.27 N2 & CO Volume % Nitrogen and Carbon Monoxide Percent 83.47 83.63 85.18 Vmstd Volume Gas Sampled (Standard)dscf 30.485 31.217 31.133 Vw Volume Water Vapor scf 3.688 3.664 3.858 Bws Fraction H2O in Stack Gas Fraction 0.108 0.105 0.110 Xd Fraction of Dry Gas Fraction 0.892 0.895 0.890 Md Molecular Wt. Dry Gas lb/lbmol 29.45 29.44 29.38 Ms Molecular Wt. Stack Gas lb/lbmol 28.21 28.24 28.12 Ts Avg Stack Temperature oF 699.0 706.4 704.8 As Stack Cross Sectional Area Sq. Ft.2.580 2.580 2.580 PG Stack Static Pressure In. H2O -0.98 -0.98 -0.98 Pbp Sample Port Barometric Pressure In. Hg. Abs 25.12 25.12 25.12 Ps Stack Pressure In. Hg. Abs 25.048 25.048 25.048 Qs Stack Gas Volumetric Flow Rate (Std) dscfm 6.13E+03 6.20E+03 6.45E+03 Qa Stack Gas Volumetric Flow Rate (Actual) cfm 1.80E+04 1.83E+04 1.91E+04 Vs Velocity of Stack Gas fpm 6.99E+03 7.08E+03 7.40E+03 Ave. CNOx Concentration of NOx ppmdv 1.6 1.7 1.8 1.7 ERNOx Emission Rate of NOx lb / hr 0.070 0.077 0.083 0.077 Prod Engine Production Kw 2342.6 2335.2 2335.6 2337.8 ERNOx Emission Rate of NOx g/hp-hr 0.010 0.011 0.012 0.011 TABLE VII COMPLETE RESULTS UTAH MUNICIPAL POWER AGENCY (UMPA), PROVO POWER PLANT CATERPILLER G3520H ENGINE 5 Symbol Description Dimensions Run #1 Run #2 Run #3 Date Date 1/9/2024 1/9/2024 1/10/2024 Begin Time Test Began 8:15 9:50 8:23 End Time Test Ended 9:20 10:53 11:43 Pbm Meter Barometric Pressure In. Hg. Abs 25.50 25.50 25.15 DH Orifice Pressure Drop In. H2O 0.900 0.900 0.900 Y Meter Calibration Y Factor dimensionless 0.994 0.994 0.994 Vm Volume Gas Sampled--Meter Conditions cf 37.816 37.570 37.098 Tm Avg Meter Temperature oF 82.3 83.8 70.8 DP Sq Root Velocity Head Root In. H2O 1.2701 1.2656 1.3498 Wtwc Weight Water Collected Grams 80.5 79.4 77.9 Tt Duration of Test Minutes 60.00 60.00 60.00 Cp Pitot Tube Coefficient Dimensionless 0.84 0.84 0.84 CO2 Volume % Carbon Dioxide Percent 6.65 6.57 7.53 O2 Volume % Oxygen Percent 10.42 9.53 9.16 N2 & CO Volume % Nitrogen and Carbon Monoxide Percent 82.93 83.90 83.31 Vmstd Volume Gas Sampled (Standard)dscf 31.272 30.983 30.914 Vw Volume Water Vapor scf 3.796 3.745 3.674 Bws Fraction H2O in Stack Gas Fraction 0.108 0.108 0.106 Xd Fraction of Dry Gas Fraction 0.892 0.892 0.894 Md Molecular Wt. Dry Gas lb/lbmol 29.48 29.43 29.57 Ms Molecular Wt. Stack Gas lb/lbmol 28.24 28.20 28.34 Ts Avg Stack Temperature oF 712.7 710.3 705.5 As Stack Cross Sectional Area Sq. Ft.2.580 2.580 2.580 PG Stack Static Pressure In. H2O -1.31 -1.31 -1.31 Pbp Sample Port Barometric Pressure In. Hg. Abs 25.47 25.47 25.47 Ps Stack Pressure In. Hg. Abs 25.374 25.374 25.374 Qs Stack Gas Volumetric Flow Rate (Std) dscfm 6.15E+03 6.14E+03 6.56E+03 Qa Stack Gas Volumetric Flow Rate (Actual) cfm 1.81E+04 1.80E+04 1.91E+04 Vs Velocity of Stack Gas fpm 7.00E+03 6.97E+03 7.40E+03 Ave. CNOx Concentration of NOx ppmdv 4.6 5.3 3.2 4.4 ERNOx Emission Rate of NOx lb / hr 0.204 0.231 0.149 0.195 Prod Engine Production Kw 2301.0 2300.8 2334.0 2311.9 ERNOx Emission Rate of NOx g/hp-hr 0.030 0.034 0.022 0.029 Method 4 and Gases Nomenclature As =stack cross-sectional area (ft3 ) ASDP =see p DP Btu =unit heat value (British thermal unit) Bws =fraction of water in stack gas C0 =average of initial and final system zero gas calibration bias checks (ppm, percent) Cavg =average gas concentration (as measured) Cdir =measured concentration of a calibration gas when introduced in direct calibration mode Cgas =concentration (ppm dry basis) of sampled gas using Method 6C, 7E, or 10 corrected for bias checks. Species symbol replaces "gas". Cgas (corr)=actual gas concentration corrected to desired percent O2 Cgas (lb/dscf)=gas concentration converted to lb/dscf Cm =average of initial and final system upscale gas calibration bias checks (ppm, percent) Cma =actual concentration of upscale calibration gas CO2 =percent carbon dioxide in the stack gas Cp =Pitot tube coefficient Deq =equivalent diameter for rectangular stack DH =orifice pressure drop (inches H2 O) DH@ =orifice pressure (inches H2 O) DP =stack flow pressure differential (inches H2 O) Ds =diameter of the stack (feet) EA =percent excess air ERgas =emission rate of a gas (lb/hr) ERmmBtu =emission rate per mmBtu or ton of fuel etc. HX =heating value of the fuel (Btu/cf) Md =molecular weight of stack gas, dry basis (lb/lb-mol) mmBtu =million Btu Ms =molecular weight of stack gas, wet basis (g/gmol) Mwgas =molecular weight of the gas species (g/gmol) N2 =percent nitrogen in the stack gas O2 =percent oxygen in the stack gasp DP =average of the square roots of DP (may also be referred to as ASDP) P =facility production rate (units vary) Pbm =absolute barometric pressure at the dry gas meter (inches Hg) Pbp =absolute barometric pressure at the sample location (inches Hg) PG =stack static pressure (inches H2 O) Ps =absolute stack pressure (inches Hg) Pstd =absolute pressure at standard conditions (29.92 inches Hg.) q =time length of test (minutes) Qa =stack gas volumetric flow rate (acfm) Qs =stack gas volumetric flow rate (dscfm) Qw =wet stack gas std. volumetric flow (ft3 /min, wscfm) R =gas constant (21.85 inches Hg ft3 =(lbmol R)) Tm =meter temperature ( F) Ts =stack temperature ( F) Tstd =absolute temperature at standard conditions (528 R) Tt =see q Vm =sample volume (ft3 ) at meter conditions Vmstd =volume standard (dscf), sample volume adjusted to 68 F and 29.92 inches Hg. Method 4 and Gases Nomenclature Vs =velocity of stack gas (fpm) Vw =volume water vapor (scf) at 68 F and 29.92 inches Hg. VX =volume of fuel used (cf) Wtwc =weight of the condensed water collected (grams) Xd =fraction of dry gas Y =meter calibration Y-factor (dimensionless) Method 4 and Gases Sample Equations As = D2 s p 4 Bws = Vw Vmstd +Vw Cgas (corr)=Cgas 20:9 desired %O2 20:9 actual %O2 Cgas (lb/dscf)=Cgas (ppmdv) Kgas lb ppmdv dscf Cgas (lb/mmBtu)=Cgas (ppmdv) Kgas lb ppmdv dscf FD dscf mmBtu 20:9 20:9 %O2 Cgas (lb/mmscf)=Cgas lb mmBtu HCH4 mmBtu mmscf Cx (mass)= Mw Cx (ppm) Pstd R Tstd 106 Deq = 2 L W L +W EA = %O2 0:5 %CO 0:264 %N2 (%O2 0:5 %CO) ERgas = Pstd Qs Mwgas Cgas 60 R Tstd 106 ERgas =Cgas lb mmBtu HCH4 Btu cf 10 6 mmBtu Btu VFuel (cf) 1 q (hr) from fuel usage Md =CO2 0:44 +O2 0:32 +N2 0:28 Ms =Md Xd +18 Bws Ps =Pbp + PG 13:6 Qa =Vs As Qs = Qa Xd Ps Tstd (Ts +460) Pstd Qw = Qs Xd Vmstd =Vm Y Tstd Pbm + DH 13:6 ! (Tm +460) Pstd Vs =85:49 60 Cp p DP s Ts +460 Ps Ms Vw =Wtwc 0:04715 Xd =1 Bws B APPENDIX B Raw Field Data Caterpillar G3520H Engine 1 Preliminary Traverse and Sampling Point Location Data Method 4 Field Data Sheets Gas Analyzer Field Data Sheets Data Logger Printout Stratification Check Caterpillar G3520H Engine 2 Preliminary Traverse and Sampling Point Location Data Method 4 Field Data Sheets Gas Analyzer Field Data Sheets Data Logger Printout Stratification Check Caterpillar G3520H Engine 3 Preliminary Traverse and Sampling Point Location Data Method 4 Field Data Sheets Gas Analyzer Field Data Sheets Data Logger Printout Stratification Check Caterpillar G3520H Engine 4 Preliminary Traverse and Sampling Point Location Data Method 4 Field Data Sheets Gas Analyzer Field Data Sheets Data Logger Printout Stratification Check Caterpillar G3520H Engine 5 Preliminary Traverse and Sampling Point Location Data Method 4 Field Data Sheets Gas Analyzer Field Data Sheets Data Logger Printout Stratification Check Caterpillar G3520H Engine 1 Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % 8:02 1.5 6.42 9.60 9:21 1.8 6.49 9.63 10:42 1.5 6.50 9.71 8:03 1.4 6.42 9.60 9:22 1.7 6.49 9.62 10:43 1.5 6.50 9.72 8:04 1.4 6.42 9.60 9:23 1.7 6.48 9.63 10:44 1.5 6.51 9.70 8:05 1.6 6.42 9.60 9:24 1.8 6.48 9.64 10:45 1.5 6.51 9.72 8:06 1.5 6.42 9.61 9:25 1.9 6.49 9.63 10:46 1.5 6.51 9.71 8:07 1.6 6.44 9.60 9:26 1.8 6.49 9.63 10:47 1.3 6.51 9.70 8:08 1.6 6.44 9.60 9:27 1.8 6.47 9.64 10:48 1.4 6.51 9.72 8:09 1.7 6.44 9.61 9:28 1.9 6.47 9.64 10:49 1.5 6.51 9.72 8:10 1.5 6.44 9.60 9:29 1.6 6.48 9.63 10:50 1.5 6.51 9.71 8:11 1.5 6.44 9.60 9:30 1.7 6.47 9.64 10:51 1.7 6.51 9.71 8:12 1.7 6.44 9.61 9:31 1.7 6.48 9.63 10:52 1.6 6.51 9.73 8:13 1.7 6.44 9.61 9:32 1.7 6.47 9.64 10:53 1.8 6.51 9.72 8:14 1.6 6.44 9.61 9:33 1.8 6.48 9.64 10:54 1.9 6.51 9.71 8:15 1.7 6.44 9.61 9:34 1.8 6.48 9.64 10:55 2.1 6.51 9.73 8:16 1.6 6.44 9.61 9:35 1.8 6.48 9.64 10:56 2.0 6.51 9.73 8:17 1.6 6.45 9.61 9:36 1.6 6.48 9.64 10:57 2.0 6.51 9.72 8:18 1.5 6.45 9.61 9:37 1.6 6.48 9.64 10:58 2.0 6.51 9.73 8:19 1.5 6.44 9.61 9:38 1.6 6.48 9.64 10:59 2.1 6.51 9.72 8:20 1.6 6.45 9.61 9:39 1.6 6.47 9.64 11:00 1.9 6.51 9.72 8:21 1.6 6.45 9.61 9:40 1.5 6.48 9.64 11:01 1.9 6.51 9.74 8:22 1.6 6.46 9.61 9:41 1.7 6.48 9.65 11:02 2.0 6.52 9.72 8:23 1.5 6.46 9.61 9:42 1.7 6.48 9.64 11:03 2.0 6.51 9.73 8:24 1.5 6.44 9.62 9:43 1.7 6.47 9.65 11:04 1.8 6.51 9.74 8:25 1.4 6.44 9.61 9:44 1.7 6.48 9.64 11:05 1.7 6.51 9.74 8:26 1.5 6.44 9.62 9:45 1.7 6.49 9.63 11:06 1.8 6.51 9.73 8:27 1.5 6.44 9.61 9:46 1.7 6.49 9.65 11:07 1.9 6.51 9.74 8:28 1.4 6.44 9.62 9:47 1.8 6.48 9.65 11:08 1.9 6.51 9.73 8:29 1.4 6.44 9.61 9:48 1.9 6.48 9.65 11:09 2.0 6.52 9.72 8:30 1.2 6.44 9.61 9:49 1.9 6.48 9.65 11:10 2.0 6.51 9.74 8:31 1.3 6.44 9.62 9:50 1.8 6.49 9.66 11:11 1.9 6.51 9.73 8:32 1.5 6.44 9.61 9:51 1.7 6.50 9.65 11:12 1.8 6.51 9.72 8:33 1.5 6.44 9.62 9:52 11:13 1.8 