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HomeMy WebLinkAboutDAQ-2024-0119071 DAQC-1202-24 Site ID 12825 (B5) MEMORANDUM TO: CEM FILE – UTAH ASSOCIATED MUNICIPAL POWER SYSTEMS (UAMPS) – Nebo Power Generating Station THROUGH: Harold Burge, Major Source Compliance Section Manager FROM: Rob Leishman, Environmental Scientist DATE: December 4, 2024 SUBJECT: Source: Nebo Generating Facility Natural Gas Turbine Generator (EU#2) Contact: Dave Gammell (Plant Manager) – 801-925-4012 Cheyney Guymon – 801-794-2950 Location: 1265 Bamberger Road, Payson, Utah County, UT Test Contractor: Montrose Air Quality Services, LLC FRS ID#: UT0000004904900234 Permit/AO#: Title V operating permit 4900234004, dated January 18, 2022 Subject: Review of RA/PST Report dated June 26, 2024 On July 8, 2024, DAQ received a Relative Accuracy/Performance Specification Test (RA/PST) report for the Nebo Power EU#2 HRSG stack. Testing was performed on May 29, 2024, to determine the relative accuracy of the NOx, CO, and O2 monitoring systems. The DAQ-calculated test results are: RA/PST EVALUATION: HRSG Stack NSPS RATA - Test Date - 5/29/2024 Primary Channel Manufacturer Serial No. Units CEM Value RM Value Relative Accuracy Status NOx Thermo - 42ILS - ANSSPCA 1501663828 ppm @ 15% O2 4.504 4.551 4.0% Passed lbs/MMBtu 0.017 0.017 5.9% Passed O2 Thermo - 48I - AGPCA 1501663829 % 14.780 14.870 1.4% Passed CO Thermo - 48I - AGPCA 1501663829 ppm @ 15% O2 8.378 8.382 0.8% Passed Stack Test Deviation Report There were no deviations observed during testing. Calibration gases were in date and met performance specifications. DEVIATIONS: No deviations were noted in this report. CONCLUSION: UAMPS Nebo Power operates the continuous emissions monitor (CEM) on the EU#2 HRSG stack at the Nebo Power facility to measure NOx, CO, and O2 emissions. The CEM was audited by the DAQ and found to meet quality assurance requirements found in 40 CFR Part 60, Appendix B, Performance Specification 1, and R307-170, Continuous Emission Monitoring System Program. Quarterly cylinder gas audits and an annual relative accuracy test audit were conducted in accordance with the procedures outlined in UAC R307-170. 1 8 2 2 RECOMMENDATION: The UAMPS Nebo Power EU#2 CEM system was operating as required in R307-170 and 40 CFR 60.13 at the time of this evaluation. HPV: No ATTACHMENTS: RATA Review Spreadsheets. ,7 I I I I I t I I I I I I I I I I I I T ffi t2?25-6s I'TAH DEPAHTMENT OF EIURONMENTAL OTJAUTY JilL - p l-^i4 DIVISION OF AtR QUALIT June26,2024 Utah Deparknent of Environmental Quality Division of Air Quality Attn: Mr. Harold Burge, Compliance Section Manager 150 North 1950 West P.O. Box 144820 Salt Lake city, utah 84116-0690 Ref: EPA Compliance Test Report for RATA Tests Dear Mr. Burge: Utah Associated Municipal Power Systems (UAMPS) has submitted results from "EPA Compliance Testing for CEM RATA Tests." These tests were conducted on the NEBO GE Frame 7EAII{RSG Gas-Fired Turbine located in Payson, Utah on May 29,2024. This testing was conducted in accordance with Section II.B of our Title V Operating Permit (No. 4900234004). The results of the report show no deviations from permit conditions. Based on the information and belief formed after reasonable inquiry, the statements and information in the test report are true, accurate and complete. t/rc/r azq David Gammell Plant Manager UAMPS - Nebo Power Station Source Test Repoft for the 2(J24 Relative Accuracy Test Audit Utah Associated Municipal Power Systems (uAMPs) Nebo Power Generating Station GE Frame 7E AIHRSG Gas-Fired Turbine (EU #2) Payson, Utah Prepared For: UAMPS 155 North 400 West, Suite 480 Salt Lake City, Utah 84103 Prepared By: Montrose Air Quality Services, LLC 6823 South 3600 West Spanish Fork, Utah 84660 For Submission To: State of Utah DEQ, Division of Air Quality 195 North 1950 West Salt Lake City, UT 84116 Document Number: GPOS1AS-O39393-RT-1619 Test Date: May 29, 2024 Submittal Date: June 26, 2024 UTAH DEPAFTMENT OF E}WIRONMENTAL OUALITY JUL - I i:"24 DNflSION OF AIR OUAI.IT ENiOU*VcattrtrtlarM M9NT+PII STAE Review and Ceftification All work, calculations, and other activities and tasks performed and presented in this document were carried out by me or under my direction and supervision. I hereby certify that, to the best of my knowledge, Montrose operated in conformance with the requirements of the Montrose Quality Management System and ASTM D7036-04 during this test project. Signature: Date:June 26, 2024 Name: .! Cheyney Guymon Title:Client Project Manager I have reviewed, technically and editorially, details, calculations, results, conclusions, and other appropriate written materials contained herein. I hereby certify that, to the best of my knowledge, the presented material is authentic, accurate, and conforms to the requirements of the Montrose Quality Management System and ASTM D7O36-04. I I I T I T I T I I I t I I I I I Signature: Name: 'tLl..^ \\o-k-*",)une 26, 2024 Beckie Hawkins Date: Title:District Manager Facility Ceftification I have reviewed this document and agree that the information contained herein is true, accurate, and complete, to the best of my knowledge. Signature: Name: June 26, 2O24 Dave Gammell Title:Plant Manager 2of85 cP08 1AS-039393-RT- 16 19 -I I I -I I T I I t T I I I t T I I T T Table of Contents Section Paoe 1.0 Introduction........ ................5 1.1 Summary of Test Program .............5 L.2 Key Personnel........... ...................7 2.0 Plant and Sampling Location Descriptions.............. ..................9 2.t Process Description, Operation, and Control Equipment.........,.... .......9 2.2 CEMS Description .......10 2.3 Operating Conditions and Process Data .....,... 10 3.0 Sampling and Analytical Procedures .....11 3.1 Test Methods............ .................11 3.1.1 EPA Methods 3A,7E, and 10, Determination of Orygen, Nitrogen Oxides, and Carbon Monoxide Concentrations in Emissions from Stationary Sources (Instrumental Analyzer Procedure) ............. ......... tl 3.1.2 EPA Method 19, Determination of Nitrogen Oxide and Carbon Monoxide Emission Rates ..................12 4.0 Test Discussion and Results .................13 4.L Field Test Deviations and Exceptions.......... ...................13 4.2 Presentation of Resu1ts.............. ..................13 5.0 Internal QA/QC Activities ....18 s.1 QA/QC Audits....... ......18 5.2 QA/QC Discussion. ......18 5.3 Quality Statement ......18 List of Appendices Field Data and Calculations ........ ........19 A.1 Instrumental Test Method Data......... ..........20 A.2 Calculations/Results.. .................32 A.3 Example Calculations.......,..... .,..37 Facility CEMS Data ........ ....44 Quality Assurance/Quality Control .......55 C.1 Units and Abbreviations............ ..................56 C.2 Instrumental Test Method QA/QC Data......... ................64 C.3 Accreditation Information/Certifications..... ................... 83 B c 3of86 cP081AS-039393-RT- 1619 List of Tables 1-1 Summary of Test Program ........5 L-Z Summary of Part 60/75 RA Test Results - Nebo EU #2, Nlay 29,2024.......................6 1-3 Test Personnel and Observers. ..............8 L-4 Part75 Qualified Individual Information .................8 2-L CEMS Information .............10 4-l Oxygen (o/ovd) RATA Results - Nebo EU #2 ..........L4 4-2 Nitrogen Oxides (lb/MMBtu) MTA Results - Nebo EU #2....... .................15 4-3 Nitrogen Oxides RATA Results - Nebo EU #2 ........16 4-4 Carbon Monoxide RATA Results - Nebo EU #? .....,L7 5-1 Gas Cylinder Information............ .......18 List of Figures 3-1 US EPA Methods 3A,7E, and 10 Sampling Train........ ............L2 I I I I I I I T I I I T I I I I I I I4of86cPo8 1AS-039393-RT-1619 I T I I t 1.O Introduction 1.1 Summary of Test Program Utah Association of Municipal Power Systems (UAMPS) contracted Montrose Air Quality Serices, LLC (Montrose) to perform a CEMS RATA on the GE Frame 7EA w/HSRG Unit, natural gas-fired, combined-cycle, stationary, combustion turbine (identified as emission unit EU #2) at the Nebo Power Generating Station located in Payson, Utah. The tests were conducted to determine compliance with the applicable RA requirements listed in State of Utah Department of Environmental Quality (UDEQ), Division of Air Quality Title V Operating Permit No. 4900234004, dated January 18,2022,40 CFR 60 Appendix B and 40 CFR Part 75, Appendix A. The specific objectives were to: . Determine the M for the Oz, NOx and CO CEMS installed to monitor the emissions from Nebo EU #2 to meet annual requirements. . Conduct the test program with a focus on safety. Montrose performed the tests to measure the emission parameters listed in Table 1-1. Table 1-1 Summary of Test Program To simplify this report, a list of Units and Abbreviations is included in Appendix D.1. Throughout this repoft, chemical nomenclature, acronyms, and reporting units are not defined. Please refer to the list for specific details. This report presents the test results and supporting data, descriptions of the testing procedures, descriptions of the facility and sampling locations, and a summary of the quality assurance procedures used by Montrose. The M test results are summarized and compared to their respective regulatory requirements in Table 1-2. Detailed results for individual test runs can be found in Section 4.0. All supporting data can be found in the appendices. The testing was conducted by the Montrose personnel listed in Table 1-3. The tests were conducted according to the test plan (protocol) dated April 9, 2024 that was submitted to and approved by the UDEQ, Division of Air Quality. I I t I I t I I I I t t t T Perform Oz, NOx and CO MTAs EPA,34,7E, 10, 19 5of86 cPo8 1AS-039393-RT- 1519 Table 1-2 Summary of Part 611175 RA Test Results - Nebo EU #2,lilay 29, 2024 I I I I I I I I I I I t I I T I T I T Nitrogen Oxides (NOx) Carbon Monoxlde (CO) S 10olo of RM Oxygen (Oz) App. B Sect. 2.3.1.2 2,Oo/o or O.3o/o Oz 3 7,5o/o of RM or *0.5olo Oz Nltrogen Oxldes (NOx) App. B Sect. 2.3.1.2 8.73o/o or 0.0015 < 10% of RM or * 0.020 6of86 cPo8 1AS-039393-RT-1619 t I I I I I I I t t I I I I I I I t I L.2 Key Personnel A list of project pafticipants is included below: Facility Information Source Location: UAMPS Nebo Power Generating Station 1265 N. Bamberger Road Payson, Utah 84651 Project Contact: Dave Gammell Role: Plant Manager Company: UAMPS Telephone: 801-925-4012 Email: dgammell@uamps.com Agency Information Regulatory Agency: State of Utah DEQ, Division of Air Quality Agency Contact: Chad Gilgen, Minor Source Compliance Telephone: 385-306-5500 Email: cgilgen@utah.gov Testing Company Information Testing Firm: Montrose Air Quality Services, LLC Contact: Beckie Hawkins Cheyney Guymon Title: District Manager Client/Field Project Manager Telephone: 8OL-372-7O49 8OL-362-4978 Email: BeHawkins@montrose-env.com ChGuymon@montrose-env.com Test personnel and observers are summarized in Table 1-3. 7of86 cP08 1AS-039393-RT-1619 Table 1-3 Test Personne! and Observers Field Team Leader/Qualified Individual (Ql)fl-railer Operator Sample recovery/Sample train operator Calculations and report preparation Observer/Client liaisonfl-est coordinator Qualified individual information is presented in Table 1-4. Table 1-4 Paft 75 Qualified Individual Information Montrose Air Quali$ Services, LLC Group 3: 05/0312024 (Expiration Date: 05/02/2028) Source Evaluation Society qstiprogram@gmail.com I t I I I t t I I I I I t I I I I I I 2.O Plant and Sampling Location Descriptions 2.L Process Description, Operation, and Control Equipment Turbines are stationary, internal combustion engines that operate with rotary rather than reciprocating motion. Gas turbines are essentially composed of three major components: compressor, combustor, and power turbine. In the compressor section, ambient air is drawn in and compressed up to 30 times ambient pressure and directed to the combustor section where fuel is introduced, ignited, and burned. Combustors can either be annular, can-annular, or silo. An annular combustor is a doughnut-shaped, single, continuous chamber that encircles the turbine in a plane perpendicular to the aifflow. Can-annular combustors are like the annular; however, they incorporate several can-shaped combustion chambers rather than a single continuous chamber. Annular and can-annular combustors are based on aircraft turbine technology and are typically used for smaller scale applications. A silo (frame-type) combustor has one or more combustion chambers mounted external to the gas turbine body. Silo combustors are typically larger than annular or can- annular combustors and are used for larger scale applications. This GE Frame 7EAIHSRG (EU #2) is a combined-cycle gas turbine (CCGT) plant. The gas turbine generator generates electricity and the waste heat from the gas turbine is used to make steam to generate additional electricity via a steam turbine; this last step enhances the efficiency of electricity generation. Hot gases from the combustion section are diluted with additional air from the compressor section and directed to the power turbine section at temperatures up to 2600 degrees Fahrenheit. Energy from the hot exhaust gases, which expand in the power turbine section, are recovered in the form of shaft horsepower. More than 50 percent of the shaft horsepower is needed to drive the internal compressor and the balance of recovered shaft horsepower is available to drive an external load. Gas turbines may have one, two, or three shafts to transmit power between the inlet air compression turbine, the power turbine, and the exhaust turbine. The heat content of the exhaust gases exiting the turbine can either be discarded without heat recovery (simple rycle); recovered with a heat exchanger to preheat combustion air entering the combustor (regenerative cycle); recovered in a heat recovery steam generator to raise process steam, with or without supplementary firing (cogeneration); or recovered, with or without supplementary firing, to raise steam for a steam turbine Rankine cycle (combined cycle or repowering). The primary pollutants from gas turbine engines are nitrogen oxides (NOx), carbon monoxide (CO), and to a lesser extent, volatile organic compounds (VOC). Particulate matter (PM) is also a primary pollutant for gas turbines using liquid fuels. Nitrogen oxide formation is strongly dependent on the high temperatures developed in the combustor. Carbon monoxide, VOC, hazardous air pollutants (HAP), and PM are primarily the result of incomplete combustion. Trace to low amounts of HAP and sulfur dioxide (SOz) are emitted from gas turbines. Ash and metallic additives in the fuel may also contribute to PM in the exhaust. Oxides of sulfur (SOx) will only appear in a significant quantity if heavy oils are 9of85 cP081AS-039393-RT- 1 519 fired in the turbine. Emissions of sulfur compounds, mainly SOz, are directly related to the sulfur content of the fuel. 2.2 CEMS Description A continuous emissions monitoring system (CEMS) is installed on the EU #2 exhaust stack. The CEMS configurations include a diluent gas oxygen (Oz) analyzer, a nitrogen oxide (NOr) analyzer, a carbon monoxide (CO) analyzer, and a data acquisition and handling system (DAHS). The CEMS analyzers are presented in Table 2-1. Table 2-1 CEMS Information 2.3 Operating Conditions and Process Data Emission tests were performed while the source/unit and air pollution control devices were operating at the conditions required by 40 CFR Part 75 (i.e., entirely within the "normal" load range) and 40 CFR Part 60 (i.e., >50o/o of full load). The unit was tested when operating at 106 MW. Plant personnel were responsible for establishing the test conditions and collecting all applicable unit-operating data. The CEMS and process data that was provided is presented in Appendix B. Data collected includes the following parameters: . Relevant CEMS data . Unit Load, MW I I I I I I I I I I T t I I I I t I Thermo Environmental Instruments EU #2 CO/Oz Thermo Environmental Instruments 10 of 86 cP08 1AS-039393-RT- 1619 I I I I I I I I I t I T I I I T I I I 3.O Sampling and Analytical Procedures 3.1 Test Methods The test methods for this test program have been presented in Table 1-1. Additional information regarding specific applications or modifications to standard procedures is presented below. 3.1.1 EPA Methods 3A, 7Et and 1O, Determination of Oxygen, Nitrogen Oxides, and Carbon Monoxide Concentrations in Emissions from Stationary Sources (fnstrumental Analyzer Procedure) Concentrations of Oz, NOx, and CO were measured simultaneously using EPA Methods 3A, 7E, and 10, which are instrumental test methods. Conditioned gas was sent to a series of analyzers to measure the gaseous emission concentrations. The performance requirements of the method must be met to validate the data. Pertinent information regarding the performance of the method is presented below: . A dry extractive sampling system was used to report emissions on a dry basis . A paramagnetic analyzer was used to measure Oz . A chemiluminescent analyzer was used to measure NOx . A gas filter correlation nondispersive infrared analyzer was used to measure CO . The alternative NOx converter efficienry test described in EPA Method 7E Section 16.2 was used (bag procedure) . Calibration span values were 0-20.45o/o Oz,0-2L.7 ppmvd NOx, and 0- 25.3 ppmvd CO . Prior to conducting the MTA testing, a stratification traverse of the effluent gas was conducted. If the three (3) traverse points show that the effluent gas at each point does not very by * 5.0 percent of the mean concentration or + 0.5 ppm (whichever is less restrictive), the gas stream is not stratified, and the use of a single point may be used for sampling. MAQS conducted the three (3) point stratification test, and it was well below the * 5.0 percent of mean concentration, or * 0.5 ppm. A single sampling point was used for this source. . Minimum Required Sample Duration: 21 minutes The typical sampling system is detailed in Figure 3-1. 