6.51 9.74 8:34 9:53 port change 11:14 port change 8:35 port change 9:54 11:15 8:36 9:55 1.5 6.47 9.66 11:16 1.7 6.50 9.74 8:37 1.5 6.39 9.66 9:56 1.5 6.47 9.67 11:17 1.9 6.51 9.73 8:38 1.6 6.41 9.64 9:57 1.4 6.48 9.66 11:18 1.7 6.51 9.74 8:39 1.3 6.42 9.63 9:58 1.3 6.49 9.65 11:19 1.7 6.51 9.74 8:40 1.5 6.42 9.63 9:59 1.4 6.48 9.66 11:20 1.9 6.51 9.74 8:41 1.6 6.44 9.63 10:00 1.5 6.47 9.67 11:21 1.8 6.51 9.73 8:42 1.5 6.44 9.63 10:01 1.3 6.48 9.66 11:22 1.9 6.51 9.73 8:43 1.5 6.44 9.63 10:02 1.4 6.48 9.67 11:23 1.9 6.51 9.74 8:44 1.5 6.44 9.64 10:03 1.4 6.49 9.66 11:24 1.8 6.51 9.74 8:45 1.5 6.44 9.63 10:04 1.4 6.48 9.67 11:25 1.7 6.51 9.74 8:46 1.5 6.44 9.63 10:05 1.3 6.49 9.67 11:26 1.7 6.51 9.73 8:47 1.6 6.45 9.62 10:06 1.3 6.48 9.67 11:27 1.6 6.51 9.74 8:48 1.5 6.44 9.63 10:07 1.2 6.48 9.67 11:28 1.7 6.51 9.73 8:49 1.6 6.44 9.63 10:08 1.2 6.48 9.67 11:29 1.7 6.50 9.73 8:50 1.4 6.45 9.63 10:09 1.2 6.48 9.67 11:30 1.8 6.51 9.73 8:51 1.4 6.45 9.63 10:10 1.2 6.48 9.67 11:31 1.8 6.51 9.72 8:52 1.5 6.45 9.64 10:11 1.2 6.48 9.67 11:32 1.7 6.51 9.73 8:53 1.5 6.45 9.63 10:12 1.4 6.49 9.67 11:33 1.6 6.51 9.72 8:54 1.5 6.45 9.63 10:13 1.3 6.47 9.68 11:34 1.7 6.51 9.71 8:55 1.4 6.46 9.63 10:14 1.4 6.49 9.67 11:35 1.8 6.50 9.73 8:56 1.5 6.47 9.63 10:15 1.5 6.49 9.67 11:36 1.8 6.50 9.73 8:57 1.5 6.46 9.64 10:16 1.4 6.48 9.68 11:37 1.8 6.51 9.71 8:58 1.4 6.47 9.64 10:17 1.5 6.49 9.68 11:38 2.0 6.50 9.72 8:59 1.4 6.48 9.63 10:18 1.6 6.49 9.68 11:39 2.0 6.50 9.73 9:00 1.3 6.47 9.64 10:19 1.5 6.49 9.68 11:40 1.7 6.50 9.73 9:01 1.3 6.47 9.64 10:20 1.5 6.49 9.69 11:41 1.8 6.51 9.72 9:02 1.4 6.47 9.64 10:21 1.4 6.49 9.68 11:42 1.8 6.51 9.72 9:03 1.4 6.47 9.64 10:22 1.4 6.49 9.68 11:43 1.9 6.50 9.72 9:04 1.4 6.48 9.63 10:23 1.5 6.49 9.69 11:44 1.9 6.51 9.71 9:05 1.4 6.48 9.64 10:24 1.2 6.50 9.68 11:45 1.9 6.50 9.72 10:25 1.2 6.50 9.69 Raw Avg 1.5 6.44 9.62 Raw Avg 1.5 6.48 9.66 Raw Avg 1.8 6.51 9.73 Run 3Run 2Run 1 UMPA, PROVO POWER PLANT, ENGINE 1 (1/12/24) Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % Run 3Run 2Run 1 UMPA, PROVO POWER PLANT, ENGINE 1 (1/12/24) Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Zeroi 0.1 0.00 -0.01 Zeroi 0.1 0.11 0.00 Zeroi 0.1 0.14 0.03 Zerof 0.1 0.11 0.00 Zerof 0.1 0.14 0.03 Zerof 0.1 0.15 0.02 Spani 10.9 9.69 9.59 Spani 11.0 9.72 9.61 Spani 11.3 9.85 9.70 Spanf 11.0 9.72 9.61 Spanf 11.3 9.85 9.70 Spanf 11.2 9.80 9.73 Corr.1.4 6.45 9.79 Corr.1.5 6.42 9.77 Corr.1.7 6.41 9.78 Calibration Calibration Calibration Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Zero Cal Gas 0.0 0.00 0.00 0.0 0.00 0.00 0.0 0.00 0.00 Mid Cal Gas 11.2 9.75 9.77 11.2 9.75 9.77 11.2 9.75 9.77 High Cal Gas 22.3 20.41 20.73 22.3 20.41 20.73 22.3 20.41 20.73 Zero Resp 0.0 0.00 -0.02 0.0 0.00 -0.02 0.0 0.00 -0.02 Mid Cal Resp 11.2 9.83 9.76 11.2 9.83 9.76 11.2 9.83 9.76 High Cal Resp 22.6 20.15 20.62 22.6 20.15 20.62 22.6 20.15 20.62 Ana. Cal. Error (ACE)ACE ACE Zero Cal Error 0.00% 0.00% -0.10%0.00% 0.00% -0.10%0.00% 0.00% -0.10% Mid Cal Error 0.00%0.39%-0.05%0.00%0.39%-0.05%0.00%0.39%-0.05% High Cal Error 1.35%-1.27%-0.53%1.35%-1.27%-0.53%1.35%-1.27%-0.53% System Bias (zero, SB)SB SB Sys Zero Cal Bias Initial 0.45% 0.00% 0.05%0.45% 0.54% 0.10%0.45% 0.69% 0.24% Sys Zero Cal Bias Final 0.45%0.54%0.10%0.45%0.69%0.24%0.45%0.73%0.19% System Zero Drift (D)0.00%0.54%0.05%0.00%0.15%0.14%0.00%0.05%0.05% System Bias (upscale, SB)SB SB System Cal Bias Initial -1.35% -0.69% -0.82%-0.90% -0.54% -0.72%0.45% 0.10% -0.29% System Cal Bias Final -0.90%-0.54%-0.72%0.45%0.10%-0.29%0.00%-0.15%-0.14% System Cal Drift (D)0.45%0.15%0.10%1.35%0.64%0.43%0.45%0.24%0.14% CGas = (Cavg - C0) • [Cma / (Cm - C0)]Eq. 7E-5 C0 = (C0i + C0f) / 2 Cm = (Cmi + Cmf) / 2 ACE = (CDir - Cv) • 100% / CS Eq. 7E-1 SB =(Cs - CDir) • 100% / CS Eq. 7E-2 Drift (D) =ABS(SBfinal - Sbinitial)Eq. 7E-4 STRATIFICATION CHECK FIELD SHEET Facility UMPA, Provo Power Plant Source Engine #1 Operator D Kitchen Date 1/12/2024 Time O2 %Time O2 %Time O2 % 7:36 9.68 7:41 9.61 7:46 9.63 7:37 9.69 7:42 9.62 7:47 9.64 7:38 9.69 7:43 9.63 7:48 9.64 7:39 9.70 7:44 9.63 7:49 9.64 7:40 9.70 7:45 9.64 7:50 9.69 Ave 9.69 9.63 9.65 3 Pt. Mean 9.66 9.66 9.66 % Diff From Mean 0.4 0.3 0.1 - The three sample points were on the east/west traverse line. -If the % diff from mean is less than 5%, one sample point may be used. Use the sample point that gave the value closest to the mean value. -If the % diff from mean is between 5% and 10%, use three sample points at 16.7, 50.0, and 83.3 % of diameter. -If the % diff from mean is greater than 10%, sample 12 points chosed according to EPA Method 1. Point 1 Point 2 Point 3 Caterpillar G3520H Engine 2 Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % 8:25 1.3 6.55 9.36 9:42 2.2 6.27 9.88 11:12 2.2 6.30 9.79 8:26 1.3 6.54 9.25 9:43 2.2 6.28 9.89 11:13 2.3 6.30 9.79 8:27 1.4 6.55 9.50 9:44 2.1 6.28 9.91 11:14 2.2 6.27 9.78 8:28 1.4 6.55 9.35 9:45 2.1 6.27 9.75 11:15 2.2 6.26 9.77 8:29 1.2 6.53 8.51 9:46 2.0 6.27 9.80 11:16 2.1 6.26 9.81 8:30 1.2 6.52 8.69 9:47 2.1 6.27 9.79 11:17 2.1 6.27 9.88 8:31 1.4 6.55 9.06 9:48 2.0 6.28 9.74 11:18 2.1 6.28 9.82 8:32 1.3 6.53 8.02 9:49 2.0 6.29 9.76 11:19 2.2 6.28 9.82 8:33 1.4 6.53 8.29 9:50 2.0 6.28 9.82 11:20 2.2 6.30 9.77 8:34 1.4 6.54 7.74 9:51 2.0 6.28 9.85 11:21 2.2 6.31 9.66 8:35 1.4 6.55 8.76 9:52 2.0 6.29 9.77 11:22 2.0 6.29 9.48 8:36 1.3 6.55 8.75 9:53 1.9 6.30 9.88 11:23 2.1 6.29 9.44 8:37 1.1 6.53 8.89 9:54 1.8 6.28 9.90 11:24 2.1 6.27 9.40 8:38 1.1 6.53 9.02 9:55 1.9 6.27 9.90 11:25 2.1 6.26 9.45 8:39 1.2 6.54 9.05 9:56 2.0 6.28 9.88 11:26 2.1 6.26 9.42 8:40 1.2 6.54 8.95 9:57 2.0 6.28 9.89 11:27 2.0 6.27 9.57 8:41 1.3 6.54 8.90 9:58 2.1 6.28 9.91 11:28 2.1 6.28 9.57 8:42 1.3 6.54 8.90 9:59 2.2 6.28 9.91 11:29 2.0 6.28 9.54 8:43 1.3 6.56 9.19 10:00 2.3 6.28 9.92 11:30 2.1 6.29 9.55 8:44 1.2 6.54 9.05 10:01 2.2 6.28 9.90 11:31 2.2 6.30 9.59 8:45 1.3 6.53 8.97 10:02 2.3 6.30 9.89 11:32 2.1 6.28 9.59 8:46 1.4 6.54 7.57 10:03 Engine Down 11:33 2.1 6.27 9.59 8:47 1.3 6.55 7.58 10:14 11:34 2.0 6.27 9.57 8:48 1.3 6.53 7.74 10:15 4.5 6.42 9.57 11:35 2.1 6.29 9.57 8:49 1.1 6.53 7.77 10:16 7.9 6.42 9.55 11:36 2.1 6.29 9.45 8:50 1.3 6.54 8.49 10:17 4.6 6.44 9.52 11:37 2.1 6.30 9.46 8:51 1.3 6.55 9.42 10:18 4.1 6.44 9.55 11:38 2.1 6.30 9.46 8:52 1.4 6.55 9.35 10:19 3.6 6.38 9.58 11:39 2.2 6.30 9.45 8:53 1.4 6.53 9.77 10:20 3.1 6.30 9.76 11:40 2.1 6.30 9.06 8:54 1.4 6.53 9.55 10:21 2.9 6.28 9.80 11:41 2.2 6.30 9.52 8:55 1.5 6.53 9.58 10:22 2.7 6.28 9.84 11:42 2.1 6.31 9.60 8:56 10:23 2.5 6.28 9.81 11:43 8:57 port change 10:24 2.5 6.28 9.86 11:44 port change 8:58 10:25 2.6 6.28 9.82 11:45 8:59 1.3 6.49 9.91 10:26 11:46 2.0 6.30 9.50 9:00 1.8 6.51 9.73 10:27 11:47 2.0 6.29 9.73 9:01 2.0 6.52 9.60 10:28 port change 11:48 2.0 6.28 9.36 9:02 2.1 6.52 9.44 10:29 11:49 1.9 6.30 9.10 9:03 2.1 6.52 9.62 10:30 2.2 6.26 9.97 11:50 2.0 6.30 9.03 9:04 2.0 6.52 9.38 10:31 2.2 6.28 9.98 11:51 2.1 6.30 9.04 9:05 2.0 6.52 9.35 10:32 2.3 6.28 9.94 11:52 2.1 6.30 8.68 9:06 1.9 6.53 9.32 10:33 2.3 6.28 9.95 11:53 2.2 6.30 8.91 9:07 1.7 6.53 9.34 10:34 2.2 6.30 9.94 11:54 2.2 6.31 8.44 9:08 1.7 6.52 9.25 10:35 2.2 6.28 9.97 11:55 2.2 6.30 8.73 9:09 1.8 6.52 8.53 10:36 2.2 6.28 9.94 11:56 2.1 6.30 9.00 9:10 1.8 6.52 8.99 10:37 2.1 6.30 9.94 11:57 2.1 6.30 9.41 9:11 1.8 6.53 8.09 10:38 2.0 6.30 9.93 11:58 1.9 6.30 9.53 9:12 1.8 6.54 8.69 10:39 2.0 6.30 9.94 11:59 1.9 6.30 9.35 9:13 1.8 6.52 8.38 10:40 2.0 6.30 9.94 12:00 1.9 6.31 9.37 9:14 1.9 6.54 8.76 10:41 2.1 6.30 9.92 12:01 2.0 6.31 9.82 9:15 1.9 6.52 8.97 10:42 2.1 6.30 9.90 12:02 2.0 6.29 9.85 9:16 1.9 6.53 9.22 10:43 2.1 6.30 9.92 12:03 1.9 6.28 9.86 9:17 2.0 6.53 9.21 10:44 2.3 6.30 9.94 12:04 1.9 6.30 9.87 9:18 2.0 6.53 9.20 10:45 2.2 6.30 9.94 12:05 2.1 6.29 9.89 9:19 2.0 6.53 9.19 10:46 2.1 6.30 9.94 12:06 2.1 6.28 9.87 9:20 2.0 6.53 9.51 10:47 2.1 6.30 9.95 12:07 2.0 6.28 9.88 9:21 2.0 6.51 9.31 10:48 2.1 6.30 9.94 12:08 2.0 6.28 9.87 9:22 2.0 6.54 8.99 10:49 2.1 6.30 9.95 12:09 1.9 6.29 9.88 9:23 2.0 6.56 9.09 10:50 2.1 6.30 9.93 12:10 2.1 6.28 9.87 9:24 2.1 6.51 9.43 10:51 2.0 6.30 9.95 12:11 2.1 6.28 9.88 9:25 2.1 6.52 8.89 10:52 2.0 6.30 9.95 12:12 2.2 6.29 9.87 9:26 2.0 6.52 8.91 10:53 2.1 6.30 9.96 12:13 2.1 6.28 9.82 9:27 1.9 6.54 9.15 10:54 2.1 6.30 9.91 12:14 2.0 6.28 9.87 10:55 2.1 6.30 9.93 10:56 2.0 6.30 9.94 10:57 1.9 6.30 9.94 Raw Avg 1.6 6.53 8.97 Raw Avg 2.4 6.30 9.87 Raw Avg 2.1 6.29 9.54 Run 3Run 2Run 1 UMPA, PROVO POWER PLANT, ENGINE 2 (1/11/24) Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % Run 3Run 2Run 1 UMPA, PROVO POWER PLANT, ENGINE 2 (1/11/24) Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Zeroi -0.1 0.15 0.21 Zeroi 0.1 0.03 -0.01 Zeroi -0.1 0.15 0.21 Zerof 0.1 0.03 -0.01 Zerof -0.1 0.15 0.21 Zerof 0.2 0.20 0.25 Spani 10.9 9.65 9.91 Spani 11.3 9.61 9.84 Spani 11.4 9.55 9.90 Spanf 11.3 9.61 9.84 Spanf 11.4 9.55 9.90 Spanf 10.9 9.52 9.95 Corr.1.6 6.58 8.87 Corr.2.4 6.38 9.77 Corr.2.0 6.37 9.38 Calibration Calibration Calibration Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Zero Cal Gas 0.0 0.00 0.00 0.0 0.00 0.00 0.0 0.00 0.00 Mid Cal Gas 11.2 9.75 9.77 11.2 9.75 9.77 11.2 9.75 9.77 High Cal Gas 22.3 20.41 20.73 22.3 20.41 20.73 22.3 20.41 20.73 Zero Resp 0.0 0.01 0.05 0.0 0.01 0.05 0.0 0.01 0.05 