11 of 86 cPo8 1AS-039393-RT-1 619 Figure 3-1 US EPA Methods 3A,7E, and 1O Sampling Train 3.1.2 EPA Method 19, Determination of Nitrogen Oxide and Carbon Monoxide Emission Rates EPA Method 19 is a manual method used to determine NOx and CO emission rates, in units of lb/hr, from the measurement of the heat input rate, stack concentration of Oz, and an F factor. The metered fuel flow rate is recorded during each test period. Typically, fuel flow rates are repofted in scf/hr or lblhr. Pertinent information regarding the performance of the method is presented below: . F factor is the oxygen-based F factor, dry basis (Fa) . F factor is the published source-based F factor in EPA Method 19, Table 19-2 t I I I I I I I I I I I I t I T I I I SIGNAL -F! .Mffi BqaffiwfrMCffnqvf,E wmmffi4vlE tl, %f'l\'uErcB.rc'MmwffudreVAE 12 of 85 cP08 1AS-039393-RT- 1619 t I I I I I I I I I I T I I I I I I I 4.O Test Discussion and Results 4.L Field Test Deviations and Exceptions During Run B, a process upset occurred during the first two minutes of the run, skewing the CEMS data collected. Run 8 is not used in calculations of M for any parameter. The CEMS start and stop times for each run was exactly one hour behind the reference method start and stop times. No other field deviations or exceptions from the test plan or test methods occurred during this test program. 4.2 Presentation of Results The RA results are compared to the regulatory requirements in Table 1-2. The results of individual test runs performed are presented in Tables 4-1 through 4-4. Emissions are reported in units consistent with those in the applicable regulations or requirements. Additional information is included in the appendices as presented in the Table of Contents. 13 of 86 cP081AS-039393-RT- 1619 I I I I I I I I I I I I I I I I t T t Table 4-1 oxygen (o/ovd) RATA Results - Nebo EU #2 1 sl29/2024 08:26-08:47 15.0 L4.7 0.3 Y 106 2 s/29/2024 08:57-09:18 14.9 L4.7 o.2 Y 106 3 sl29/2024 09|27-O9;48 15.0 74.7 0.3 Y 106 4 s/29/2024 09:57-10:18 15.0 74.7 0.3 Y 106 5 s/29/2024 10:29-10:50 15.0 L4.7 0.3 Y 106 5 sl29/2024 11:01-11:22 15.0 L4-7 0.3 Y 106 7 5129/2024 11:32-11:53 L4.9 14.5 0.3 Y 106 8 s/29/2024 L2:2O-L2:4L t4.9 74.9 0.0 N 106 9 s/29/2024 12:50-13:11 15.0 15.0 0.0 Y 106 10 s/29/2024 13:20-13:41 L4.9 15.0 0.1 Y 106 Averages 15.O 14.8 o.2 106 Standard Deviation 0,10 o/ovd Confidence Coeffi cient (CC)0.08 o/ovd Bias Adjustment Factor (BAF)1.015 Unit Load 106 MW RA based on mean RM value 2.00 o/o 14 of 86 cPo8 1AS-039393-RT-16 19 I I I I I I I I I I I I Table 4-2 Nitrogen Oxides (!b/MMBtu) RATA Results - Nebo EU #2 I I I I I I I 1 sl29/2024 08:26-08:47 0.018 0.015 0.0024 Y 106 2 s/29/2024 08:57-09:18 0.ot7 o.oL7 0.0003 Y 106 3 s/29/2024 09:27-O9:48 0.018 0.016 0.0017 Y 106 4 slze/2024 09:57-10:18 0.017 0.017 0.0004 Y 106 5 s/29/2024 10:29-10:50 o.oL7 o.oL7 0.0002 Y 106 5 s/29/2024 11:01-1 1:22 0.018 0.017 0.0006 Y 106 7 s/2912024 11:32-11:53 0.017 0.015 0.0014 Y 105 8 5/29/2024 L2:20-1-2z4L 0.015 0.017 0.0007 N 106 9 sl29/2024 12:50-13:11 0.015 0.017 0.0008 Y 105 10 sl29/2024 13:20-13:41 0.016 0.017 0.0008 Y 106 Averages o.o17 o.o17 o.ooo9 106 Standard Deviation 0.0007 lblMMBtu Confidence Coefficlent (CC)0.0006 IblMMBtu Bias Adjustment Factor (BAF)1.055 Unit Load 106 MW RA based on absolute difference 0.0015 lblMMBtu 15 of 86 cPo8 1AS-039393-RT- 16 19 t I t I I T I I I I I I I T t I I Table 4-3 Nitrogen Oxides RATA Results - Nebo EU #2 1 s/29/2024 08:26-08:47 5.0 4.5 0.5 Y 106 2 s/29/2024 08:57-09:18 4.6 4.5 0.1 Y 106 3 s/29/2024 09:27-09:48 4.8 4.5 0.3 Y 106 4 s/29/2024 09: 57-10: 18 4.8 4.5 0.3 Y 106 5 sl29/2024 10:29-10:50 4.7 4.6 0.1 Y 105 6 sl29/2024 11:01-11:22 4.8 4.5 0.3 Y 105 7 sl29/2024 1 1:32-11:53 4.8 4.4 0.3 Y 106 8 sl29/2024 L2:2O-L2t4t 4.5 4.6 0.1 N 105 9 sl29/2024 12:50-13:11 4.4 4.5 0.1 Y 106 10 s/29/2.024 13:20-13:41 4.5 4.5 0.0 Y 106 Averages 4.7 4.5 o.2 106 Standard Deviation 0.16 ppmvd Confi dence Coefficient (CC)o.L2 ppmvd Bias Adjustment Factor (BAF)1.053 Unit Load 106 MW RA based on mean RM value 7.64 o/o cP081AS-039393-RT-1619 I I I I I t I I I T I t I I I I I I I Table 4-4 Carbon Monoxide R^ATA Results - Nebo EU #2 1 s/2912024 08:25-08:47 9.0 9.0 0.0 Y 106 2 s/2912024 08:57-09:18 8.2 8.3 0.1 Y 106 3 s/2912024 O9:27-09:48 8.2 8.0 o.2 Y 105 4 s/29/2024 09:57-10:18 8.5 8.3 o.2 Y 106 5 sl29l2o24 10:29-10:50 8.4 8.2 0.2 Y 106 6 s/29/2024 LLzOL-LL:22 8.2 8.1 0.1 Y 105 7 sl29/2024 11:32-11:53 8.5 8.3 o.2 Y 106 8 sl29/2024 L2:20-L2:47 8.8 8.6 o.2 N 105 9 s/29/2024 12:50-13:11 8.7 8.4 0.3 Y 105 10 sl29/2024 13:20-13:41 8.7 8.5 o.2 Y 106 Averages 8.5 8.3 o.2 106 Standard Deviatlon 0.07 ppmvd Confidence Coefficient (CC)0.06 ppmvd Bias Adjustment Factor (BAF)1.018 Unit Load 106 MW RA based on mean RM value 2.4 o/o L7 of 86 cPo8 1AS-039393-RT-1619 5.O Internal QA/QC Activities Table 5-1 presents a summary of the gas cylinder information. Table 5-1 Gas Cylinder Information 5.1 QA/QC Audits EPA Method 3A,7E, and 10 calibration audits were all within the measurement system performance specifications for the calibration drift checks, system calibration bias checks, and calibration error checks. The NOz to NO convefter efficiency check of the analyzer was conducted per the procedures in EPA Method 7E, Section 8.2.4. The conversion efficiency met the criteria. 5.2 QA/QC Discussion All QA/QC criteria were met during this test program. 5.3 Quality Statement Montrose is qualified to conduct this test program and has established a quality management system that led to accreditation with ASTM Standard D7036-04 (Standard Practice for Competence of Air Emission Testing Bodies). Montrose participates in annual functional assessments for conformance with D7O36-04 which are conducted by the American Association for Laboratory Accreditation (A2lA). All testing performed by Montrose is supervised on site by at least one Qualified Individual (QI) as defined in D7036-04 Section 8.3.2. Data quality objectives for estimating measurement uncertainty within the documented limits in the test methods are met by using approved test protocols for each project as defined in D7035-04 Sections 7.2.L and 12.10. Additional quality assurance information is included in the report appendices. The content of this report is modeled after the EPA Emission Measurement Center Guideline Document (GD-043). I I t I I I I I I T I T I I I I I I I Oz, Balance Nz Mid tO.o7o/o F22023 cc283s37 LL/20/2O3L Oz, Balance Nz High 20.45o/o F22023 DT0049452 02/o8/2O37 NOx, Balance Nz Mid 11.78 ppmv F22024 DTo051716 04/04/2027 NOx, Balance Nz High 2L.7 ppmv F22024 cc755305 03/o4/2O27 CO, Balance Nz Mid 12.0 ppmv F22077 sAs186 LZl06/ZOzs CO, Balance Nz High 25.3 ppmv F22023 DT0008978 08/oL/2031 18 of 86 cPo8 1AS-039393-RT- 1619 Appendix A Field Data and Calculations 29 of 8E GP081AS-039393-RT-1519 Appendix A,1 Instrumental Test Method Data 2B of 88 GP08 1AS-039393-RT- 1619 Ol FI\oF{IFd.InoOl 04OlnooIar. t@oo-(9 e- e Eg E 1 \ E-=d ; at E ., EHa 5 r2 EE6 I HE E 5^ o F 3t # OE s E SS E =E L <r r , u J fo;; ;EE E H" . ; o IItIIIIItIIIIIIIIII == = J J J = f f f == = = 3 : > l r = -o - o - o - o - o - o - o - o -o -o -o -o - o -o -o - o -o - o - o -o EE E E E E E E E E EE E E E E E E E E EE E E E E E E E E E E E E E E E E E E \\ \ \ \ \ \ \ \ \ \ \ \ \ .o € o€ 4 99 € . o .o -o -o - o -o - o -o -o -o -o -o t{ ) N ( Y ) ( Y ) ( v ) ( ' ) ( q $ t 9 $l( \ t ( \ l N ( \ t ( \ t N N G t N @ l\ @ r\ l \ @ t\ (O ( O (O O O O O O O O O O O oo o o o o o o o o qq q q q q g q q o oo o o o o o o o o oo o o o o o o o _ oo o o o c r o o Q Q - oo o o o o o o o o dc i d o o d d c ; c i c ; -$ l c T r r f l O @ l \ c o O r O *t l t l t l t l t { t * * l t - c c c c c c c c c ' t F f5 r f = = J = f c tt t t t t E t d a :: : : : : : _ = - y oo o o o o o o o : - 6o 6 6 6 6 5 5 6 9 o EE ! E O O ! E ! E oo o o o o o o o o o( ) o o o o o o ( ) o oo o o o ( D o d r ( l ) c ) ts T E E T t s E E t s E oo o o o o o o o o oo o o o o o o o o oo o o o a t r o o o o .( U . ( U .( u .O .O .O .O .( o .( U .