Mid Cal Resp 11.3 9.87 9.92 11.3 9.87 9.92 11.3 9.87 9.92 High Cal Resp 22.6 20.24 20.55 22.6 20.24 20.55 22.6 20.24 20.55 Ana. Cal. Error (ACE)ACE ACE Zero Cal Error 0.00% 0.05% 0.24%0.00% 0.05% 0.24%0.00% 0.05% 0.24% Mid Cal Error 0.45%0.59%0.72%0.45%0.59%0.72%0.45%0.59%0.72% High Cal Error 1.35%-0.83%-0.87%1.35%-0.83%-0.87%1.35%-0.83%-0.87% System Bias (zero, SB)SB SB Sys Zero Cal Bias Initial -0.45% 0.69% 0.77%0.45% 0.10% -0.29%-0.45% 0.69% 0.77% Sys Zero Cal Bias Final 0.45%0.10%-0.29%-0.45%0.69%0.77%0.90%0.93%0.96% System Zero Drift (D)0.90%0.59%1.06%0.90%0.59%1.06%1.35%0.24%0.19% System Bias (upscale, SB)SB SB System Cal Bias Initial -1.79% -1.08% -0.05%0.00% -1.27% -0.39%0.45% -1.57% -0.10% System Cal Bias Final 0.00%-1.27%-0.39%0.45%-1.57%-0.10%-1.79%-1.71%0.14% System Cal Drift (D)1.79%0.20%0.34%0.45%0.29%0.29%2.24%0.15%0.24% CGas = (Cavg - C0) • [Cma / (Cm - C0)]Eq. 7E-5 C0 = (C0i + C0f) / 2 Cm = (Cmi + Cmf) / 2 ACE = (CDir - Cv) • 100% / CS Eq. 7E-1 SB =(Cs - CDir) • 100% / CS Eq. 7E-2 Drift (D) =ABS(SBfinal - Sbinitial)Eq. 7E-4 STRATIFICATION CHECK FIELD SHEET Facility UMPA, Provo Power Plant Source Engine #2 Operator D Kitchen Date 1/11/2024 Time O2 %Time O2 %Time O2 % 7:53 9.85 7:58 9.79 8:03 9.80 7:54 9.66 7:59 9.89 8:04 9.90 7:55 9.58 8:00 9.88 8:05 9.78 7:56 9.76 8:01 9.89 8:06 9.69 7:57 9.80 8:02 9.76 8:07 9.84 Ave 9.73 9.84 9.80 3 Pt. Mean 9.79 9.79 9.79 % Diff From Mean 0.6 0.5 0.1 - The three sample points were on the east/west traverse line. -If the % diff from mean is less than 5%, one sample point may be used. Use the sample point that gave the value closest to the mean value. -If the % diff from mean is between 5% and 10%, use three sample points at 16.7, 50.0, and 83.3 % of diameter. -If the % diff from mean is greater than 10%, sample 12 points chosed according to EPA Method 1. Point 1 Point 2 Point 3 Caterpillar G3520H Engine 3 Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % 8:52 5.9 6.56 9.70 8:07 0.7 6.51 9.71 9:28 1.9 6.51 9.62 8:53 5.9 6.56 9.70 8:08 0.8 6.52 9.71 9:29 1.9 6.51 9.62 8:54 5.3 6.56 9.71 8:09 0.7 6.52 9.70 9:30 1.9 6.51 9.62 8:55 6.5 6.56 9.71 8:10 0.8 6.53 9.70 9:31 1.9 6.51 9.63 8:56 6.9 6.56 9.71 8:11 0.9 6.54 9.70 9:32 1.9 6.51 9.62 8:57 6.3 6.56 9.72 8:12 0.7 6.54 9.69 9:33 1.9 6.51 9.63 8:58 6.6 6.58 9.68 8:13 0.6 6.54 9.69 9:34 1.9 6.51 9.62 8:59 7.6 6.57 9.69 8:14 0.6 6.54 9.70 9:35 1.9 6.51 9.62 9:00 6.3 6.56 9.72 8:15 0.6 6.54 9.69 9:36 1.9 6.50 9.62 9:01 6.4 6.57 9.72 8:16 0.7 6.54 9.70 9:37 2.0 6.51 9.62 9:02 6.5 6.58 9.72 8:17 0.7 6.54 9.70 9:38 1.8 6.50 9.62 9:03 6.7 6.58 9.72 8:18 0.6 6.55 9.69 9:39 1.8 6.49 9.62 9:04 7.0 6.56 9.73 8:19 0.6 6.55 9.69 9:40 2.1 6.50 9.61 9:05 6.7 6.58 9.72 8:20 0.5 6.56 9.69 9:41 2.0 6.49 9.62 9:06 6.9 6.57 9.72 8:21 0.6 6.54 9.69 9:42 2.1 6.51 9.58 9:07 7.1 6.59 9.71 8:22 0.6 6.54 9.69 9:43 2.1 6.51 9.60 9:08 6.2 6.58 9.73 8:23 0.6 6.55 9.68 9:44 2.0 6.51 9.60 9:09 6.3 6.57 9.74 8:24 0.5 6.55 9.69 9:45 1.9 6.49 9.61 9:10 6.5 6.58 9.73 8:25 0.6 6.56 9.68 9:46 2.0 6.50 9.60 9:11 7.0 6.60 9.70 8:26 1.0 6.56 9.67 9:47 2.1 6.50 9.60 9:12 6.9 6.59 9.71 8:27 1.6 6.55 9.68 9:48 2.0 6.49 9.61 9:13 6.9 6.59 9.73 8:28 1.6 6.56 9.67 9:49 2.1 6.49 9.60 9:14 6.8 6.59 9.74 8:29 1.5 6.56 9.68 9:50 2.1 6.49 9.61 9:15 7.3 6.59 9.74 8:30 1.6 6.56 9.67 9:51 2.0 6.49 9.61 9:16 6.9 6.58 9.74 8:31 1.6 6.56 9.68 9:52 2.0 6.49 9.60 9:17 5.4 6.57 9.75 8:32 1.6 6.56 9.67 9:53 2.0 6.49 9.60 9:18 5.7 6.59 9.74 8:33 1.5 6.56 9.68 9:54 2.0 6.52 9.56 9:19 6.1 6.59 9.74 8:34 1.5 6.55 9.68 9:55 2.1 6.49 9.58 9:20 7.5 6.61 9.71 8:35 1.6 6.55 9.68 9:56 2.1 6.49 9.59 9:21 6.2 6.59 9.74 8:36 1.6 6.54 9.70 9:57 2.1 6.49 9.58 9:22 6.9 6.59 9.74 8:37 1.5 6.54 9.69 9:58 2.0 6.49 9.58 9:23 6.8 6.59 9.74 8:38 1.6 6.54 9.69 9:59 2.0 6.49 9.58 9:24 port change 8:39 10:00 9:25 8:40 port change 10:01 port change 9:26 10.8 6.58 9.76 8:41 10:02 9:27 12.3 6.59 9.75 8:42 2.1 6.54 9.68 10:03 2.0 6.49 9.58 9:28 13.8 6.59 9.74 8:43 2.1 6.53 9.70 10:04 2.2 6.49 9.57 9:29 12.7 6.58 9.77 8:44 2.0 6.54 9.69 10:05 2.1 6.48 9.59 9:30 14.1 6.59 9.76 8:45 2.1 6.56 9.66 10:06 2.0 6.48 9.58 9:31 13.6 6.60 9.75 8:46 2.0 6.55 9.65 10:07 2.0 6.48 9.58 9:32 13.5 6.61 9.73 8:47 2.0 6.54 9.67 10:08 2.1 6.49 9.56 9:33 12.3 6.59 9.76 8:48 2.1 6.54 9.67 10:09 2.2 6.49 9.56 9:34 11.5 6.59 9.76 8:49 2.0 6.54 9.67 10:10 2.1 6.48 9.57 9:35 11.4 6.59 9.76 8:50 2.0 6.54 9.67 10:11 2.1 6.48 9.57 9:36 11.7 6.59 9.76 8:51 2.0 6.54 9.66 10:12 2.1 6.47 9.57 9:37 11.2 6.59 9.76 8:52 2.0 6.54 9.67 10:13 2.1 6.47 9.57 9:38 10.1 6.59 9.78 8:53 2.0 6.54 9.67 10:14 2.2 6.47 9.57 9:39 11.8 6.59 9.77 8:54 2.0 6.54 9.67 10:15 2.0 6.48 9.56 9:40 11.6 6.61 9.74 8:55 2.0 6.54 9.67 10:16 2.0 6.47 9.56 9:41 12.4 6.61 9.75 8:56 1.9 6.54 9.66 10:17 2.0 6.47 9.56 9:42 10.7 6.59 9.77 8:57 2.1 6.54 9.66 10:18 2.0 6.47 9.56 9:43 11.2 6.59 9.77 8:58 2.1 6.54 9.66 10:19 2.0 6.47 9.56 9:44 11.7 6.60 9.77 8:59 2.0 6.54 9.66 10:20 2.1 6.48 9.55 9:45 10.4 6.59 9.78 9:00 2.0 6.53 9.66 10:21 2.1 6.48 9.53 9:46 12.3 6.59 9.78 9:01 2.1 6.54 9.66 10:22 2.0 6.47 9.55 9:47 11.4 6.59 9.78 9:02 2.1 6.52 9.67 10:23 2.1 6.47 9.55 9:48 10.9 6.59 9.78 9:03 2.1 6.52 9.67 10:24 2.1 6.47 9.55 9:49 12.3 6.62 9.74 9:04 2.0 6.53 9.66 10:25 2.0 6.47 9.55 9:50 13.7 6.61 9.75 9:05 1.9 6.53 9.66 10:26 2.0 6.46 9.55 9:51 11.5 6.59 9.78 9:06 2.0 6.53 9.66 10:27 2.1 6.45 9.55 9:52 11.4 6.60 9.78 9:07 1.9 6.52 9.65 10:28 2.1 6.45 9.55 9:53 12.2 6.60 9.78 9:08 2.0 6.52 9.66 10:29 2.1 6.44 9.54 9:09 1.9 6.52 9.65 10:30 1.9 6.44 9.55 9:10 2.0 6.53 9.65 Raw Avg 9.1 6.58 9.74 Raw Avg 1.5 6.54 9.68 Raw Avg 2.0 6.49 9.58 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Zeroi 0.0 0.04 -0.01 Zeroi 0.0 0.10 -0.01 Zeroi 0.0 0.28 0.04 Zerof 0.2 0.12 0.00 Zerof 0.0 0.28 0.04 Zerof 0.1 0.20 0.00 Spani 11.0 9.63 9.65 Spani 11.3 9.68 9.75 Spani 11.2 9.72 9.73 Spanf 10.8 9.80 9.79 Spanf 11.2 9.72 9.73 Spanf 10.9 9.67 9.61 Corr.9.3 6.58 9.79 Corr.1.5 6.51 9.71 Corr.2.0 6.44 9.68 Run 3 (1/16/24)Run 2 (1/16/24)Run 1 (1/15/24) UMPA, PROVO POWER PLANT, ENGINE 3 (1/15-16/24) Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % Run 3 (1/16/24)Run 2 (1/16/24)Run 1 (1/15/24) UMPA, PROVO POWER PLANT, ENGINE 3 (1/15-16/24) Calibration Calibration Calibration Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Zero Cal Gas 0.0 0.00 0.00 0.0 0.00 0.00 0.0 0.00 0.00 Mid Cal Gas 11.2 9.75 9.77 11.2 9.75 9.77 11.2 9.75 9.77 High Cal Gas 22.3 20.41 20.73 22.3 20.41 20.73 22.3 20.41 20.73 Zero Resp 0.0 0.08 0.04 0.1 0.15 0.05 0.1 0.15 0.05 Mid Cal Resp 11.4 9.69 9.68 11.3 9.85 9.81 11.3 9.85 9.81 High Cal Resp 22.6 20.18 20.50 22.5 20.30 20.80 22.5 20.30 20.80 Ana. Cal. Error (ACE)ACE ACE Zero Cal Error 0.00% 0.39% 0.19%0.45% 0.73% 0.24%0.45% 0.73% 0.24% Mid Cal Error 0.90%-0.29%-0.43%0.45%0.49%0.19%0.45%0.49%0.19% High Cal Error 1.35%-1.13%-1.11%0.90%-0.54%0.34%0.90%-0.54%0.34% System Bias (zero, SB)SB SB Sys Zero Cal Bias Initial 0.00% -0.20% -0.24%-0.45% -0.24% -0.29%-0.45% 0.64% -0.05% Sys Zero Cal Bias Final 0.90%0.20%-0.19%-0.45%0.64%-0.05%0.00%0.24%-0.24% System Zero Drift (D)0.90%0.39%0.05%0.00%0.88%0.24%0.45%0.39%0.19% System Bias (upscale, SB)SB SB System Cal Bias Initial -1.79% -0.29% -0.14%0.00% -0.83% -0.29%-0.45% -0.64% -0.39% System Cal Bias Final -2.69%0.54%0.53%-0.45%-0.64%-0.39%-1.79%-0.88%-0.96% System Cal Drift (D)0.90%0.83%0.68%0.45%0.20%0.10%1.35%0.24%0.58% CGas = (Cavg - C0) • [Cma / (Cm - C0)]Eq. 7E-5 C0 = (C0i + C0f) / 2 Cm = (Cmi + Cmf) / 2 ACE = (CDir - Cv) • 100% / CS Eq. 7E-1 SB =(Cs - CDir) • 100% / CS Eq. 7E-2 Drift (D) =ABS(SBfinal - Sbinitial)Eq. 7E-4 STRATIFICATION CHECK FIELD SHEET Facility UMPA, Provo Power Plant Source Engine #3 Operator D Kitchen Date 1/15/2024 Time O2 %Time O2 %Time O2 % 7:50 9.59 7:55 9.66 8:00 9.87 7:51 9.63 7:56 9.66 8:01 9.89 7:52 9.64 7:57 9.67 8:02 9.79 7:53 9.65 7:58 9.68 8:03 9.79 7:54 9.63 7:59 9.82 8:04 9.78 Ave 9.63 9.70 9.83 3 Pt. Mean 9.72 9.72 9.72 % Diff From Mean 0.9 0.2 1.1 - The three sample points were on the east/west traverse line. -If the % diff from mean is less than 5%, one sample point may be used. Use the sample point that gave the value closest to the mean value. -If the % diff from mean is between 5% and 10%, use three sample points at 16.7, 50.0, and 83.3 % of diameter. -If the % diff from mean is greater than 10%, sample 12 points chosed according to EPA Method 1. Point 1 Point 2 Point 3 Caterpillar G3520H Engine 4 Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % 12:30 1.9 6.40 9.75 13:47 1.8 6.39 9.91 15:07 1.5 6.37 8.58 12:31 1.8 6.41 9.94 13:48 1.8 6.40 9.90 15:08 1.5 6.36 8.70 12:32 1.8 6.42 10.01 13:49 1.8 6.39 9.89 15:09 1.5 6.35 8.83 12:33 1.7 6.41 10.05 13:50 1.8 6.38 9.90 15:10 1.5 6.36 8.86 12:34 1.7 6.43 10.06 13:51 1.8 6.39 10.04 15:11 1.4 6.37 8.92 12:35 1.8 6.43 10.03 13:52 1.6 6.40 10.11 15:12 1.4 6.35 8.88 12:36 1.7 6.42 10.04 13:53 1.6 6.38 10.14 15:13 1.5 6.37 8.90 12:37 1.6 6.44 10.03 13:54 1.7 6.40 10.13 15:14 1.7 6.38 8.72 12:38 1.6 6.44 10.02 13:55 1.7 6.40 10.09 15:15 1.6 6.36 8.74 12:39 1.5 6.44 10.04 13:56 1.6 6.39 10.10 15:16 1.6 6.36 8.78 12:40 1.6 6.43 10.06 13:57 1.6 6.40 10.15 15:17 1.6 6.37 8.74 12:41 1.5 6.44 10.04 13:58 1.5 6.39 10.16 15:18 1.5 6.37 8.76 12:42 1.4 6.44 10.05 13:59 1.7 6.40 10.15 15:19 1.5 6.37 8.73 12:43 