(U -o - o - o -o -o - o -o - o - o -o EE E E E E E E E E o- o- o. o . o . o_ o _ o- o_ o - o- o- o. o- o. o- o - o - o - o- ET ' E E D ! D ! E ! oo r o o r ( D o ( l ) ( D o r o oo o o o o o o o o oo r o o o o o o o o EI E t E t t s E T t s oo o o o o o o o o oo o o o o o o o o oo o o o o t t r o o o .o . g . o . ( 0 . g s . g . ( ! . o . o -o -o - o -o -o - o -o -o -o -o EE E E E E E E E E o. o - o o . o . o . o . o . o - o - o. o- o. o- o - o - o - o - o - o- l\ (Y ) (O l. ( , (O F (O ( O ( O (Y ) o? o l . : - t a ? q - q \ q \ @@ @ o @ @ c o @ @ @ F( \ l ( Y r s l l O ( O I \ @ O r O :t t : t t : t t r* +L lt *n +t :| h - EC C C . C C , C C C * ff = = = = = : r = c tt t r E t r t r E E t = :: : : : : : : : t oo o o o o o o o l - oo o 6 6 5 6 6 6 0 -- - - - o N- C . , 1 @ O T O N N ( O l r ) qq o g \ q o q \ n - t a ro $ $ s t r f r + ! + s $ -N ( A \ t l r ) ( O N @ C D O :t t :t b rt t {t t t :t t :t t tt rt t - cc c c . c . c e c c * f= f = f f f , = f c tr t t r t t t t t E a :: : : - : : - : E x x x x x x x x x - oo o o o o o o o x zz z 2 z z z z z 9 , z r( \ , l ( Y ) t r O @ N c O O ) O It +t rt t tt :t t +b :t t : t t *t - c c c c c c c c c * ,f = f f = f = f E t_ t _ c . t t t t t t = -- : - = , : v v = . c a x x x x x x x x x - oo o o o o o o o x zz z z z z z z z 9 z ro@or, rN EE E O ! E ! ! T O E oo o o o o ( l ) o ( D ( I ) oo o o o o o o o o oo o o o o o o J o o LL L L L L L LL L L L L E oo o o o o o o o o oo o o o o o o o o .t a n @ o o o o o a t q t .g . g . q . o .( u .( ! .9 . g .g .g -o -o - o -o - o -o -o - o - o -o ;e : e } e ; s ; s : e ; s S : s S (' ) \ f r o ( o N c r c t o +t + t l t + t + t + t { t - E c c c c c c * ff f f = : f f E tr t t t t t t a v- E N( \ t 6 t N ( \ t N ( \ t - oo o o o o o s ! (J lr ) ( v ) ( \ l ( \ l N r O ) c O F O ) o? \ \ \ \ \ q q \ q t$ r + < * \ f $ t + $ $ TF T F F F - F F F rN ( ' ) $ t O ( g N O O ) O +{ t + + h : r L + t t { t : r t - cc c E c c c c c * =3 = f = f = f f c tt r t t t t r E t t = :: : : : : : : = 2 8 NN N N ( \ I N O I 6 I N - oo o o o o o o o l t - - o (g r l \ l \ 1 \ ( O s t t t ( o r O o? o ? o ? o ? o ? o ? o l o ? o ? q 3r + S $ $ t r f t s s r- - F F - F r - r ;e ; e ; e ; e b S S S ; e ; e S rN:t L :t h CC . aa ttNNoo lt oEg=( ) :6O. c9, 2Hs 5 PEE6 e HE E -> l 6^ 0 F or d oo rn sg s E RS E >E r r <l r ) u J fo EE E E E E E E E E o- o - o - o - o. o- o - o - o_ o_ o- o - o - o - o. o. o . o_ o _ o_ (o ( o ( \ t ( o o) rr ) (o €o o) lr ) \: n a r y r c ? u ? a q co o c o c o @ @ @ @ o @ EE E E E E E E E E o. o . o . o- o - o - o - o - o - o- cL o- o - o - o - o - o - o - o- o. (o o r ( ) N F r o | o ( o o ) o ) qq o ? o ? o q e o ? q u ? u ? l. , $ \ t $ < \ f $ . t . ( t . s f -N ( f ) $ l O ( O N @ O ) O +t + t lt l t l * :l t lt :t t : t t F c c c c c t r c c c * 5= f = a = f = = E tt t t t r t E t t = :: =, : : = , : : : Ca x x x x x x x x x - oo o o o o o o o x zZ Z Z Z > 2 2 > . 9 z >o o BE I EE o FN ( f r r + l . l ) ( ) 1 \ @ o l r O +t *: l t t t : t t : t t * t :t t : l t - c E c c c c c c c * =5 f 5 = f f = f , c tt t t r t t r E t E = :: : : : : : : _ - t oo o o o o o o o : - oo o 6 6 6 5 6 0 9 -o Plant Source Date Run MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle May29,2024 #1 RATA T T I I T I I I I I I I I t I I I I I o2 tu Date and Time 5129124 8:26 5129124 8:27 5129124 8:28 5129124 8:29 51291248:30 5129124 8:31 5129124 8:32 5129124 8:33 51291248:M 5129124 8:35 51291248:36 5129124 8:37 5129124 8:38 51291248:39 51291248:40 5129124 8:41 51291248:42 5129124 8:43 51291248:M 5129124 8:45 5129124 8:46 NO, (ppm) co (ppm) 8.7 8.6 8.9 9.1 9.1 9.0 8.8 8.7 8.8 8.8 8.7 8.7 8.6 8.6 8.7 8.7 8.9 8.9 8.8 8.8 8.3 5.1 5.0 4.8 4.9 4.9 5.1 5.1 5.1 5.0 4.9 5.1 5.1 5.2 5,1 5.1 5.0 4.9 5.0 5.1 5.1 5.2 14.9 14.9 14.9 14.9 15.0 15.0 15.0 15.0 14.9 14.9 14.9 15.0 15.0 15.0 15.0 14.9 15.0 15.0 15.0 15.0 15.0 Average :8.8 15.0 22 of 8B GP08 1AS-039393-RT- 1619 MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 Plant: UAMPS Nebo Power Station Source : GE Frame 7EA Turbine - Combined Cycle Date: May29,2024 Run : #2 RATA Date and Time 5129124 8:57 5129124 8:58 5129124 8:59 51291249:OO 51291249:01 51291249:02 51291249:03 5129124 9:04 51291249:05 51291249:06 5129124 9:07 51291249:08 51291249:09 5129124 9:10 5129124 9:11 5129124 9:12 51291249:13 5129124 9:14 5129124 9:15 51291249:16 51291249:17 NOr (pom) 4.6 4.5 4.5 4.5 4.6 4.8 4.7 4.7 4.6 4.7 4.7 4.8 4.8 4.8 4.8 4.7 4.6 4.6 4.7 4.8 4.7 co 02(ppm) gn Average: 4.7 14.7 14.7 14.8 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.8 14.8 14.7 14.7 14.8 14.7 14.7 14.7 14.8 14.7 14.7 8.4 8.6 8.7 8.5 8.6 8.2 7.9 8.2 8.0 8.0 7.9 7.9 7.9 7.9 7.9 8.1 8.2 8.2 8.2 8.1 8.1 I 28 of 88 GP081AS-039393-RT- 1 619 MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 8O1-266-7111 Spanish Fork, Utah 84660 Plant: UAMPS Nebo Power Station Source : GE Frame 7EA Turbine - Combined Cycle Date : May 29,2024 Run: #3 RATA Date and NO, CO 02 Time (ppm) (ppm) lle) 51291249:27 4.9 8.1 14.7 5129124 9:28 4.9 8.0 14.7 51291249:29 4.9 8.1 14.7 5129124 9:30 4.8 8.2 14.7 5129124 9:31 4.9 8.3 14.7 51291249:32 5.0 8.2 14.7 51291249:33 5.0 8.1 14.7 51291249:34 4.9 8.3 14.7 51291249:35 4.8 8.4 14.7 5129124 9:36 4.9 8.6 14.7 5129124 9:37 4.9 8.7 14.7 5129124 9:38 5.0 8.4 14.7 51291249:39 5.1 8.2 14.7 51291249:40 5.0 8.2 14.7 51291249:41 4.9 8.1 14.7 5129124 9:42 5.0 8.3 14.7 51291249:43 5.0 8.2 14.8 5129124 9:44 5.1 8.2 14.7 51291249:45 5.0 8.0 14.7 51291249:46 5.1 8.1 14.7 51291249:47 5.0 8.2 14.7 Average: 5.0 8.2 14.7 I 24 of 88 GPoslAS-03s393-RT-161s I o2 gn NOr (ppm) I I I I I I I I I I t t I I I I I t I Plant Source Date Run MONTROSE AIR QUALIW SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle May29,2024 #4 RATA Date and Time 51291249:57 51291249:58 51291249:59 512912410:OO 512912410:01 512912410:02 512912410:03 512912410:A4 512912410:05 512912410:06 512912410:07 5129124'10:08 512912410:09 512912410:10 512912410:11 512912410:12 512912410:13 512912410:14 512912410:15 512912410:16 512912410:17 4.8 4.7 4.8 4.9 5.0 4.9 5.0 4.9 4.9 4.8 4.8 4.9 4.9 4.9 5.0 5.0 5.0 5.0 5.1 4.9 4.9 co (ppm) 8.4 8.4 8.3 8.2 8.2 8.3 8.5 8.5 8.6 8.7 8.6 8.7 8.6 8.5 8.6 8.5 8.4 8.5 8.4 8.4 8.5 14.7 14.7 14.7 14.7 14.7 14.8 14.7 14.7 14.8 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 Average: 4.9 8.5 14.7 28 of 8d GP08 1AS-039393- RT- 1519 Plant Source Date Run MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle May29,2024 #5 RATA I Date and Time 512912410:29 512912410:30 512912410:31 512912410:32 512912410:33 512912410:34 512912410:35 512912410:36 512912410:37 512912410:38 512912410:39 512912410:40 512912410:41 512912410:42 512912410:43 512912410:M 512912410:45 512912410:46 512912410:47 512912410:48 512912410:49 NO, (ppm) 5.1 4.9 4.9 4.9 4.9 4.8 4.8 4.8 4.8 4.8 4.9 4.9 5.0 4.9 4.9 4.9 4.9 4.9 4.9 4.8 4.8 14.7 14.7 14.7 14.7 '14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14,7 14.8 14.7 14.7 14.8 14.8 14.7 14.7 o2 tY!) co (ppm) 8.4 8.3 8.3 8.3 8.5 8.5 8.5 8.4 8.6 8.5 8.4 8.3 8.3 8.2 8.1 8.2 8.2 8.1 8.1 8.1 8.0 I I Average: 4.9 8.3 I I14.7 t29 of 8d GP08 1AS-039393-RT- 1619 Plant Source Date Run MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 UAMPS Nebo Power Station GE Frame 7EA Turlcine - Combined Cycle May 29,2024 #6 RATA Date and Time 512912411:01 512912411:02 512912411:03 512912411:04 512912411:05 512912411:06 512912411:OT 512912411:O8 512912411:09 512912411:10 512912411:11 512912411:12 512912411:13 512912411:14 512912411:15 512912411:16 512912411:17 512912411:18 512912411:19 512912411:20 512912411:21 NO, CO 02(ppm) (ppm) tZ,) I t 5.0 4.9 4.9 4.8 5.0 5.0 4.9 4.9 4.9 5.0 5.0 5.0 5.0 5.0 5.0 5.0 5.0 4.8 4.9 4.9 5.0 8.2 8.2 8.2 8.2 8.2 8.0 8.0 8.1 8.1 8.2 8.1 8.2 8.2 8.2 8.'t 8.1 8.0 8.1 8.3 8.3 8.2 14.7 14.8 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 Average: 4.9 8.1 14.7 I 2A of 88 GP08 1AS-039393-RT- 15 19 Plant Source Date Run MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle May29,2024 #7 RATA Date and Time 512912411:32 512912411:33 512912411:34 512912411:35 512912411:36 512912411:37 512912411:38 512912411:39 512912411:40 512912411:41 512912411:42 512912411:43 512912411:44 512912411:45 512912411:46 512912411:47 512912411:48 512912411:49 512912411:50 512912411:51 512912411:52 NO, CO 02(ppm) (opm) {yt) I I 5.0 5.0 5.0 4.8 4.9 5.2 5.1 5.0 4.9 5.0 4.9 5.0 4.9 4.8 4.8 4.9 5.0 4.9 4.9 4.9 5.0 8.3 8.3 8.2 8.3 8.5 8.3 8.3 8.4 8.2 8.5 8.4 8.5 8.4 8.5 8.5 8.3 8.2 8.3 8.4 8.4 8.3 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 I I GP08 1AS-039393-RT-16 19 o2 {Ye) I I I I I I I T I I I I I I I I I I MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 Plant: UAMPS Nebo Power Station Source : GE Frame 7EA Turbine - Combined Cycle Date: May29,2024 Run : #8 RATA t NOr (opm) 4.8 4.8 4.9 4.9 4.9 4.9 4.7 4.9 4.7 4.7 4.6 4.6 4.5 4.4 4.5 4.6 4.5 4.5 4.5 4.5 4.5 co (ppm) 8.5 8.5 8.6 8.4 8.6 8.5 8.6 8.6 8.4 8.4 8.7 8.7 8.7 8.6 8.6 8.9 8.8 8.7 8.6 8.5 8.5 14.7 14.7 14.7 14.7 14.6 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 Date and Time 512912412:20 512912412:21 512912412:22 512912412:23 512912412:24 512912412:25 512912412:26 512912412:27 512912412:28 512912412:29 512912412:30 512912412:31 512912412:32 512912412:33 512912412:Al 512912412:35 512912412:36 512912412:37 512912412:38 512912412:39 512912412:40 Average: 4.7 8.6 14.7 39 of 86 GP08 1AS-039393-RT- 1619 Plant Source Date Run MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle May29,2024 #9 RATA Date and Time 512912412:50 512912412:51 512912412:52 512912412:53 512912412:54 512912412:55 5129124'12:56 512912412:57 512912412:58 512912412:59 512912413:00 512912413:01 512912413:02 512912413:03 512912413:04 512912413:05 512912413:06 512912413:07 512912413:08 512912413:09 512912413:10 o2 t%t NOr (ppm) 4.6 4.6 4.6 4.7 4.6 4.6 4.6 4.6 4.5 4.5 4.5 4.6 4.6 4.6 4.7 4.7 4.7 4.5 4.6 4.5 4.6 co (ppm) 8.6 8.5 8.5 8.4 8.5 8.6 8.6 8.5 8.5 8.5 8.6 8.6 8.5 8.3 8.5 8.5 8.3 8.3 8.4 8.5 8.6 14.7 14.7 14.7 14.7 14.7 't4.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 Average:4.6 8.5 14.7 GP08 1AS-039393-RT- 1 619 I t I MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 Plant: UAMPS Nebo Power Station Source : GE Frame 7EA Turbine - Combined Cycle Date : May 29,2024 Run: #10 RATA Date and Time 512912413:20 512912413:21 512912413:22 512912413:23 512912413:24 512912413:25 512912413:26 512912413:27 512912413:28 512912413:29 512912413:30 512912413:31 512912413:32 512912413:33 512912413:34 512912413:35 512912413:36 512912413:37 512912413:38 512912413:39 512912413:40 NO, CO 02(ppm) (ppm) tye) 4.6 4.6 4.5 4.5 4.5 4.5 4.5 4.7 4.7 4.7 4.7 4.6 4.6 4.7 4.7 4.6 4.6 4.6 4.5 4.5 4.6 8.6 8.6 8.5 8.5 8.6 8.7 8.6 8.7 8.5 8.4 8.3 8.6 8.7 8.6 8.4 8.5 8.6 8.4 8.5 8.7 8.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 14.7 t T Average:8.6 14.7 34 of 86 GP08 1AS-039393-RT-16 19 Appendix A.2 Calculations/ Results I I I I I I I t Montrose AIr Quallty Services, LLC. 6823 South 3600 West Spanish Fork, Utah 84660 801-794-2950 RATASheet Company: UAMPS - Nebo Power Station Monitor 02 (Ory) Yo Source: Turbine Date: 512912024 Reference Relative Mothod Method Run # (Yo) (o/,) Abs. Diff Ditr. Sqd.1 15.0 14.7 0.26 0.072 14.9 14.7 0.21 0.053 1s.0 14.7 0.27 0.074 15.0 14.7 0.27 0.075 't 5.0 14.7 0.27 0.076 15.0 14.7 0.26 0.077 14.9 14.6 0.34 0.12'8 14.9 14.9 0.04 0.00I 1s.0 1s.0 0.04 0.0010 14.9 15.0 0.05 0.00 I . Notused,";::r" 14'es 14'76 o'22 Part 75 Llmlt PS3 Llmlt r "".?fl"0#"'"!#3,iT 3:13 -?l?'ffiff:,'n",1, 2'00 to 7'5 Yo 20 o/o I Bias Adjustnent Faclor (BAF) '1.015 Mean Dlfference 0.30 o/oo2 +/- 0.5 oloO2 +/- 1,0 Yooz (including confi dence coefficient) I I I I I I I I I 36 of 88 GP081AS-039393-RT- 16 19 Montrose Air Quality Services, LLC. 6823 South 3600 West Spanish Fork, Utah 84660 801-794-2950 RATA Sheet Company: UAMPS - Nebo Power Station Monitor: Source: Turbine Date: 512912024 Applicable Standard NOx lb/MMBtu I I I I T t I I t I I I I I I I I I T 0.200 lb/MMBtu Reference Relative Method MethodRun# (lb/MMBtu)(lb/MMBtu)1 0.018 0.0162 0.017 0.0173 0.018 0.0164 0.017 0.0175 0.017 0.0176 0.018 0.0177 0.017 0.016*8 0.016 0.0179 0.016 0.01710 0.016 0.017 Abs. Diff o.0024 0.0003 0.0017 0.0004 0.0002 0.0006 0.0014 0.0007 0.0008 0.0008 Diff. Sqd. 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 Ave ' Not used in average Standard Deviation Confldence Coefficient Bias Adjustment Factor (BAF) 0.017 0.017 0.0009 0.0007 0.0006 1.056 Relative Accuracy 8.73 (of RM Test Data) Relative Accuracy 0.75 (of Applicable Standard) Mean Difference 0.0015 (including confidence coefficient) Part 75 Limit %10% lb/MMBtu +l-0.020 Ib/MMBtu 34 of 86 GPo8 1AS-039393-RT- 1619 t I I I I t t Montrosa Alr Quallty Sorvlcas, LLC. 6823 South 3600 West Spanish For*, Utah 84660 801-794-2950 RATA Sheot Company: UAMPS - N6bo Power Station Monitor: NOx ppmdv Source: Turbine Dale: 512912024 Applicable Standard 97.87 ppmdv The standard is 97.12 ppmdv@15o/o o2, dry Reference Relative Method Method Run # (ppmdv) (ppmdv) Abs. Diff Diff. Sqd.1 5.O2 4.49 0.53 0.282 4.61 4.50 0.11 0.013 4.82 4.48 0.34 0.124 4.76 4.50 0.26 0.075 4.69 4.55 o.fi O.026 4.80 4.49 0.31 0.097 4.77 4.M 0.33 o.'tl4.47 4.58 0.11 0.01I 4.43 4.50 0.07 0.0010 4.45 4.50 0.05 0.00 t Ave 4.7'l 4.49 0.24 I 'Not used in average 75 Llmlt PS2 Ltmtt ""f,fl"0;y"::H:l$l 3:13 .i:?'ff+::InB 7'u '/' 10 '/' 20 '/. I Bias Adjustmsnt Factor (BAF) '1.053 Relatlve Accurary 0.37 % - 10 %I (of Applicabl€ Standard) Mean Dlfisrence 0.36 ppm I (including confidenca coefficient) I T I I I I I I 38 of 8B GP081AS-039393-RT- 1619 Montrose Air Quality Services, LLC. 6823 South 3600 West Spanish Fork, Utah 84660 801-794-2950 RATA Sheet Company: UAMPS - Nebo Power Station Source: Turbine Dale: 512912024 Applicable Standard 10.08 ppmdv The standard is 1 0 ppmdv@1io/o o2, dry I I I I I I T T I I T T I T I I I I I 0.158.47Ave * Not used in average Standard Deviation Confidence Coefficient Bias Adjustment Factor (BAF) ppmdv Abs. Diff Diff. Sqd.0.03 0.000.07 0.000.16 0.030.15 0.020.16 0.020.11 0.010.16 0.030.16 0.030.26 0.070.23 0.05 Relative Accuracy 2.41 o/o (of RM Test Data) Relative Accuracy 2.03 Yo (of Applicable Standard) Mean Difference O.2O ppm (including confi dence coefflcient) PS4a Limit 10% +/- 0.5 ppm CO Reference Relative Method Method Run # (ppmdv) (ppmdv) 1 9.0 9.02 8.2 8.33 8.2 8.04 8.5 8.3s 8.4 8.2 6 8.2 8.'r 7 8.5 8.3t8 8.8 8.69 8.7 8.410 8.7 8.5 0.074 0.057 1.018 39 of 86 GP08 1AS-039393- RT-16 19 I Appendix A.3 Example Calculations 30 of 88 GP081AS-039393-RT-1619 SAMPLE CALCULATIONS UAMPS - Nebo Power Station, GE Frame 7EA Turbine - Combined Cycle 24-May-24 AVERAGE STACK GAS CALCULATIONS CORRECTED FOR SYSTEM BIAS VIA USEPA 7E Averaoe Gas Effluent Calculation Corrected for Svstem Bias Check. C ,-": USEPA 7E Run I cro = (c"*-cJx[c*/(G,-c")l O, Concentration in Stack Gas (oercent) Gs*o = (14.954-0.1)x[10.070/(10.1 -0.1)] CsasD = 14.958 % NO- Goncentration in Stack Gas (parts per million bv volume. drv) CsuD = (5.032-0)x[11.78/(11.800-0)] CsasD = 5.023 ppmvd CO Concentration in Stack Gas (oarts oer million bv volume. drv) Cgaro = (8.762 - 0.2) xl12 / (11.650 - 0.2)I CgasD = 8.973 ppmvd I I I I I t I I I I I I I I I I I I I Symbol Definition ravo Average gas concentration from analyzer, parts per million by volume or percent volume sma Actual concentration of the upscale calibration gas (SV), parts per million by volume or percent volume vO Average of the initial (Zi) and final (2fl calibration bias check results for the zero gas, parts per million by volume or percent volume em Average of the initial (Si) and final (Sf) calibration bias check results for the upscale calibration gas, parts per million by volume or percent volume vgasD Average gas effluent concentration conected for system bias check, parts per million by volume or percent volume egasW Average gas effluent concentration conected for system bias check, parts per million by volume or percent volume Gas Component o2 o/ovd Coz o/o vd Nox oomvd co oomvd Soz oomvd THC DDMVW CHr DtlMl,ll, vavo 15.0 N/A 5.0 8.8 N/A N/A N/A zero initial (Zi)o.2 N/A 0.0 0.1 N/A N/A zero final (Zf)0.0 N/A 0.0 0.3 N/A N/A co 0.1 N/A 0.0 0.2 N/A N/A N/A uoscale initial (Si)10.2 N/A 11.8 11.7 N/A N/A uoscale final (Sfl 10.0 N/A 11.8 11.6 N/A N/A cm 10.1 N/A 11.8 11.7 N/A N/A N/A uoscale value (SV)10.07 N/A 11.78 12.0 N/A N/A N/A 38 of 8B GP08 1AS-039393-RT-16 19 UAMPS Nebo Pouer Stadon GE Frame 7EA Turblne - Comblned cYclc sl29l2O24 Run ll1 Sample Calclrlatlons EPA Method 7E: DGtermlnatlon of Nltrogen (xldes Emlsslons from statlonary Sources (hstrumental Analyrer Procedurel (to cFn Part 50, Appendh A-41 (C--Cd)xC-, (C, - Co) (5.0-(0))x11.78 (11.8 - (0)) = s.oppmvd (Eq.7E-Sb) cd= (c-,) (Mw) (", , ("""., = 5.mE-07 lblsc{ Ery*-= (Ca) (Fa) (20.9) (20.$Or%vd) = (s.0) (8,710) (20.s) (20.