1.4 6.43 10.07 14:00 1.7 6.40 10.13 15:20 1.6 6.38 8.64 12:44 1.5 6.45 10.04 14:01 1.6 6.39 10.14 15:21 1.6 6.37 8.62 12:45 1.6 6.43 10.04 14:02 1.7 6.40 10.14 15:22 1.5 6.36 8.68 12:46 1.6 6.43 10.05 14:03 1.7 6.42 10.12 15:23 1.6 6.38 8.63 12:47 1.6 6.45 9.98 14:04 1.7 6.40 10.14 15:24 1.6 6.38 3.93 12:48 1.6 6.44 9.99 14:05 1.7 6.40 10.14 15:25 1.6 6.37 3.09 12:49 1.7 6.43 10.03 14:06 1.8 6.40 10.14 15:26 1.6 6.36 4.63 12:50 1.7 6.44 10.03 14:07 1.7 6.40 10.14 15:27 1.6 6.39 8.15 12:51 1.7 6.45 9.99 14:08 1.7 6.40 10.14 15:28 1.6 6.38 8.54 12:52 1.6 6.43 10.03 14:09 1.7 6.40 10.12 15:29 1.6 6.36 8.59 12:53 1.6 6.43 10.01 14:10 1.5 6.40 10.11 15:30 1.5 6.38 8.52 12:54 1.7 6.44 9.97 14:11 1.5 6.41 10.11 15:31 1.6 6.39 8.51 12:55 1.6 6.44 9.99 14:12 1.5 6.40 10.08 15:32 1.5 6.38 8.53 12:56 1.6 6.43 10.12 14:13 1.5 6.38 10.09 15:33 1.5 6.38 8.53 12:57 1.7 6.43 10.11 14:14 1.6 6.40 10.08 15:34 1.5 6.40 8.47 12:58 1.5 6.42 10.13 14:15 1.7 6.41 10.05 15:35 1.6 6.39 8.45 12:59 1.5 6.44 10.11 14:16 1.7 6.39 10.05 15:36 1.6 6.38 8.45 13:00 1.5 6.44 10.08 14:17 1.6 6.39 10.03 15:37 1.7 6.39 8.46 13:01 14:18 1.7 6.41 9.98 15:38 1.7 6.26 8.44 13:02 port change 14:19 port change 15:39 13:03 14:20 15:40 port change 13:04 1.2 6.38 10.52 14:21 1.2 5.77 13.35 15:41 13:05 1.4 6.40 10.14 14:22 1.5 6.34 10.49 15:42 1.6 6.38 8.52 13:06 1.6 6.41 10.04 14:23 1.6 6.36 6.95 15:43 1.7 6.38 8.46 13:07 1.7 6.41 10.00 14:24 1.6 6.38 7.64 15:44 1.9 6.38 8.50 13:08 1.7 6.40 9.98 14:25 1.6 6.37 9.18 15:45 2.0 6.40 8.48 13:09 1.7 6.41 9.98 14:26 1.6 6.37 9.54 15:46 2.0 6.39 8.44 13:10 1.7 6.42 9.96 14:27 1.5 6.39 9.63 15:47 2.0 6.39 8.35 13:11 1.7 6.40 9.98 14:28 1.4 6.40 9.58 15:48 2.1 6.40 8.42 13:12 1.6 6.41 9.96 14:29 1.5 6.38 9.49 15:49 2.0 6.40 8.39 13:13 1.7 6.42 9.93 14:30 1.6 6.38 9.46 15:50 1.9 6.39 8.33 13:14 1.6 6.41 9.95 14:31 1.7 6.38 9.47 15:51 1.9 6.40 8.15 13:15 1.5 6.40 9.95 14:32 1.7 6.38 9.46 15:52 2.0 6.40 7.25 13:16 1.5 6.42 9.93 14:33 1.8 6.38 9.39 15:53 2.0 6.40 6.34 13:17 1.5 6.41 9.91 14:34 1.9 6.40 9.27 15:54 2.1 6.41 7.67 13:18 1.5 6.40 9.92 14:35 1.9 6.38 9.19 15:55 2.0 6.40 7.93 13:19 1.6 6.41 9.91 14:36 1.8 6.38 9.07 15:56 1.9 6.40 8.10 13:20 1.6 6.42 9.88 14:37 1.8 6.38 9.00 15:57 1.8 6.42 8.15 13:21 1.5 6.40 9.90 14:38 1.9 6.38 9.00 15:58 1.6 6.40 8.25 13:22 1.5 6.40 9.91 14:39 1.9 6.38 9.06 15:59 1.7 6.40 8.28 13:23 1.7 6.41 9.91 14:40 1.8 6.39 9.27 16:00 1.8 6.41 8.28 13:24 1.7 6.40 9.91 14:41 1.7 6.39 9.15 16:01 2.0 6.41 8.23 13:25 1.6 6.39 9.91 14:42 1.7 6.38 7.97 16:02 2.1 6.40 8.24 13:26 1.6 6.40 9.88 14:43 1.7 6.39 8.49 16:03 2.1 6.41 8.24 13:27 1.7 6.40 9.88 14:44 1.7 6.39 8.70 16:04 2.5 6.41 8.27 13:28 1.7 6.38 9.89 14:45 1.6 6.38 8.80 16:05 2.8 6.40 8.27 13:29 1.6 6.40 9.86 14:46 1.6 6.38 8.82 16:06 2.9 6.41 8.26 13:30 1.6 6.39 9.85 14:47 1.7 6.38 9.16 16:07 2.7 6.43 8.31 13:31 1.6 6.38 9.87 14:48 1.8 6.38 9.22 16:08 2.3 6.41 8.31 14:49 1.7 6.37 9.23 Raw Avg 1.6 6.42 9.99 Raw Avg 1.7 6.38 9.67 Raw Avg 1.8 6.38 8.18 Run 3Run 2Run 1 UMPA, PROVO POWER PLANT, ENGINE 4 (1/10/24) Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % Run 3Run 2Run 1 UMPA, PROVO POWER PLANT, ENGINE 4 (1/10/24) Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Zeroi 0.2 0.10 0.22 Zeroi -0.1 0.00 0.26 Zeroi 0.0 0.06 0.29 Zerof -0.1 0.00 0.26 Zerof 0.0 0.06 0.29 Zerof 0.0 0.05 0.20 Spani 11.1 9.65 9.90 Spani 10.8 9.45 9.65 Spani 11.2 9.47 9.62 Spanf 10.8 9.45 9.65 Spanf 11.2 9.47 9.62 Spanf 11.1 9.50 9.60 Corr.1.6 6.54 9.99 Corr.1.7 6.56 9.80 Corr.1.8 6.54 8.27 Calibration Calibration Calibration Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Zero Cal Gas 0.0 0.00 0.00 0.0 0.00 0.00 0.0 0.00 0.00 Mid Cal Gas 11.2 9.75 9.77 11.2 9.75 9.77 11.2 9.75 9.77 High Cal Gas 22.3 20.41 20.73 22.3 20.41 20.73 22.3 20.41 20.73 Zero Resp 0.1 0.00 0.05 0.1 0.00 0.05 0.1 0.00 0.05 Mid Cal Resp 11.1 9.80 9.74 11.1 9.80 9.74 11.1 9.80 9.74 High Cal Resp 22.6 20.19 20.48 22.6 20.19 20.48 22.6 20.19 20.48 Ana. Cal. Error (ACE)ACE ACE Zero Cal Error 0.45% 0.00% 0.24%0.45% 0.00% 0.24%0.45% 0.00% 0.24% Mid Cal Error -0.45%0.24%-0.14%-0.45%0.24%-0.14%-0.45%0.24%-0.14% High Cal Error 1.35%-1.08%-1.21%1.35%-1.08%-1.21%1.35%-1.08%-1.21% System Bias (zero, SB)SB SB Sys Zero Cal Bias Initial 0.45% 0.49% 0.82%-0.90% 0.00% 1.01%-0.45% 0.29% 1.16% Sys Zero Cal Bias Final -0.90%0.00%1.01%-0.45%0.29%1.16%-0.45%0.24%0.72% System Zero Drift (D)1.35%0.49%0.19%0.45%0.29%0.14%0.00%0.05%0.43% System Bias (upscale, SB)SB SB System Cal Bias Initial 0.00% -0.73% 0.77%-1.35% -1.71% -0.43%0.45% -1.62% -0.58% System Cal Bias Final -1.35%-1.71%-0.43%0.45%-1.62%-0.58%0.00%-1.47%-0.68% System Cal Drift (D)1.35%0.98%1.21%1.79%0.10%0.14%0.45%0.15%0.10% CGas = (Cavg - C0) • [Cma / (Cm - C0)]Eq. 7E-5 C0 = (C0i + C0f) / 2 Cm = (Cmi + Cmf) / 2 ACE = (CDir - Cv) • 100% / CS Eq. 7E-1 SB =(Cs - CDir) • 100% / CS Eq. 7E-2 Drift (D) =ABS(SBfinal - Sbinitial)Eq. 7E-4 STRATIFICATION CHECK FIELD SHEET Facility UMPA, Provo Power Plant Source Engine #4 Operator D Kitchen Date 1/10/2024 Time O2 %Time O2 %Time O2 % 12:05 9.89 12:10 9.85 12:15 9.83 12:06 9.86 12:11 9.87 12:16 9.89 12:07 9.85 12:12 9.83 12:17 9.90 12:08 9.76 12:13 9.35 12:18 9.88 12:09 9.81 12:14 9.80 12:19 9.92 Ave 9.83 9.74 9.88 3 Pt. Mean 9.82 9.82 9.82 % Diff From Mean 0.1 0.8 0.7 - The three sample points were on the east/west traverse line. -If the % diff from mean is less than 5%, one sample point may be used. Use the sample point that gave the value closest to the mean value. -If the % diff from mean is between 5% and 10%, use three sample points at 16.7, 50.0, and 83.3 % of diameter. -If the % diff from mean is greater than 10%, sample 12 points chosed according to EPA Method 1. Point 1 Point 2 Point 3 Caterpillar G3520H Engine 5 Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % 8:15 5.3 6.59 10.44 9:50 4.8 6.48 9.53 8:23 5.1 7.65 9.54 8:16 5.0 6.58 10.45 9:51 5.3 6.47 9.55 8:24 4.9 7.65 9.54 8:17 4.7 6.56 10.50 9:52 4.9 6.49 9.54 8:25 4.7 7.65 9.54 8:18 4.6 6.56 10.49 9:53 4.7 6.48 9.57 8:26 4.4 7.66 9.54 8:19 4.4 6.57 10.46 9:54 4.5 6.47 9.59 8:27 4.4 7.66 9.54 8:20 4.3 6.57 10.47 9:55 4.3 6.47 9.60 8:28 4.3 7.66 9.53 8:21 4.2 6.56 10.45 9:56 4.4 6.47 9.58 8:29 4.2 7.67 9.53 8:22 4.3 6.57 10.45 9:57 4.3 6.48 9.54 8:30 4.2 7.66 9.54 8:23 4.4 6.56 10.45 9:58 3.9 6.48 9.48 8:31 4.0 7.66 9.54 8:24 4.3 6.58 10.44 9:59 4.0 6.47 9.55 8:32 3.8 7.66 9.53 8:25 4.2 6.60 10.44 10:00 4.1 6.47 9.59 8:33 3.8 7.68 9.45 8:26 4.5 6.58 10.45 10:01 4.0 6.47 9.57 8:34 3.7 7.68 9.48 8:27 4.6 6.58 10.44 10:02 3.9 6.49 9.54 8:35 3.7 7.66 9.50 8:28 4.5 6.59 10.46 10:03 3.9 6.47 9.55 8:36 3.7 7.67 9.48 8:29 4.5 6.58 10.45 10:04 3.9 6.48 9.53 8:37 3.8 7.67 9.48 8:30 4.3 6.58 10.47 10:05 4.0 6.48 9.52 8:38 3.7 7.68 9.47 8:31 4.1 6.58 10.44 10:06 4.1 6.47 9.56 8:39 3.7 7.68 9.46 8:32 4.2 6.58 10.46 10:07 4.2 6.47 9.54 8:40 3.6 7.67 9.47 8:33 4.3 6.58 10.43 10:08 4.3 6.47 9.54 8:41 3.7 7.68 9.44 8:34 4.2 6.58 10.44 10:09 4.2 6.47 9.53 8:42 3.7 7.68 9.46 8:35 4.2 6.59 10.43 10:10 4.2 6.47 9.50 8:43 3.6 7.68 9.47 8:36 4.2 6.58 10.42 10:11 4.1 6.47 9.51 8:44 3.6 7.68 9.47 8:37 4.1 6.58 10.44 10:12 4.1 6.46 9.52 8:45 3.5 7.68 9.44 8:38 3.9 6.58 10.44 10:13 4.1 6.48 9.50 8:46 3.2 7.68 9.44 8:39 3.7 6.58 10.45 10:14 4.1 6.48 9.50 8:47 3.4 7.69 9.44 8:40 3.7 6.59 10.28 10:15 4.0 6.46 9.52 8:48 3.4 7.70 9.40 8:41 3.6 6.58 10.35 10:16 3.5 6.48 9.50 8:49 3.9 7.68 9.38 8:42 3.6 6.59 10.34 10:17 3.5 6.48 9.48 8:50 4.1 7.65 9.40 8:43 3.7 6.58 10.37 10:18 3.4 6.46 9.50 8:51 4.1 7.66 9.39 8:44 3.7 6.58 10.41 10:19 3.4 6.47 9.45 8:52 4.5 7.66 9.39 8:45 3.8 6.60 10.38 10:20 3.5 6.47 9.44 8:53 port change and sample 8:46 port change 10:21 3.6 6.48 9.44 11:12 line plugging problems 8:47 10:22 3.7 6.48 9.51 11:13 4.6 7.66 9.24 8:48 3.5 6.59 10.35 10:23 11:14 3.9 7.68 9.23 8:49 3.5 6.54 10.41 10:24 port change 11:15 3.4 7.67 9.23 8:50 2.9 6.12 11.24 10:25 11:16 3.0 7.66 9.23 8:51 3.4 6.56 10.47 10:26 6.5 6.45 9.58 11:17 2.8 7.66 9.22 8:52 6.1 6.59 10.40 10:27 7.5 6.46 9.56 11:18 2.7 7.65 9.22 8:53 6.9 6.59 10.39 10:28 7.7 6.46 9.58 11:19 2.5 7.67 9.22 8:54 6.5 6.60 10.37 10:29 7.5 6.46 9.54 11:20 2.5 7.67 9.22 8:55 6.0 6.60 10.37 10:30 7.5 6.47 9.51 11:21 2.4 7.67 9.21 8:56 5.6 6.59 10.40 10:31 7.4 6.46 9.54 11:22 2.3 7.65 9.21 8:57 5.5 6.61 10.37 10:32 7.4 6.46 9.55 11:23 2.3 7.67 9.21 8:58 5.4 6.59 10.41 10:33 7.4 6.48 9.50 11:24 2.3 7.67 9.17 8:59 5.4 6.60 10.37 10:34 7.5 6.46 9.52 11:25 2.3 7.65 9.16 9:00 5.5 6.60 10.35 10:35 7.3 6.46 9.54 11:26 2.4 7.66 9.18 9:01 5.4 6.60 10.37 10:36 7.0 6.47 9.54 11:27 2.4 7.65 9.20 9:02 5.3 6.60 10.36 10:37 6.6 6.47 9.54 11:28 2.4 7.67 9.19 9:03 5.2 6.60 10.37 10:38 6.6 6.46 9.56 11:29 2.3 7.66 9.18 9:04 5.1 6.61 10.36 10:39 6.5 6.47 9.58 11:30 2.3 7.65 9.20 9:05 5.2 6.60 10.39 10:40 6.5 6.46 9.60 11:31 2.3 7.66 9.19 9:06 5.0 6.61 10.38 10:41 6.6 6.47 9.60 11:32 2.3 7.65 9.18 9:07 5.2 6.59 10.25 10:42 6.5 6.47 9.61 11:33 2.2 7.67 9.15 9:08 5.2 6.61 10.21 10:43 6.6 6.46 9.62 11:34 2.1 7.65 9.16 9:09 5.1 6.60 10.41 10:44 6.6 6.47 9.62 11:35 2.1 7.65 9.16 9:10 5.2 6.61 10.41 10:45 5.8 6.46 9.61 11:36 2.2 7.67 9.14 9:11 5.1 6.59 10.46 10:46 5.2 6.47 9.59 11:37 2.1 7.65 9.15 9:12 5.1 6.60 10.43 10:47 5.0 6.46 9.60 11:38 2.2 7.65 9.16 9:13 4.9 6.61 10.43 10:48 5.0 6.48 9.59 11:39 2.1 7.64 9.16 9:14 4.9 6.60 10.42 10:49 5.0 6.46 9.60 11:40 2.0 7.65 9.15 9:15 4.6 6.61 10.44 10:50 5.1 6.46 9.62 11:41 2.0 7.66 9.14 9:16 4.4 6.60 10.47 10:51 5.1 6.46 9.61 11:42 2.0 7.64 9.15 9:17 4.2 6.61 10.45 10:52 5.0 6.47 9.62 11:43 2.1 7.64 9.15 9:18 4.0 6.61 10.44 10:53 5.1 6.46 9.60 9:19 3.8 6.62 10.45 9:20 3.9 6.61 10.46 Raw Avg 4.6 6.58 10.43 Raw Avg 5.1 6.47 9.55 Raw Avg 3.2 7.66 9.33 Run 3 (1/10/24)Run 2 (1/9/24)Run 1 (1/9/24) UMPA, PROVO POWER PLANT, ENGINE 5 (1/9-10/24) Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 %Time NOx ppm CO2 % O2 % Run 3 (1/10/24)Run 2 (1/9/24)Run 1 (1/9/24) UMPA, PROVO POWER PLANT, ENGINE 5 (1/9-10/24) Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Gas Val 11.2 9.75 9.77 Zeroi 0.0 0.00 -0.01 Zeroi 0.2 0.10 0.20 Zeroi 0.1 0.03 0.25 Zerof 0.2 0.10 0.20 Zerof -0.1 0.06 0.15 Zerof 0.0 0.18 0.24 Spani 11.0 9.69 9.68 Spani 10.9 9.57 9.88 Spani 11.1 9.79 9.82 Spanf 10.9 9.57 9.88 Spanf 10.9 9.56 9.69 Spanf 11.2 9.99 10.05 Corr.4.6 6.65 10.42 Corr.5.3 6.57 9.53 Corr.3.2 7.53 9.16 Calibration Calibration Calibration Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Span 22.3 20.41 20.73 Zero Cal Gas 0.0 0.00 0.00 0.0 0.00 0.00 0.0 0.00 0.00 Mid Cal Gas 11.2 9.75 9.77 11.2 9.75 9.77 11.2 9.75 9.77 High Cal Gas 22.3 20.41 20.73 22.3 20.41 20.73 22.3 20.41 20.73 Zero Resp 0.2 0.03 -0.01 0.2 0.03 -0.01 0.1 0.06 0.01 Mid Cal Resp 11.3 9.82 9.85 11.3 9.82 9.85 11.4 9.84 9.79 High Cal Resp 22.4 20.20 20.47 22.4 20.20 20.47 23.1 20.15 20.48 Ana. Cal. Error (ACE)ACE ACE Zero Cal Error 0.90% 0.15% -0.05%0.90% 0.15% -0.05%0.45% 0.29% 0.05% Mid Cal Error 0.45%0.34%0.39%0.45%0.34%0.39%0.90%0.44%0.10% High Cal Error 0.45%-1.03%-1.25%0.45%-1.03%-1.25%3.59%-1.27%-1.21% System Bias (zero, SB)SB SB Sys Zero Cal Bias Initial -0.90% -0.15% 0.00%0.00% 0.34% 1.01%0.00% -0.15% 1.16% Sys Zero Cal Bias Final 0.00%0.34%1.01%-1.35%0.15%0.77%-0.45%0.59%1.11% System Zero Drift (D)0.90%0.49%1.01%1.35%0.20%0.24%0.45%0.73%0.05% System Bias (upscale, SB)SB SB System Cal Bias Initial -1.35% -0.64% -0.82%-1.79% -1.22% 0.14%-1.35% -0.25% 0.14% System Cal Bias Final -1.79%-1.22%0.14%-1.79%-1.27%-0.77%-0.90%0.73%1.25% System Cal Drift (D)0.45%0.59%0.96%0.00%0.05%0.92%0.45%0.98%1.11% CGas = (Cavg - C0) • [Cma / (Cm - C0)]Eq. 7E-5 C0 = (C0i + C0f) / 2 Cm = (Cmi + Cmf) / 2 ACE = (CDir - Cv) • 100% / CS Eq. 7E-1 SB =(Cs - CDir) • 100% / CS Eq. 7E-2 Drift (D) =ABS(SBfinal - Sbinitial)Eq. 7E-4 STRATIFICATION CHECK FIELD SHEET Facility UMPA, Provo Power Plant Source Engine #5 Operator D Kitchen Date 1/9/2024 Time O2 %Time O2 %Time O2 % 7:45 9.61 7:50 9.62 7:55 9.65 7:46 9.61 7:51 9.64 7:56 9.63 7:47 9.64 7:52 9.59 7:57 9.65 7:48 9.61 7:53 9.60 7:58 9.65 7:49 9.60 7:54 9.64 7:59 9.61 Ave 9.61 9.62 9.64 3 Pt. Mean 9.62 9.62 9.62 % Diff From Mean 0.1 0.1 0.2 - The three sample points were on the east/west traverse line. -If the % diff from mean is less than 5%, one sample point may be used. Use the sample point that gave the value closest to the mean value. -If the % diff from mean is between 5% and 10%, use three sample points at 16.7, 50.0, and 83.3 % of diameter. -If the % diff from mean is greater than 10%, sample 12 points chosed according to EPA Method 1. Point 1 Point 2 Point 3 C APPENDIX C Laboratory Data and Chain of Custody Moisture Determination Sample Recovery D APPENDIX D Raw Production and Control Equipment Data Figure 1. Facility Schematic Representation (Caterpillar G3520H Engines 1-5) Recorded Engine Kw Output Facility: Stack Identification: ∅ Figure 1. Facility Schematic Representation Process Type: Control Unit Type:Natural Gas Engine 7000Estimated Velocity, fpm Selective Catalytic Reduction 2Number of Ports 21.75''∅: Stack Inside Diameter, inches 11Estimated Moisture, percent 700Estimated Temperature, oF UMPA, Provo Power Plant 13.5'β: Distance downstream from last disturbance, feet 30.0'γ: Distance of Sample Level to Ground, feet α: Distance upstream from next disturbance, feet 21.0' Caterpillar G3520H Engine α γ β E APPENDIX E Calibration Procedures and Results Calibration of the console dry gas meter(s), pitot tubes, nozzle diameters, and temperature sensors were carried out in accordance with the procedures outlined in the Quality Assurance Handbook. The appropriate calibration data are presented in the following pages. Figure 2. Schematic Representation of Method 4 Sampling Train Figure 3. Schematic of Gas Analyzer Sampling Train Meter Box Calibration Data and Calculations Forms Post-test Dry Gas Meter Calibration Data Forms Type S Pitot Tube Inspection Data Sample Box Temperature Sensor Calibration Calibration Gas Certifications NOx Converter Efficiency Check Figure 3. Schematic of Gas Analyzer Sampling Train. Mesh Filter Stack Wall Sample Probe Heated Sample Line Bias Valve Bias Line Sample Line Calibration Gases Calibration Gas Lines Analyzer Analyzer Analyzer Analyzer Flowmeters By-Pass Flowmeter Sample Exhaust Valve Valve Sampled Gas Manifold Exhaust Data Aquisition System Sample Pump Water Peristalic Pump Peltier Cooler TETCO Themocouple Meter Reading Calibration Date:1/19/2024 Calibrator:Reference:Omega CL3512A Temperature Temperature Source Sensor Difference (Medium)(oF)(oF) Water 33 0 Water 206 1 Water 33 0 Water 206 1 Water 33 0 Water 206 2 Water 33 0 Water 204 1 Water 33 0 Water 204 0 Water 33 0 Water 204 0 Water 33 0 Water 205 1 Water 32 1 Water 202 -2 Water 31 32 1 Water 204 202 -2 Water 33 32 -1 Water 204 202 -2 Water 31 32 1 Water 204 202 -2 Water 31 32 1 Water 204 202 -2 Water 31 32 1 Water 204 203 -1 Water 31 32 1 Water 204 203 -1 Water 32 1 Water 203 -1 Water 32 -1 Water 204 0 Water 33 32 -1 Water 204 203 -1 Water 33 32 -1 Water 204 203 -1 Water 33 33 0 Water 204 204 0 Water 33 31 -2 Water 204 203 -1 Water 31 -2 Water 203 -1 Water 31 -2 Water 204 0 Water 34 1 Water 205 0 Water 33 33 0 Water 205 205 0 Water 33 33 0 Water 205 204 -1 Water 33 34 1 Water 205 205 0 Water 33 33 0 Water 205 205 0 Water 33 0 Water 205 0 Water 35 2 Water 206 1 33 204 33 203 33 204 33 204 #4 2 3 4 5 6 7 205 33 205 7 4 5 6 2 3 4 204 31 204 5 33 1 33 205 1 2 3 4 204 #2 31 204 #3 1 2 3 Temperature 33 33 204 33 M. McNamara Thermocouple Meter ID Reference (oF) Dial Position #1 7 6 1 204 205 33 33 7 8 5 6 33 205 TETCO Themocouple Meter Reading Calibration Date:1/19/2024 Calibrator:Reference:Omega CL3512A Temperature Temperature Source Sensor Difference (Medium)(oF)(oF) Water 33 0 Water 204 0 Water 33 32 -1 Water 204 203 -1 Water 33 32 -1 Water 204 202 -2 Water 33 32 -1 Water 204 203 -1 Water 33 32 -1 Water 204 203 -1 Water 33 32 -1 Water 204 205 1 Water 33 0 Water 203 -10 Water 35 2 Water 202 -2 Water 33 35 2 Water 204 204 0 Water 33 34 1 Water 204 204 0 Water 33 33 0 Water 204 203 -1 Water 33 33 0 Water 204 202 -2 Water 33 33 0 Water 204 203 -1 Water 32 -1 Water 203 -1 Water 32 -1 Water 203 -1 Water 32 -1 Water 202 -2 Water 33 32 -1 Water 204 202 -2 Water 33 32 -1 Water 204 202 -2 Water 33 31 -2 Water 204 202 -2 Water 33 31 -2 Water 204 203 -1 Water 31 -2 Water 203 -1 Water 33 31 -2 Water 204 202 -2 Water 32 -1 Water 202 -2 Water 32 -1 Water 202 -2 Water 33 31 -2 Water 204 202 -2 Water 33 31 -2 Water 204 203 -1 Water 33 32 -1 Water 204 203 -1 Water 33 32 -1 Water 204 202 -2 Water 33 0 Water 202 -2 Water 33 0 Water 202 -2 4 3 5 2 6 204 204 33 204 33 33 204 #8 204 204 #7 1 33 204 #6 1 33 8 3 4 5 33 7 4 7 3 2 6 204 1 33 7 5 33 8 33 6 204 33 204 204 33 M. McNamara (oF) 7 5 4 3 2 1 #5 2 6 Thermocouple Meter ID Dial Position Temperature Reference TETCO Themocouple Meter Reading Calibration Water 33 0 Water 205 -1 Water 33 32 1 Water 204 205 -1 Water 33 32 1 Water 204 204 0 Water 33 31 2 Water 204 204 0 Water 33 31 2 Water 204 205 -1 Water 32 1 Water 206 -2 Water 33 33 0 Water 204 206 -2 Water 33 34 -1 Water 204 205 -1 Water 34 -1 Water 205 0 Probe Water 31 2 CONSOLE #6 Water 202 2 Oven Water 33 34 -1 Water 204 205 -1 Probe Water 31 2 #1 LINE Water 202 2 CONTROLLER Oven Water 33 32 1 Water 204 202 2 204 33 33 204 33 204 Shop Meter 1 33 204 2 3 4 7 8 9 33 205 5 6 Type S Pitot Tube Inspection Data Date:Pitot Tube Identification: Technician: Dt=0.244 Is PA = PB ? Is 1.05 • Dt  PA & PB  1.50 • Dt ? PA = 0.294 PB =0.294 a1 < 10o a1 = o a2 < 10o a2 = o b1 < 5o b1 = o b2 < 5o b2 = o Z  0.125 in.Z = in. W W  0.03125 in.W = in. W > 3 inches W = in. Z > 3/4 inch Z = in. Y ≥ 3 inches Y = in. The pitot tube meets the specifications for a calibration factor of 0.84?Yes Reference: TemperatureSource Reference Sensor (Medium)(oF)(oF) Probe AIR 70 71 AIR 70 71 ICE WATER 33 33 BOIL WATER 203 203 SILICONE OIL 1/3/2024 36 S X. Dang in. 0.041 2 0 2 2 1 in. in. Yes Yes 0.021 8 1 3 7/8 Heat Check 248 Temperature Sensor Calibration 1 0 0Stack Omega CL3512A Probe Yes Yes Continuity Check Temperature TemperatureDifference (oF) b2 b1 B A w Dt PA PB METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES 1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range. 2) Record barometric pressure before and after calibration procedure. 