$15.0) = 0.018 lb/mmBtu (Eq.1e-7) Varlable value )eflnftlon 5.0 ryeraoe Unadiusted Gas Concentration pDmvd c"0.0 qveraoe Pra/Post Zero Gas Resoonse ppmvd c--1'1.8 loncsntratlon of Upscalo Calibration Gas oom c-"t't.8 ryerage Pro/Post Upscalo Gas R€ponso ppmvd 5.0 ryeraqe Gas Concentration Adiusted for Bias Ppmvd MW 46.01 \,lolecular W€ioht lbllFmole 385.3 385.3 r'olume of One Pound of ldsal Gas at Standard Conditions scfllFmole F,4710 : Fac{or ftom EPA Method '19 scflmmBtu 6.00E-07 ,ollutant Conc€ntration. Drv Basls oounds oer standard cubic foot O, %vd 15.0 ), Concentration dry volume oercent Errr-^n.0.018 :mission Rate pounds per million British thermal units 39 of 88 GP08 1AS-039393-RT- 1 619 UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle s12912024 Relative Accuracy Test Audit Sample Calculations 02% Run # t I I I I t I t I I T I I T I I t I I d2 1 2 3 4 5 6 7 I 9 10 11 12 14.960 14.910 14.970 14.970 14.970 14.960 14.940 14.960 14.950 14.700 14.700 14.700 14.700 14.700 't4.700 14.600 15.000 15.000 0.260 0.210 o.270 0.270 0.270 0.260 0.340 0.040 0.050 0.067600 0.044100 0.072900 0.072900 0.072900 0.067600 0.115600 0.001600 0.002500 Average Sum -2)um L4.954 L4.756nla nla nla nla 0.219 L.970 3.8809 o.05752 o.5L770 nla CC=(b.osrr) Sd Vn (2.306) (0.104) = 0.0799 sa= ld l+ lCCl RM = 0.219 + 0.080 M.954 = 2.OO96 BAF= 1 + ldl cEMavs = 1 + 0.219 (100) (100) 14.756 1.015 Variables rd',0.51770 Sum of the Squared Dffierences lId,l'3.8809 Square of the Summed Differences n I Number of Test Runs sd 0.104 Standard Deviation of Differences h.oszs 2.306 T-value from PS2, Table 2-1 cc u.u/99 2.5% Confi dence Coefficient tdt o.219 Absolute Averaoe Dffierence lccl 0.0799 Absolute Confi dence Coefficient RM 14.954 Averaqe RM Value RA 2.00%Relative Accuracv RA 0.22 % Absolute Difference 49 of 88 GP08 1AS-039393-RT- 16 19 1 2 3 4 5 6 7 8 I 10 't1 12 I t I I I I I t I t I I I I I I I I I UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle slzel2o24 Relative Accuracy Test Audit Sample Calculations NO, (lblmmBtu) Run# RM CEM d d2 0.018 0.017 0.018 0.017 0.017 0.018 0.017 0.016 0.016 0.016 0.017 0.016 0.017 0.017 0.017 0.016 0.002 0.000 0.002 0.000 0.000 0.001 0.001 0.001 0.001 0.000004 0.000000 0.000004 0.000000 0.000000 0.000001 0.000001 0.000001 0.000001 Sa= 0.017 0.017 Average Sum -25Um 0.017 nla nla o.oL7 nla nla 0.00000 0.00001 nla 0.001 0.008 0.0001 CC= (b.ogzs) Sa Vn = (2.306) (0.001) 3 = 0.0005 pa= ld l+lccl RM = 0.001 + 0.001oI'17- = 8.7196 BAF= 1 + ldl cEM"r8 = 1 + 0.001 o.u7 = 1.053 (100) (100) Variables rd',0.00001 Sum of the Squared Differences tIdJ 0.0001 Square of the Summed Differences n 9 Number of Test Runs sd 0.001 Standard Deviation of Differences to.mzs 2.306 T-value from PS2, Table 2-1 CC 0.0006 2.5o/o Confidence Coeffi cient tdt 0.001 Absolute Averaoe Difference lccl 0.0006 Absolute Confidence Coeffi cient RM 0.017 Averaoe RM Value RA 8.710/o Relative Accuracv 44 of 8d GPo8 1AS-039393-RT-15 19 UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle sl2sl2o24 Relative Accurary Test Audit Sample Calculations NO, PPm Run# RM CEM I I I I I I I I I I I I T I T t I I I Sa= d2 0.070 0.0049000.050 0.002500 4.430 4.450 ,| 2 3 4 5 6 7I I 10 11 12 5.020 4.610 4.820 4.760 4.690 4.800 4.770 4.490 4.500 4.480 4.500 4.550 4.490 4.440 4.500 4.500 0.530 0.110 0.340 0.260 0.140 0.310 0.330 0.280900 0.012100 0.1 15600 0.067600 0.019600 0.096100 0.108900 Average 4.7OG Sum nla sum2 nla Applicable Standard Variables 4.494 nla nla 97.12 o.238 2.140 4.5796 0.07869 0.70820 nla (100) (100) CC=(to.osrr) Sd Vn = (2.306) (0.158) = O.t2L3 pq= ld l+ lcc I RM = 0.239 + 0.121 -Joo = 7.6396 BAF= 1 + ldl cEM"r8 = 1 + 0.238T = 1.053 (100) (100) R/q= ld l+ lcc I AS = 0.239 + 0.121 97ln = 0.35 rd',0.70820 Sum of the Squared Differences tId,l'4.5796 Square of the Summed Differences n I Number of Test Runs sd 0.'158 Standard Deviation of Differences b.*rt 2.306 T-value from PS2, Table2-1 cc 0.1213 2.5% Confidence Coefficient tdt 0.238 Absolute Averaoe Difference lccl 0.1213 Absolute Confidence Coefficient RM 4.706 Averaoe RM Value RA 7.630/o Relative Accuracy RA 0.36 % RA of Aoolicable Standard 42 of 8B GPo8 1AS-039393-RT- 1619 1 2 3 4 5 6 7 8I 10 11 12 t I I I I I I I I t I I I I I I I I I UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle slzel2o24 Relative Accuracy Test Audit Sample Calculations CO ppm Run# RM 9.0 8.3 8.0 8.3 8.2 8.1 8.3 8.4 8.5 9.0 8.2 8.2 8.5 8.4 8.2 8.5 8.7 8.7 o.o27 0.067 0.161 0.152 0.156 0.107 0.164 0.262 o.232 0.001 0.005 0.026 0.023 0.024 0.011 0.027 Average Sum Sum2 0.069 0.054 o.o27 0.239 nla 8.34 0.148 nla 1.328 nla 1.7642 8.47 nla nla CC=(b.orrr) Sd Vn = (2.306) (0.074) 3 = 0.0566 p.1q= ld l+ lccl RM = 0.148 + 0.057 8,471 = 2.4lYo BAF= 1 + ldl cEMavs = 1 + 0.148 (100) (100) 8.344 1.018 Variables rd',0.23940 Sum of the Squared Differences lldrl'1.7642 Square of the Summed Differences n I Number of Test Runs sd o.o74 Standard Deviation of Differences h.oszs 2.306 f-value from PS2, Table 2-1 cc 0.0566 2.5% Confldence Coefficient tdt 0.148 Absolute Averaoe Difference I ccl 0.0566 Absolute Confidence Coefficient RM 8.471 Averaoe RM Value RA 2.41o/o Relative Accuracv Mean Diff 0.20 ppm including lCCl 48 of 88 GP08 1AS-039393-RT- 1 619 Appendix B Facility CEMS Data 44 of 8A GP08 1AS-039393-RT-1619 ol rl(o7.1IFdI0. )ol (nor (Y toIoFI@oCL(,GoEo6$FdI (JUI( doNr o '{ € NO r{ dc ) o dN dNNdNN d@ oc; HON: n dNN+)coG.ntr .. oo C') !, (,Lo |! > r{ t A N O O g m + O O N O O I m @ O N 3 O O O N .s 6 IF U v r { O O m @ @ O O @ 6 @ 6 6 F l O r{ 6 6 h O (O ,; t d n o t o O N 6 O O 6 F. 4 (O N € n (O $ 6 h rc , 6 € € Ei J O { J O O O O O O O O O O O O O O O O O O O O O >o o : - FF { E N N N N N N N F. N N N l- N N F. N N N t\ N N -- !lor { Edl, F{ ll, ^. ( O (O N (O @ @ @ @ N (O N (o ( ! Ft (o ( o N (o {, o (o N E o o o o o o o o o o o o o . o o o o o o o o o p- eH d d d d r { d F d H d d r- l r { d d d d r { r - l d E- } J =- 3 dCOE F d !,(,oJ d . c A O o O O O O O O O O O O O O O O O O (, o o &6 HE I J \ r O O O O O O O O O O O O O O O O O O O O O 7 0 0 iu co P =- O 3 BH g O'F F=q?id td(, Fl t A N c l O t m S O O N O @ S m @ O N S O O O N .| l o p FU v d o o m @ o o o @ 6 o m @ d o i 6 h h o @ .; u q o o @ N o 6 o € N h o N 6 6 \o t 6 6 ro € @ @ E o { J o o o o o o o o o o o o o o o o o o o o o )- O J -H C N N. N ' N N N N N N N N T N N N N N N N N N O. F - LoF l (ltJ XU A N N N N N N N N N N N T\ . N N N N N N N N 6 9t J O . d I vr t t $ $ S \n $ r+ $ 3 $ tl < t < t < t $ rt t * <t tf P OH i id dF t d d F{ H d r l F l F i F l t H d dH H (, L E ooc-!. NF I o X a A h € I @ @ N r @ @ @ (O tO N @ € @ @ @ N r f \ uP o d d d d d d d d i Fl d d d d Fl H d d r- l . i d d a a vo o o o o o o o o o o o o o o o o o o o o PU O . 0L P O O O O O O O O O O O O () ( ) O O O O O O O of uG c 0- o l) E - xoz ! U ^N N € A N N N N N € N N N a\ N N 6 N t s @ 6 u€ oh $ N 6 $ 6 h t t m s t h + t = m * h € 6 6> v . uE @ s $ 9 + 3 + + s s * { r t $ 3 t 3 t + s = Ut o ' P [5 g, Ccx - -o 2A J U A€ i 6 I N O o Q O O O O O 6 O N N O () h N ut t o . t! > v@ 6 o o o o € o o € 6 @ @ @ o 61 6 6 o 6 € ve o hc r P AA (, t r 40 - r( J r{ O N 6 Or O Fl N 6 i+ 4 @ N € O l O r{ N 6 t f 6 tO r\ N N N m 6 m m m 6 m m 6 m rl rl $ * I \t S .. N N N N N N N N N N N N N F . N N N N F. N N go o o o o o o o o o o o o o o o o o o o o tis s s 9 v v v qv v s s s gs s s q v g q rN N N N N . ! N N N N N N N N N N N N N N N >c i o o o o o o o o o o o o o o o o o o o o Y{N N N N N N N N N N N N N N N N N N N N N E\ \ \ \ \ \ \ \ \ \ \ \ \ \\ \ \ \ \ \ \ .P 6 6 6 o o o o o o o ao o o o o 6 o o o o BN NN N N N N N N N NN N N N N N N N N N \\ \ \ \ \ \ \ \ \ \ \ \ \ \ \ \ \ \ \ \ 6h 6 6 6 6 6 h 6 6 h 6 h 6 6 6 6 6 6 h 6 o( , o o o o o o o o o o o o o o o o o o o trfi ITtIIIItttItIIIIIII + troP(6P|/ l - c (d r- P (U = 3oo- E o oU l ll >(u ( o zo - i;Ett ,z>c PO .r (t t 99cl O tl J (o:No$a\ lor!\Ol (\\hooF@F l N fY 1 {J *; L oo O \r $ A t \ I t \ l+o F; ( d, ;; rN l \ l +J v oo E (U U ? c] ! q ii i 0, ,t n u : I i h .. L ( l: X Eo u su eE ; II EEr gHI sEltTII 6t;l ItIIIIIEl IEl do o ddN oqNooN rl r 0NO r{ NdNNd oo r- t o$ N @ PEoL.nP(, .. oo o Ed Lo (r > Fl S @ 6 O O @ m O 6 O () N m m 6 N O @ + O m @ -lF o P- U V d A 6 6 FJ m d 6 6 6 d m 6 @ '1 O @ 6 h @ H .F dO O O * 6 I 6 m m f i 6 N N m S Fl -l d d N O F i m EP O { J O O O O O ' O O O O O O O O O O O O O O O O 20 0 = FF I tr N N N N N N F . N N N N N F - N F. N N N l'r N N -- IOH r(!t9 d o A N \o N N @ @ @ N ro (o N r o N 6 N @ 6 N @ (o N - oo o o o o o o o o o o o o o o o o o o o o lr - vH d d d d. . l d d H d i i F l F l F l d d H d d d o c- P )e = rU C o-F H a;a6oJ XY A N N N @ N N N A @ N Nts @ A N N NN @N N UU q . 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"\+ coP(gPl/ ) - c d LPor = =oo. t r o o t/ t -O >r (u f ! z. o- oEd>r t r +J O -P.r G l rJ u do N-l@o$No(\Ol r!utooFhs P *; L oa O <r s r\ l r \ il RR d. .- . ; .d SS P v oo ! rd l l * o! q ti <6 f; t \V E t r Ot t- l roF{+d.I(Y lo|mOl (noIat{ooo-u, TE@5oBEr FdJthE HN @oN€oqN r. t oo F{ ( o Nc ) t{ r{ o 6 HN !tFI rr € NH oc; daNr t t oPco4r!Po{ , C' .E t 6 o .l > d I A O 6 @ t O N O m 6 N m t t * l r O f\ N O O (O |o rO .t l - o X F U v O O H r . { F l m € @ d € O O 6 h (O i O 6 r. { Fl d ;'. i o o st N m m N o 6 o o o o o o F. o d F l o o o o 't y o P o o o o o o o o 6 o o o o o o o o o o o o =o o = ' Fd C N N N N N I . " lD O TO (O N T\ (. 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J t\ f t\ l l\ l ao Gt (\ l O) O l (\ r\ Lr t r / l oo PE ESS. - (r r g LAoq .q l B o:r!r{=f(\ONCt i (\tnOoo( 0 (\ l Lr ) (\ I ar. ) rl r l PLoCL (ud(dP' (U U aE l- {9 3? Appendix C Quality Assurance/Quality Control 58 of 88 GPo8 1AS-039393-RT-1619 Appendix C.1 Units and Abbreviations 59 of 8B cP08 1AS-039393-RT-16 19 I I t I I I I I I I I t I I I I I I I M I+?N,T+SP.H @XYoo,2 lccl tdtoc oF oR " Hzo 13.6 AH AP e ps Pa tu acfm ,\ A Btu B* c, Caw Con cf or ft3 cfm Co"" cM cm or m3 cMA co cp c" CS cs cv D d6 dcm Dn D8 dscf dscfm dscm Fd fpm fps ft tr I gal gr UNITS OF MEASUREMENT conected to X% orygen (corrected for dilution air) absolute value of the confidence coefficient absolute value of the mean differences degrees Celsius degrees Fahrenheit degrees Rankine inches of water column specific gravity of mercury pressure drop across orifice meter, inches H2O velocity head of stack gas, inches H2O total sampling time, minutes microgram density of acetone, mg/ml density of water, 0.9982 g/ml or 0.002201 lb/ml actual cubic feet of gas per minute at stack conditions cross-sectional area of node,# cross-sectional area of stack, square feet (f) British thermal unit proportion by volume of water vapor in gas stream particulate matter concentration in stack gas, gr/acf average unadjusted gas concentration, ppmv measured concentration of calibration gas, ppmv cubic feet cubic feet per minute average gas concentration adjusted for bias, ppmv average of initial and final system bias check responses from upscale calibration gas, ppmv cubic meters actual concentration of the upscale calibration gas, ppmv average of initial and final system bias check responses ftom low-level calibration gas, ppmv pitot tube coefflcient particulate matter concentration in strack gas, gr/dscf calibration span, % or ppmv measured concentration of calibration gas, ppmv manufactured certified concentration of calibration gas, ppmv drift assessment, % of span dry cubic feet dry cubic meters diameter of noZe, inches diameter of stack, inches dry standard cubic feet dry standard cubic feet per minute dry standard cubic meters F-factor, dscf/MMBtu of heat input feet per minute feet per second feet square feet gram gallons grains (7000 grains per pound) 60 of 88 GP08 1AS-039393-RT- 1519 UNITS OF MEASUREMENT I 6.'i\ l*?N,I+gLI gr/dscf hr I in k K K3 lq kgq kwscftr I lb/hr lb/MMBtu lpm m M m' ma Md meq mg Mg min ml or mL mm MM MMBtu/hr mn mol mol. wt. or MW M" IvM n ng nm Nm3 oI bar pg Ps P. ppb ppbv ppbvd ppm ppmv ppmvd ppmvw P" psi psia psig grains per dry standard cubic feet hour percent of isokinetic sampling inch kilo or thousand (metric units, multiply by 103) kelvin (temperature) conversion factor 0.0154 gr/mg conversion factor 0.002668 ((in. HgXft3))/((mlX'R)) kilogram pitot tube constant (85.49 fUsec) thousand wet standard cubic feet per hour liters pounds per hour pounds per million Btu liters per minute meter or milli thousand (English units) or mega (million, metric units) cubic meters mass of residue of acetone after evaporation, mg molecular weight of stack gas; dry basis, lb/lb-mole milliequivalent milligram megagram (106 grams) minute milliliter millimeter million (English units) million Btu per hour total amount of particulate matter collected, mg mole molecular weight molecular weight of stack gas; wet basis, lb/lb-mole molecular weight or megawatt number of data points nanogram nanometer normal cubic meter barometric pressure, inches Hg picogram stack static pressure, inches H2O barometric pressure of dry gas meter, inches Hg parts per billion parts per billion, by volume parts per billion by volume, dry basis parts per million parts per million, by volume parts per million by volume, dry basis parts per million by volume, wet basis absolute stack gas pressure, inches Hg pounds per square inch pounds per square inch absolute pounds per square inch gauge I I I t I I t I I I I I I I I t IGP08 1AS-039393-RT- 1 619 I I M A,}?"I.{,T+ST.H UNITS OF MEASUREMENT I Petd standard absolute pressure, 29.92 inches Hg Q" volumetric flow rate, actual conditions, acfm I Q" volumetric flow rate, standard conditions, scftn t Qsr volumetric flow rate, dry standard conditions, dscfm R ideal gas constant 21.85 ((in. HSI (fttry(fnl (lbmole)) I SBn*r post-run system bias check, % of span I SBr pre-run system bias check, % of span scf standard cubic feetscffr standard cubic feet per hour I scfm standard cubic feet per minutef scm standard cubic meters scmh standard cubic meters per hourI Ll""o. o, ",r :lff:'f" t metric ton (1000 kg) I r o.szs t-value f T" absolute average ambient temperature, 'R (+459.67 for English) Tm absolute average dry gas meter temperature, oR (++SS.OZ for English) I ton ort ton = 2000 pounds I tph or tons/trr tons per hour tpy or tons/yr tons per year I T" absolute average stack gas meter temperature, oR (+459.67 for English) I J- absolute temperature at standard conditions % volume of acetone blank, ml I Vtr volume of acetone used in wash, ml I V6 total volume H2O collec{ed in impingers and silica gel, grams V- volume of gas sampled through dry gas meter, ft3 I V,x*l volume of gas measured by the dry gas meter, conected to standard conditions, dscf f Vna stack gas volume sampled, acf Vn volume collected at stack conditions through nozzle, ad I VB average stack gas velocity, feet per second f V*r",ar volume of water vapor condensed, conected to standard conditions, scfIVu(su) volume of water vapor in gas sampled from impingers, scf r Vws(srd) volume of water vapor in gas sampled ftom silica gel, scf I W" Il[* " residue in acetone wash, ms Wr,np total weight of impingers, grams I W., total weight of silica gel, grams I Y dry gas meter calibration factor, dimensionless t I I I 69 of 88 GPo8 1AS-039393-RT-1619 64\ m?N,I+gp.E- ACE AD ADL AETB AS ASTM BACT BDL BHP BIF BLS cc CD CE CEM CEMS CERMS CET CFR CGA CHNOS CNCG co coc COMS CPM GPMS CT CTM CTO CVAAS D8 DE Dioxins DLL DNCG ECD EIT ELCD EMPC EPA EPRI ES ESP EU FCCU FGD FI FIA FID FPD FPM I I I t I I I I I I I I I I I I t I I AAS ACDP ABBREVIATIONS atomic absorption spectroscopy air contaminant discharge permit analyzer calibration enor, percent of span absolute difference above detection limit Air Emissions Testing Body applicable standard (emission limit) American Society For Testing And Materials best achievable control technology below detection limit brake horsepower boiler and industrial furnace black liquor solids confidenc€ coefficient calibration drift calibration error continuous emissions monitor continuous emissions monitoring system continuous emissions rate monitoring system calibration error test Code of Federal Regulations cylinder gas audit elemental analysis for determination of C, H, N, O, and S content in fuels concentrated non-condensable gas catalytic oxidizer chain of custody continuous opacity monitoring system condensable particulate matter continuous parameter monitoring system combustion turbine conditional test method catalytic thermal oxidizer cold vapor atomic absorption spectroscopy equivalent diameter destruction efficiency polychlorinated dibenzo-p{ioxins (PCDDS) detection level limited dilute non-condensable gas electron capture detector Engineer ln Training electrolytic conductivity detector (hall detector) estimated maximum possible concentration US Environmental Protection Agency Electric Power Research lnstitute emission standard (applicable limit) electrostatic precipitator emission unit fluid catalytic cracking unit flue gas desulfurization flame ionization fl ame ionization analyzer fl ame ionization detector fl ame photometric detector fi lterable particulate matter 59 of 8B GP081AS-03939 3-RT- 1619 I I I I I T I I I I I I I t I I I I t 6.1\}I?N,T+ST.H FTIR FTPB FTRB Furans GC GC/MS GFAAS GFC GHG HAP HC HHV HPLC HRGC/HRMS HRSG tc ICAP ICPCR ICP-MS IR tso KW LFG LHV LPG MACT MDI MDL MNOC MRL MS NA NCASI NCG ND NDIR NESHAP NG NIOSH NIST NMC NMOC NIA/OC NPD NSPS OSHA PAH PCB PCWP PE PFAS PI PID PM ABBREVIATIONS Fourier-transform infrared spectroscopy field train proof blank field train recovery blank polych lori nated dibenzofurans (PCDFS) gas chromatography gas chromatography/mass spectroscopy graphite fu mace atomic absorption spectroscopy gas filter conelation greenhouse gas hazardous air pollutant hydrocarbons higher heating value high performance liquid chromatography high-resolution gas chromatography/high-resolution mass spectroscopy heat recovery steam generator ion chrcmatography inductively-coupled argon plasma emission spectroscopy ion chromatography with a