3) Run at tested vacuum (from Orifice Calibration Report), for a period of time necessary to achieve a minimum total volume of 5 cubic feet. 4) Record data and information in the GREEN cells, YELLOW cells are calculated. TECHNICIAN:INITIAL FINAL AVG (Pbar) DATE:1/24/2024 METER SERIAL #: 68092 BAROMETRIC PRESSURE (in Hg): 25.50 25.50 25.50 IF Y VARIATION EXCEEDS 2.00%, METER PART #: Console 6 CRITICAL ORIFICE SET SERIAL #: 1453S EQUIPMENT ID #:ORIFICE SHOULD BE RECALIBRATED K' TESTED TEMPERATURES °F ELAPSED FACTOR VACUUM DGM READINGS (FT3)AMBIENT DGM INLET DGM OUTLET DGM TIME (MIN)DGM DH (1)(2)(3)Y ORIFICE # RUN # (AVG) (in Hg)INITIAL FINAL NET (Vm)INITIAL FINAL INITIAL FINAL AVG q (in H2O) Vm (STD) Vcr (STD)Y VARIATION (%)DH@ 1 0.5317 15 57.755 71.235 13.480 68 64 72 64 91 72.8 19.25 1.20 11.4277 11.3618 0.994 1.643 2 0.5317 15 71.235 79.086 7.851 71 72 79 91 101 85.8 11.00 1.20 6.4971 6.4741 0.996 1.613 3 0.5317 15 79.086 87.740 8.654 73 79 80 101 110 92.5 12.000 1.20 7.0740 7.0494 0.997 1.599 AVG = 0.996 0.00 1 2 3 AVG = 1 2 3 AVG = AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = 0.996 AVERAGE DH@ = 1.618 (1)=Net volume of gas sample passed through DGM, corrected to standard conditions K1 =17.64 oR/in. Hg (English), 0.3858 oK/mm Hg (Metric) Tm =Absolute DGM avg. temperature (oR - English, oK - Metric) DH@ = 0.75 q DH Vm(std) Vcr(std) Vm (2)=Volume of gas sample passed through the critical orifice, corrected to standard conditions Tamb =Absolute ambient temperature (oR - English, oK - Metric) K' = Average K' factor from Critical Orifice Calibration REFERENCE IN OUT (3)=DGM calibration factor 68 67 68 32 33 33 TEMPERATURE SENSORS oF Post Calibration UMPA Provo Facility Caterpillar G3520H Engines 1-5 X Dang Console #6 19 ENVIRONMENTAL SUPPLY COMPANY USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS: The following equations are used to calculate the standard volumes of air passed through the DGM, Vm (std), and the critical orifice, V cr (std), and the DGM calibration factor, Y. These equations are automatically calculated in the spreadsheet above. ()2 () METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES 1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range. 2) Record barometric pressure before and after calibration procedure. 3) Run at tested vacuum (from Orifice Calibration Report), for a period of time necessary to achieve a minimum total volume of 5 cubic feet. 4) Record data and information in the GREEN cells, YELLOW cells are calculated. TECHNICIAN:INITIAL FINAL AVG (Pbar) DATE: 12/7/2023 METER SERIAL #: 68092 BAROMETRIC PRESSURE (in Hg): 25.65 25.65 25.65 IF Y VARIATION EXCEEDS 2.00%, METER PART #: Console 6 CRITICAL ORIFICE SET SERIAL #: 1453S EQUIPMENT ID #:ORIFICE SHOULD BE RECALIBRATED K' TESTED TEMPERATURES °F ELAPSED FACTOR VACUUM DGM READINGS (FT3)AMBIENT DGM INLET DGM OUTLET DGM TIME (MIN)DGM DH (1)(2)(3)Y ORIFICE # RUN # (AVG) (in Hg)INITIAL FINAL NET (Vm)INITIAL FINAL INITIAL FINAL AVG q (in H2O)Vm (STD)Vcr (STD)Y VARIATION (%)DH@ 1 0.8137 10 204.981 213.255 8.274 71 71 84 69 71 73.8 7.75 2.90 7.0764 7.0215 0.992 1.700 2 0.8137 10 213.255 221.823 8.568 71 82 88 70 72 78.0 8.00 2.90 7.2699 7.2481 0.997 1.686 3 0.8137 10 221.823 226.926 5.103 71 86 88 72 72 79.5 4.75 2.90 4.3178 4.3035 0.997 1.682 AVG = 0.995 0.11 1 0.5317 11 184.867 190.097 5.230 69 72 80 69 71 73.0 7.50 1.20 4.4576 4.4485 0.998 1.635 2 0.5317 11 190.097 196.569 6.472 65 78 82 70 71 75.3 9.25 1.20 5.4930 5.5074 1.003 1.616 3 0.5317 11 196.569 204.797 8.228 65 79 84 70 72 76.3 11.75 1.20 6.9704 6.9959 1.004 1.613 AVG = 1.001 0.72 1 0.3307 13 227.035 233.113 6.078 72 83 80 72 72 76.8 13.75 0.43 5.1329 5.0582 0.985 1.509 2 0.3307 13 233.113 240.071 6.958 72 78 79 71 71 74.8 15.75 0.43 5.8980 5.7939 0.982 1.515 3 0.3307 13 240.071 245.134 5.063 72 78 89 71 71 77.3 11.50 0.43 4.2717 4.2305 0.990 1.508 AVG = 0.986 -0.83 AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = 0.994 AVERAGE DH@ = 1.607 (1)=Net volume of gas sample passed through DGM, corrected to standard conditions K1 =17.64 oR/in. Hg (English), 0.3858 oK/mm Hg (Metric) Tm =Absolute DGM avg. temperature (oR - English, oK - Metric) DH@ = 0.75 q DH Vm(std) Vcr(std) Vm (2)=Volume of gas sample passed through the critical orifice, corrected to standard conditions Tamb =Absolute ambient temperature (oR - English, oK - Metric) K' = Average K' factor from Critical Orifice Calibration REFERENCE IN OUT (3)=DGM calibration factor 32 33 32 72 73 73 203 203 202 TEMPERATURE SENSORS oF 2024 Pre-Calibration Console #6 30 19 12 R Kitchen ENVIRONMENTAL SUPPLY COMPANY USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS: The following equations are used to calculate the standard volumes of air passed through the DGM, Vm (std), and the critical orifice, Vcr (std), and the DGM calibration factor, Y. These equations are automatically calculated in the spreadsheet above. ()2 () Date:1/2/23 Calibrator:Reference: Temperature Temperature Source Difference (Medium)(oF) Water 0 Water -2 Water 0 Water -2 Water 0 Water -1 Water 0 Water -2 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water -1 Water 0 Water -1 Water 0 Water 0 Water 0 Water 0 Water 0 Water -1 Water 0 Water -1 Water 0 Water 0 Water 1 Water 0 Water 0 Water -2 Water 0 Water -1 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 D E Oven 33 33 203 202F Oven (4) Oven (3) Oven (4) TETCO Sample Box Temperature Sensor Calibration B C 203 203 33 33 33 33 203 33 33 Xuan N. Dang Omega CL3512A Unit ID Reference (oF) Sensor (oF) Temperature 33 203 33 33 203Impinger Out B Impinger Out C 33 33 203 202 202 Impinger Out A 33 33 203 Impinger Out D 33 33 203 203 Impinger Out E 33 34 203 203 Impinger Out F 33 33 203 203 203 203 202 203 203 33 33 Impinger Out G 203 201 Oven (3)33 203 203 33 33 203Oven (4) 203 A 201203 33 Oven (3)33 33 Oven (4) Thermocouple Location 203 201 201 33 G H Oven (3)33 33 203 203 Oven (4)33 203 Oven 33 33 203 203 Oven 33 33 33 203 202 Oven (3) 202 33 33 Impinger Out K 33 33 203 203 33 33 Impinger Out J Impinger Out H Impinger Out I 33 203 33 203 33 203 33 203 203 F APPENDIX F Related Correspondence The testing protocol and other correspondence related to the tests are included here. 1 COMPLIANCE NOX EMISSION TESTING PROTOCOL FOR THE UTAH MUNICIPAL POWER AGENCY (UMPA) PROVO POWER PLANT CATERPILLAR G3520H ENGINES Project Organization and Responsibility The following personnel and the testing contractor are presently anticipated to be involved in the testing program. The Utah Division of Air Quality (DAQ) may have their own personnel to observe all phases including the process. Company: Contacts: Utah Municipal Power Agency (UMPA) Kevin Garlick 801 798-7489 696 W 100 S Tom Sorrels 801 798-7489 Spanish Fork, UT 84660 Provo Power Plant 702 North 300 West Provo, UT 84601 Test Contractor: Dean Kitchen 801-492-9106 TETCO 391 East 620 South American Fork, Utah 84003 Facility Location and Description Utah Municipal Power Agency (UMPA) operates a power generating facility in Provo, Utah. The plant operates five (5) Caterpillar G3520H 2547 kW natural gas-fired engines equipped with a combination of SCR and oxidation catalyst to control emissions. Test Objective The purpose of this test project is to demonstrate compliance with the NOx emission limits for the Caterpiller engines as required in the facilities Approval Order, DAQE-AN107950015-16, section II.B.1.c.1 which requires testing of the engines once every three (3) years. Test results will be reported in terms of grams per horsepower-hour (g/hp-hr) and/or pounds per hour (lb/hr). Testing will be conducted according to the principals of EPA Methods 1-4, and 7E. 2 Test Schedule It is planned to complete all testing the week of January 8, 2024. More than one engine may be tested each day testing occurs. If necessary, a pretest meeting may be scheduled by DAQ or UMPA. Operational Data and Instrumentation Each test will be conducted within 10 percent of 100 percent of the highest achievable load. The kilowatts produced by each engine will be recorded at least once every 15 minutes during each test run. Any additional, pertinent process data will be made available to DAQ personnel. Test Procedures Three test runs will be completed on each engine. The duration of each test run will be at least 60-minutes. Stack testing will be EPA Methods 1-4 and 7E as specified in 40 CFR 60, Appendix A. Specific procedures are as follows: EPA Methods 1-4 1. The configuration and dimensions of each stack are identical. The inside diameters are 21.75 inches. The sample ports are located 252 inches downstream and 162 inches upstream from any flow disturbance and meet the requirements of EPA Method 1 for undisturbed flow. The total number of sample points will be based on Method 1 for a nonparticulate traverse. 2. EPA Method 2 will be used to determine the gas stream velocity. Type S pitot tubes will be used with a Cp factor of 0.84. A dual inclined/vertical manometer with graduations of 0.01 inches of water will be used. If the measured pressure differential is below 0.05 inches of water a more sensitive manometer will be used with graduation marks of 0.005 inches of water. Previous testing has verified the absence of cyclonic flow and there have not been any configurational changes to the ducting that would increase any cyclonic flow; therefore, cyclonic flow measurement should not be required for this testing project. 3. EPA Method 3 or 3A will be used to determine the gas stream dry molecular weight. For Method 3, an integrated flue gas sample will be taken from the exhaust line after the dry gas meter orifice during each test run and analyzed at the completion of the test with an Orsat to determine the molecular weight of the effluent gas stream. 3 4. EPA Method 4 will be followed to determine the gas stream moisture content. The dry gas meter (DGM) sample volume will be sufficient to sample at least 21 dscf per test run. 5. Probe liners will be 316 stainless steel. 6. The barometric pressure will be measured with a barometer which is periodically checked against a mercury barometer. The barometer will be checked prior to testing to assure an accurate barometric pressure. 7. Calibration data is provided with this protocol in the Appendix. Equipment calibrations that fall past due prior to the test dates will be recalibrated prior to being used. Any calibration not included with this protocol, such as new or additional equipment, will be made available to DAQ representatives upon request. 8. If maintenance or operating problems arise during the test, the test may be stopped. This determination will be made by UMPA representatives and operating personnel in consultation with agency representatives. 9. Any necessary preparation and clean-up by the contractor will be performed in the contractor's sampling trailer or a clean area on UMPA=s property. The laboratory work and analysis will be done by the contractor as soon as possible after all tests have been completed. Gaseous Analyzer Measurements A gaseous analyzer will be used to measure the NOx concentrations simultaneously with EPA Methods 1-4. It is planned to run the NOx machine on the 0-25, or 0-50 ppm range. EPA Protocol 1 gases will be used as calibration standards with dry nitrogen as a zero gas. Bias checks, calibration drift, zero drift and calibration error will follow the specified guidelines of EPA Method 7E. Interference responses were determined in the factory and no alterations have been done, therefore, factory specifications are satisfactory. The average NOx ppm level will be corrected according to equation 7E-5. The gas analyzer sampling train will consist of the following: an in-stack glass fiber filter, heated stainless-steel probe, Teflon heated sampling line to the water removal system, water removal system, Teflon transport lines, gas manifold, and out of stack Teflon filter after the gas manifold but prior to analyzer. The sampling train is built such that the sampled gas only contacts inert materials, i.e., Teflon, stainless steel, and glass. A data logger will be used to provide a recorded gas concentration measurement. Gas analyzer data taken between port changes will be discarded; this allows for moving of the gas analyzer probe to allow the flows and moisture test probe to have undisturbed access to all ports. 4 Potential Hazards Moving Equipment No Hot Equipment Yes Chemical No Other Noise Test Area The test area shall include the engine room, control room, stack and associated areas, and the area around the contractor=s testing trailer for preparation and clean-up. Quality Assurance All testing and analysis in these compliance tests will be conducted according to Methods 1-4, and 7E and appropriate sections of the EPA Quality Assurance Handbook for Air Pollution Measurement Systems Volume III. Reporting Complete copies of raw data, calculations and summary of the test will be included in the test report. All process and production data will be recorded and retained for inspection and copying by DAQ. Preliminary verbal results will be reported to UMPA on site. The written reports will be submitted to DAQ within 30 days following completion of the tests. 5 Appendix ME T H O D 5 D R Y G A S M E T E R C A L I B R A T I O N U S I N G C R I T I C A L O R I F I C E S 1) Se l e c t t h r e e c r i t i c a l o r i f i c e s t o c a l i b r a t e t h e d r y g a s m e t e r w h i c h b r a c k e t t h e e x p e c t e d o p e r a t i n g r a n g e . 2) Re c o r d b a r o m e t r i c p r e s s u r e b e f o r e a n d a f t e r c a l i b r a t i o n p r o c e d u r e . 3) Ru n a t t e s t e d v a c u u m ( f r o m O r i f i c e C a l i b r a t i o n R e p o r t ) , f o r a p e r i o d o f t i m e ne c e s s a r y t o a c h i e v e a m i n i m u m t o t a l v o l u m e o f 5 c u b i c f e e t . 4) Re c o r d d a t a a n d i n f o r m a t i o n i n t h e GR E E N c e l l s , Y E L L O W c e l l s a r e c a l c u l a t e d . TE C H N I C I A N : IN I T I A L FI N A L AV G ( P ba r ) DA T E : 12 / 1 4 / 2 0 2 2 ME T E R S E R I A L # : 27 8 6 3 BA R O M E T R I C P R E S S U R E ( i n H g ) : 25 . 5 0 25 . 5 0 25 . 5 0 IF Y V A R I A T I O N E X C E E D S 2 . 0 0 % , ME T E R P A R T # : Co n s o l e 4 CR I T I C A L O R I F I C E S E T S E R I A L # : 14 5 3 S EQ U I P M E N T I D # : OR I F I C E S H O U L D B E R E C A L I B R A T E D K' TE S T E D TE M P E R A T U R E S ° F EL A P S E D FA C T O R VA C U U M DG M R E A D I N G S ( F T 3) AM B I E N T DG M I N L E T DG M O U T L E T DG M TI M E ( M I N ) DG M DH (1 ) (2 ) (3 ) Y OR I F I C E # RU N # (A V G ) (i n H g ) IN I T I A L FI N A L NE T ( V m) IN I T I A L FI N A L IN I T I A L FI N A L AV G q (i n H 2O) Vm ( S T D ) Vcr ( S T D ) Y VA R I A T I O N ( % ) DH@ 1 0. 8 1 3 7 11 64 . 8 4 5 69 . 9 1 1 5. 0 6 6 73 77 81 74 74 76 . 5 4. 7 5 2. 7 0 4. 2 8 3 1 4. 2 7 0 3 0. 9 9 7 1. 5 8 9 2 0. 8 1 3 7 11 69 . 9 1 1 74 . 9 8 5 5. 0 7 4 73 80 82 73 73 77 . 0 4. 7 5 2. 7 0 4. 2 8 5 8 4. 2 7 0 3 0. 9 9 6 1. 5 8 7 3 0. 8 1 3 7 11 74 . 9 8 5 80 . 0 3 6 5. 0 5 1 73 79 83 73 74 77 . 3 4. 7 5 2. 7 0 4. 2 6 4 4 4. 2 7 0 3 1. 0 0 1 1. 5 8 6 AV G = 0. 9 9 8 -0 . 2 8 1 0. 5 3 1 7 13 49 . 2 0 5 54 . 2 7 2 5. 0 6 7 70 75 76 71 71 73 . 3 7. 2 5 1. 2 0 4. 2 9 1 5 4. 2 7 1 0 0. 9 9 5 1. 6 4 7 2 0. 5 3 1 7 13 54 . 2 7 2 59 . 3 1 2 5. 0 4 0 70 75 79 71 73 74 . 5 7. 2 5 1. 2 0 4. 2 5 8 7 4. 2 7 1 0 1. 0 0 3 1. 6 4 3 3 0. 5 3 1 7 13 59 . 3 1 2 64 . 7 3 6 5. 4 2 4 70 79 79 74 74 76 . 5 7. 7 5 1. 2 0 4. 5 6 6 0 4. 5 6 5 6 1. 0 0 0 1. 6 3 7 AV G = 0. 9 9 9 -0 . 1 8 1 0. 3 3 0 7 13 80 . 0 7 6 85 . 1 4 7 5. 0 7 1 73 80 78 74 75 76 . 8 11 . 7 5 0. 4 2 4. 2 5 7 3 4. 2 9 3 1 1. 0 0 8 1. 4 8 6 2 0. 3 3 0 7 13 85 . 1 4 7 90 . 2 1 4 5. 0 6 7 73 78 77 75 74 76 . 0 11 . 7 5 0. 4 2 4. 2 5 9 9 4. 2 9 3 1 1. 0 0 8 1. 4 8 8 3 0. 3 3 0 7 13 90 . 2 1 4 95 . 3 0 9 5. 0 9 5 73 76 77 74 74 75 . 3 11 . 7 5 0. 4 2 4. 2 8 9 5 4. 2 9 3 1 1. 0 0 1 1. 4 9 0 AV G = 1. 0 0 6 0. 4 6 AV E R A G E D R Y G A S M E T E R C A L I B R A T I O N F A C T O R , Y = 1. 0 0 1 AV E R A G E DH@ = 1. 5 7 3 (1 ) = Ne t v o l u m e o f g a s s a m p l e p a s s e d t h r o u g h D G M , c o r r e c t e d t o s t a n d a r d c o n d i t i o n s K1 = 17 . 6 4 oR/ i n . H g ( E n g l i s h ) , 0 . 3 8 5 8 oK/ m m H g ( M e t r i c ) Tm = Ab s o l u t e D G M a v g . t e m p e r a t u r e ( oR - E n g l i s h , o K - M e t r i c ) DH@ = 0. 7 5 q DH V m(s t d ) Vcr (s t d ) V m (2 ) = Vo l u m e o f g a s s a m p l e p a s s e d t h r o u g h t h e c r i t i c a l o r i f i c e , c o r r e c t e d t o s t a n d a r d c o n d i t i o n s Tam b = Ab s o l u t e a m b i e n t t e m p e r a t u r e ( oR - E n g l i s h , o K - M e t r i c ) K' = Av e r a g e K ' f a c t o r f r o m C r i t i c a l O r i f i c e C a l i b r a t i o n RE F E R E N C E IN OU T (3 ) = DG M c a l i b r a t i o n f a c t o r 32 33 32 72 73 73 20 3 20 3 20 2 TE M P E R A T U R E S E N S O R S oF 20 2 3 P r e - C a l i b r a t i o n Co n s o l e # 4 30 19 12 R K i t c h e n EN V I R O N M E N T A L S U P P L Y C O M P A N Y US I N G T H E C R I T I C A L O R I F I C E S A S C A L I B R A T I O N S T A N D A R D S : Th e f o l l o w i n g e q u a t i o n s a r e u s e d t o c a l c u l a t e t h e s t a n d a r d v o l u m e s o f a i r p a s s e d t h r o u g h t h e D G M , V m (s t d ) , a n d t h e c r i t i c a l o r i f i c e , Vcr (s t d ) , a n d t h e D G M c a l i b r a t i o n f a c t o r , Y . T h e s e e q u a t i o n s a r e a u t o m a t i c a l l y c a l c u l a t e d i n t h e s p r e a d s h e e t a b o v e . ( )2 ( ) Type S Pitot Tube Inspection Data Date:Pitot Tube Identification: Technician: Dt=0.250 Is PA = PB ? Is 1.05 • Dt  PA & PB  1.50 • Dt ? PA = 0.302 PB =0.302 a1 < 10o a1 = o a2 < 10o a2 = o b1 < 5o b1 = o b2 < 5o b2 = o Z  0.125 in.Z = in. W W  0.03125 in.W = in. W > 3 inches W = in. Z > 3/4 inch Z = in. Y ≥ 3 inches Y = in. The pitot tube meets the specifications for a calibration factor of 0.84?Yes Reference: TemperatureSource Reference Sensor (Medium)(oF)(oF) Probe AIR 68 69 AIR 68 69 ICE WATER 33 34 BOIL WATER 204 204 SILICONE OIL 1/4/2023 36 S M. McNamara in. 0.029 2 0 2 2 1 in. in. Yes Yes 0.012 8 1 3 7/8 Heat Check 248 Temperature Sensor Calibration 1 1 0Stack Omega CL3512A Probe Yes Yes Continuity Check Temperature TemperatureDifference (oF) b2 b1 B A w Dt PA PB Date:1/5/23 Calibrator:Reference: Temperature Temperature Source Difference (Medium)(oF) Water 1 Water 1 Water 0 Water 1 Water 0 Water 0 Water 0 Water 0 Water 1 Water -1 Water -1 Water 0 Water -1 Water 0 Water -1 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 0 Water 1 Water -2 Water 0 Water -1 Water 0 Water 0 Water 1 Water -1 Water 1 Water 0 Water 0 Water 0 Water 1 Water -2 Water 0 Water -1 Water 0 Water -2 Water 0 Water -1 Water 0 Water -1 202 33 33 Impinger Out K 33 33 204 203 33 34 Impinger Out J Impinger Out H Impinger Out I 33 202 33 203 33 204 33 204 204 204 33 G H Oven (3)33 33 204 204 Oven (4)33 204 Oven 33 33 204 204 Oven 33 33 33 204 204 Oven (3) A 205204 33 Oven (3)33 34 Oven (4) Thermocouple Location 204 205 Impinger Out F 33 33 203 204 204 204 204 204 204 33 33 Impinger Out G 204 204 Oven (3)32 204 204 33 32 204Oven (4) 204 Impinger Out D 33 34 204 203 Impinger Out E 33 34 204 204 202 33 33 204Impinger Out B Impinger Out C 33 33 204 204 203 Impinger Out A 33 34 204 Oven (3) Oven (4) TETCO Sample Box Temperature Sensor Calibration B C 204 203 33 32 33 33 204 33 34 Mike McNamara Omega CL3512A Unit ID Reference (oF) Sensor (oF) Temperature 33 D E Oven 33 33 204 204F Oven (4) Airgas Specialty Gases Airgas USA, LLC an Air Liquide company 525 North Industrial Loop Road Tooele, UT 84074 Part Number: CERTIFICATE OF ANALYSIS Grade of Product: EPA Protocol E03Nl99E15A0PK1 Reference Number: Cylinder Number: CC495698 Cylinder Volume: Laboratory: 124 -Tooele (SAP) -UT Cylinder Pressure: PGVP Number: B72021 Valve Outlet: Gas Code: CO,NO,NOX,BALN. Certification Date: Expiration Date: Sep 15, 2024 Airgas.com 153-402210499-1 144.3 CF 2015 PSIG 660 Sep 15, 2021 Certification performed in accordance with "EPA Traceability Protocol for Assay and Certification of Gaseous Calibration Standards (May 2012)" document EPA 600/R-12/531, using the assay procedures listed. Analytical Methodology does not require correction for analytical interference. This cylinder has a total analytical uncertainty as stated below with a confidence level of 95%. There are no significant impurities which affect the use of this calibration mixture. All concentrations are on a mole/mole basis unless otherwise noted. D N t U Th' C I' d b I 100 . 0 7 0 0 se Is ;yin er eow PSIQ, I.e. . meQapascals. " -. .. '>-.,.. cccc ... --ANALITJCAI:;1IBSULT~'.: -"-"-------· ~---.::::~--~----:::-r--_--·-··--···-·· - Component , Requested Actual Protocol Total Relative Assay •• Concentration Concentration Method Uncertainty Dates NOX 4.500 PPM 4.668 PPM G1 +/-1.3% NIST Traceable 09/08/2021, 09/15/2021 CARBON MONOXIDE 4.500 PPM 4.385 PPM G1 +/-1.4% NIST Traceable 09/08/2021 NITRIC OXIDE 4.500 PPM 4.625 PPM G1 +/-1.2% NIST Traceable 09/08/2021, 09/15/2021 NITROGEN Balance CALIBRATION STANDARDS Type Lot ID Cylinder No Concentration Uncertainty Expiration Date NTRM 12062857 CC401933 9.82 PPM CARBON MONOXIDE/NITROGEN 1.0% Feb 12, 2024 PRM 12401 APEX1324267 5.00 PPM NITRIC OXIDE/NITROGEN 0.8% Dec 23, 2022 GMIS 08012126A KAL004291 5.08 PPM NITRIC OXIDE/NITROGEN 0.9% Apr27,2024 PRM 12401 APEX1324267-NOX 5.00 PPM NOx/NITROGEN 0.8% Dec 23, 2022 GMIS 08012126A KAL004291-NOX 5.08 PPM NOx/NITROGEN 0.9% Apr27,2024 The SRM, PRM or RGM noted above is only in reference to the GMIS used in the assay and not part of the analysis. ANALYTICAL EQUIPMENT Instrument/Make/Model Analytical Principle Last Multipoint Calibration Thermo 48i-TLE 1163640031 CO CO NDIR (Mason) Aug 17, 2021 Thermo 42i-LS 1123749327 NO Chemiluminescence (Mason) Aug 30, 2021 Thermo 42i-LS 1123749327 NOx Chemiluminescence (Mason) Aug 30, 2021 Triad Data Available Upon Request Page 1 of 153-402210499-1 as. an Air Liquide company CERTIFICATE OF ANALYSIS Grade of Product: EPA Protocol Part Number: E03Nl99E15A3631 Reference Number: Cylinder Number: EB0141000 Cylinder Volume: Laboratory: 124 -Tooele (SAP) -UT Cylinder Pressure: PGVP Number: 872021 Valve Outlet: Gas Code: CO,NO,NOX,BALN Certification Date: Expiration Date: Sep 14, 2024 Airgas Specialty Gases Airgas l,JSA, LLC 525 North Industrial Loop Road Tooele, UT 84074 Airgas.com 153-402211480-1 144.3 CF 2015 PSIG 660 Sep 14, 2021 Certification performed in accordance with "EPA Traceability Protocol for Assay and Certification of Gaseous Calibration Standards (May 2012)" document EPA 600/R-12/531, using the assay procedures listed. Analytical Methodology does not require correction for analytical interference. This cylinder has a total analytical uncertainty as stated below with a confidence level of 95%. There are no significant impurities which affect the use of this calibration mixture. All concentrations are on a mole/mole basis unless otherwise noted. C d b 1 Do Not Use This ;vlin er elow 00 osiq, i.e. 0.7 meqaoascals. ANALYTICAL RESULTS ···componem ,.t·--C•1wqffirsteu=~~Actua1 ·,·ProTocol . Total Relalive ------Ks~~~---~ Concentration Concentration Method Uncertainty Dates NOX 11.00 PPM 11.15 PPM G1 +/-1.2% NIST Traceable 09/07/2021, 09/14/2021 CARBON MONOXIDE 11.00 PPM 11.20 PPM G1 +/-1.2% NIST Traceable 09/07/2021 NITRIC OXIDE 11.00 PPM 11.12 PPM G1 +/-1.3% NIST Traceable 09/07/2021, 09/14/2021 NITROGEN Balance CALIBRATION STANDARDS Type Lot ID Cylinder No Concentration Uncertainty Expiration Date NTRM 12062857 CC401933 9.82 PPM CARBON MONOXIDE/NITROGEN 1.0% Feb 12, 2024 NTRM 12010210 AAL073499 10.04 PPM NITRIC OXIDE/NITROGEN 1.0% Oct 16, 2022 NTRM 12010507 KAL004854 20.00 PPM NITRIC OXIDE/NITROGEN 1.1% Feb 13, 2024 NTRM. 12010507 KAL004854-NOX 20.00 PPM NOx/NITROGEN 1.1% Feb 13, 2024 NTRM 12010210 AAL073499-NOX 10.04 PPM NOx/NITROGEN 1.0% Oct 16, 2022 ANALYTICAL EQUIPMENT Instrument/Make/Model Analytical Principle· Last Multipoint Calibration Thermo 48i-TLE 1163640031 CO CO NDIR (Mason) Aug 17, 2021 Thermo 42i-LS 11237 49327 NO Chemiluminescence (Mason) Aug qO, 2021 Thermo 42i-LS 1123749327 NOx Chemiluminescence (Mason) Aug 3Q, 2021 Triad Data Available Upon Request ~~ Page 1 of 153-402211480-1 . Making our world more productive DocNumber: 488688 Certificaw /ssuan~e Date: 07/28/2022 Linde Order Number: 72093085 Linde Gas & Equipment Inc. 5700 S. Alameda Street Los Angeles CA 90058 Tel: 323-585-2154 Fax: 714-542-6689 PGVP ID: F22022 Fill Date: 07/06/2022 Lot Number: 70086218703 Customer & Order Information LGEPKG SALT LAKE CITY UT H 6880 S 2300 E Part Number: NI C022.5MN2EAS Customer PO 'Number: 80096754 Cylinder Style & Outlet: AS CGA 660 SALT LAKE CITY UT84121-3183 I Cylinder Pressure and Volume: 2000 psig 140 ft3 Expiration Date: Cylinder Number: For Reference Only: 22.3 ppm 22.3 ppm Balance NOx 22.4ppm Certified Concentration 07/28/2025 CC3394 Carbon monoxide· Nitric oxide Nitrogen NIST Traceable Expanded Uncertainty ± 0.1 ppm ±0.2 ppm Certification Inf(Jrmation: Cerlification Date:07/28/2022 Term: 36 Months Expiration Date: 07/28/2025 ~- This cylinder was certified according to the 2012 EPA Traceability Protocol, Document#EPA-600/R-12/531, using Procedure G1. Uncertainty above is expressed as absolute expanded uncertainty at a level of confidence of approximately 95% with a coverage factor k = 2. Do Not'Use this Standard if Pressure is less than 100 PSIG. Analvtical Data: (R=Reference Standard, Z=Zero Gas, C=Gas CanciiJ~te) 1. Component: Carbon monoxide RequesteaConcentration: 22.5 ppm Certified Concentration: Instrument Used: Analytical Metl)~d:. · 22.3 ppm Horiba VIA-510 S/N 43627990042 NDIR Last Multipoint Calibratioh:' 06/27/2022 Reference Standard: Type/ Cylinder#: GMIS / CC707385 Concentration/ Uncertainty: 24.51 ppm ±0.04 ppm Expiration Date: 10/09/2027 Traceable to: SRM #/Sample# / Cylinder#: SRM 2635a / 58-E-34 / FF10666 SRM Concentration/ Uncertainty: 24.512 ppm/ ±0.029 ppm SRM Expiration Date: 03/28/2021 First Analysis Data: ;,,c"•t'·~,,~;·· 24.5 ~:~_c: ... ,.>c-.o~~~__'.l~,: •. ;=•,S~,:2,.:~1J.ndAn~,Y-~ta: _,_ .... ~ , .... J>ate'--•. ~ .. -... C: 22.3 Cone: 22.3 Z: O R: O C: · O Cone: 0 2. R: 24.6 Z: 0 Z: 0 C: 22.4 UOM: ppm Component: Nitric oxide Requested Coqcentration: 22.5 ppm Certified Concentration: 22.3 ppm C: 22.4 Cone: 22.4 R: o Z: O C: o Cone: 0 R: 24.5 Cone: 22.4 Z: o C: O R: o Cone: 0 Mean Test Assay: 22.3 ppm UOM: ppm Mean Test Assay: Reference Standard: Type/ Cylinder#: GMIS / DT0037183 Concentration I Uncertainty: 19.97 ppm ±0.20 ppm Expiration Date: 04/1212025 Instrument Used: . , Thermo Electron 42i-LS SIN 1030645077 Traceable to: SRM #/Sample#/ Cylinder#: 2629a / 50-G-17 / FF31691 Analytical Method: Chemiluminescence Last Multipoint Calibration: 06/28/2022 SRM Concentration I Uncertainty: 18.99 ppm /±0.19 ppm SRM Expiration Date: 10/21/2023 ppm First Analysis Data: Date 07/14/2022 Second Analysis Data: Date 07/28/2022 Z: 0 R: 20 C: 22.3 Cone: 22.3 Z: 0 R: 20 C: 22.3 Cone: 22.2 R: 20 Z: 0 C: 22.4 Cone: 22.4 R: 20 Z: 0 C: 22.3 Cone: 22.2 Z: 0 C: 22.2 R: 20 Cone: 22.2 Z: 0 C: 22.3 R: 20.1 Cone: 22.2 UOM: ppm Mean Test Assay: 22.3 ppm UOM: Mean Test Assay: 22.2 ppm Analyzed By Henry Koung Information contained herein has been prepared at your request by qualified experts within Linde Gas & Equipment Inc. While we believe that the information is accurate within the limits of the analytical methods employed and Is complete to the extent of the specific analyses performed, we 'make no warranty or representation as to the suitability of the use of the Information for any purpose, The information is offered with the understanding that any use of the information is at the sole discretion and risk of the user. In no event shall the liability of Linde Gas & Equipment Inc. , arising out of the use of the information contained herein exceed the fee established for providing such information.