post-column reactor inductively coupled plasma-mass spectroscopy infrared radiation I ntemational Standards Organization kilowatts landfill gas lower heating value liquified petroleum gas maximum achievable control technology methylene diphenyl diisocyanate method detection limit maximum normal operating conditions method reporting limit mass spectrometry not applicable or not available National Council ForAirAnd Steam lmprovement non-condensable gases not detected non-dispersive infrared National Emissions Standards For Hazardous Air Pollutants natural gas National lnstitute For Occupational Safety And Health National lnstitute Of Standards And Technology non-methane cutter non-methane organic compounds non-methane volatile organic compounds nitrogen phosphorus detector New Source Performance Standards Occupational Safety And Health Administration polycyclic aromatic hydrocarbons polychlorinated biphenyl compounds plyrvood and composite wood products Professional Engineer per- and polyfluoroalkyl substances (PFAS) photoionization photoionization detector particulate matter 64 of 88 GP08 1AS-039393-RT- 1 619 A4\ AT?N,T+ST.H PMro PMz.s POM PS PSD PSEL PST PTE PTM OA,/OC QI QSTI RA RAA RACT RATA RCTO RICE RM RTO SAM SCD SCR SD Semi-VOST SRM TAP TBD TCA TCD TGNENMOC TGNMOC TGOC THC Trc TO TO TPM TSP fiE ULSD UV VE voc VOST WC WWTP ABBREVIATIONS particulate matter less than 10 microns in aerodynamic diameter particulate matter less than 2.5 microns in aerodynamic diameter polycyclic organic matter performance specifi cation particle size distribution plant site emission limits performance specifi cation test permanent total enclosure performance test method quality assurance and quality control Qualified lndividual Qualifled Source Testing lndividual relative accuracy relative accuracy audit reasonably available control technology relative accuracy test audit rotary concentrator thermal oxidizer stationary reciprocating internal combustion engine reference method regenerative thermal oxidizer sulfuric acid mist sulfu r chemiluminescent detector selective catalytic reduction system standard deviation semi-volatile organic compounds sample train standard reference material toxic air pollutant to be determined thermal conductivity analyzer thermal conductivity detector total gaseous non-ethane non-methane organic compounds total gaseous non-methane organic compounds total gaseous organic compounds total hydrocarbons tentatively identifi ed compound thermal oxidizer toxic organic (as in EPA Method TO-15) total particulate matter total suspended particulate matter temporary total enclosure ultra-low sulfur diesel ultraviolet radiation range visible emissions volatile organic compounds volatile organic sample train water column waste water treatment plant t t I I I T t I T t I I T I t t T I t6E of 88 GP08 1AS-039393-RT- 1619 I I I I I I I I I N2 NHs Ni I I I t I I I I t 6/i\ A+Q,N,I+g:,H Ag silver As arsenic Ba barium Be beryllium C carbonCd cadmium CdS cadmium sulfide CH2O formaldehyde CH3CHO acetaldehyde CH3OH methanol CHn methane QHrO ethylene oxide QHo ethane CaH4O acrolein CaH6O propionaldehyde CsHa propane C6H5OH phenol Clz chlorine ClO2 chlorine dioide CO carbon monoxide Co cobalt COz carbon dioxide Cr chromiumCu copper EtO ethylene oxide EIOH ethyl alcohol (ethanol) H2 hydrogen CHEMICAL NOMENCLATURE Se soz Sog SO, TCDD TCDF TGOC THC TI TRS Zn selenium sulfur dioxide sulfur trioxide sulfur oxides tetrachlorodibenzodioxin tetrachlorodibenzofu ran total gaseous organic concentration total hydrocarbons thallium total reduced sulfur compounds zinc I HzOz hydrogen peroide HzS hydrogen sulfide H2SO1 sulfuric acid HCI hydrogen chlorideHg mercuryIPA isopropyl alcoholMDI methylene diphenyl diisoryanate MeCl2 methylene chlorideMEK methyl ethyl ketone MeOH methanolMn manganese nitrogen ammonia nickel NO nitric oxide NOz nitrogen dioxide NO, nitrogen oxides 02 orygen P phosphorus Pb lead PCDD polychlorinated dibenzo-pdioxins PCDF polychlorinated dibenzofurans 68 of 88 GP08 1AS-039393-RT- 1619 Appendix C.2 Instrumental Test Method QA/QC Data 64 of 8E GP081AS-039393-RT-16 19 I t I I I I t I I I I I I I I I I I t Plant Source Date Run MONTROSE AIR QUALITY SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle 512912024 Stratification Traverse Point No. 1 Date and Time 51291247:59 5129124 8:00 5129124 8:01 51291248:02 51291248:03 51291248:04 co (ppml Point Average 5.13 o2 gn NO, (ppm) o,,o diff 5.1 5.1 5.1 5.1 5.2 5.1 8.0 8.0 8.0 8.0 8.0 8.0 15.0 14.9 14.9 14.9 14.9 14.9 -1.1o/o 5129124 8:05 5129124 8:06 5129124 8:07 5129124 8:08 5129124 8:09 5129124 8:10 5129124 8:11 -0.4% 5.3 8.05.2 8.15.1 8.15.1 8.25.0 8.15.1 8.35.1 8.34.8 8.15.1 8.25.0 8.54.9 8.75.0 8.75.0 8.85.0 8.7 15.3 14.9 14.9 14.9 14.9 14.9 15.0 5.09 5129124 8:12 5129124 8:13 5129124 8:14 5129124 8:15 5129124 8:16 5129124 8:17 5129124 8:18 15.3 14.9 14.9 14.9 15.0 14.9 15.0 4.99 1.60/" 5129124 8:19 5129124 8:20 5129124 8:21 51291248:22 51291248,,23 51291248:24 5129124 8:25 4.8 5.0 5.0 5.1 5.1 5.1 5.2 8.3 8.5 8.7 8.7 8.9 8.8 8.6 15.2 15.0 15.0 15.0 15.0 14.9 14.9 5.08 -0.1o/o Mean =5.1 58 of 88 GPo8 1AS-039393-RT- 16 19 Company Source Date Sample Gas Span UAMPS GE Frame 7EA Turbine - Combined Cycle 512912024 02 20.45 I I I I I I T I T T I I I t I t I I Analrzer Calibration Cylinder Value (%) 0 10.07 20.45 lnitial Bias Analyzer Response Absolute Difference (%) 0.10 0.13 0.05 System Bias (% of span) 0.49 0.00 System Bias (% of span) 0.49 0.98 System Bias (% of span) 0.49 1.47 System Bias (% of span) 0.49 1.47 Difference (% of span) 0.49 0.64 0.24 Drift (% of span) 0.98 0.98 Drift (% of span) 0.00 0.49 Drift (% of span) 0.00 0.00 (Y,) 0.1 10.2 20.4 Anallzer Response System Response(%) (%)0.1 0.210.2 10.2 Post-test #1 Bias Analyzer Response System Response(%) (T,) 0.1 010.2 10 Post-test #2 Bias Analyzer Response System Response(%) (%) 0,1 0 10.2 9.9 Post-test #3 Bias Analper Response System Response(%) (Y") 0.1 0 10.2 9.9 60 of 8B GP081AS-039393- RT- 16 19 I I I I I I I I I I I I I I I I I t I Post-test tl4 Bias Anallzer Response (Y") 0.1 10.2 Post-test #5 Bias Anallzer Response (Y,) 0.1 '10.2 Post-test #6 Bias Analyzer Response (o/") 0.1 10.2 Post-test #7 Bias Analger Response (Y,) 0.1 10.2 Post-test #8 BIas Anallzer Response (Y') 0.1 10.2 System Response (Y") 0.1 9.9 System Response (Y") 0 10 System Responsevt 0.'t 9.9 System Response (%) 0.1 10 Syatem Response (%) 0 9.9 System Bias (% of span) 0.00 1.47 System Bias (% of span) 0.49 0.98 Syatem Bias (% of span) 0.00 1.47 System Bias (% of span) 0.00 0.98 Syatem Bias (% of span) 0.49 1.47 System Bias (% of span) 0.49 1.47 Post-test #0 Bias Analyzer Response Syatem Response(Y,) (%)0.1 0'1o.2 9.9 Drift (% of span) 0.49 0.00 Drift (% of span) 0.49 0.49 Drift (% of span) 0.49 0.49 Drift (% of span) 0.00 0.49 Drift (% of span) 0.49 0.49 Drift (% of span) 0.00 0.00 6A of 88 GP081AS-039393-RT- 1619 Post-test #10 Bias Analper Response System Response (Y") 0 10 (%) 0.1 10.2 (%) Post-test #{2 Bias Analper Response System Response (Yo) 0.1 10.2 System Bias (% of span) 0.49 0.98 System Bias (% of span) 0.49 49.88 System Bias (% of span) 0.49 49.88 Drift (% of span) 0.00 0.49 Drift (% of span) 0.00 48.90 Drift (% of span) 0.00 0.00 I I I I I I I I I I I I I I T I t I I Post-test #11 Bias Analper Response System Response (%) 0.1 10.2 (%) 6E of 88 GP08 1AS-039393-RT-1619 I I I I I I I I I I I I I I I I I I I Company Source Date Sample Gas Span UAMPS GE Frame 7EA Turbine - Combined Cycle 512912024 NO, 21.7 Anahzer Galibration Cylinder Value (ppm) 0 11.78 21.7 lnitialBias Analper Response (ppm) 0 11.8 Analper Response Absolute Difference (ppm) 0 11.8 21.7 (ppm) 0.0 0.0 0.0 System Bias (% of span) 0.00 0.00 System Bias (% of span) 0.00 0.00 Syatem Bias (% of span) 0.00 1.38 System Bias (% of span) 0.00 1.38 Difference (% of span) 0.00 0.09 0.00 Drift (% of span) 0.00 0.00 Drift (% of span) 0.00 1.38 Drift (% of span) 0.00 0.00 System Response (ppm) 0 11.8 Post-test #1 Blas Analper Response Sptem Response(ppm) (ppm) 0011.8 11.8 Post-test #2 Bias Analper Response Syatem Response(ppm) (ppm) 0011.8 12.1 Post-test #l Bias Analyzer Response System Response(ppm) (ppm) 0011.8 12.1 69 of 8B GPo8 1AS-039393-RT-1619 Post-test #4 Bias Analyzer Response System Response I I I I I I I I I I I I T I I I I t I Analper Response System Response (ppm) 0 11.8 Post-test #5 Bias (ppm) 0 't 1.8 Post-test #6 Bias (ppm) 0 11.8 Post-test #7 Bias (ppm) 0 11.8 Post-test #8 Bias (ppm) 0 11.8 Post-test #9 Bias (ppm) 0 11.8 (ppm) 0.1 12.1 (ppm) 0 12.2 (ppm) 0 't2.1 (ppm) 0.1 12.2 (ppm) 0 12.2 (ppm) 0 12.2 System Bias (% of span) 0.46 1.38 System Bias (% of span) 0.00'l.u System Bias (% of span) 0.00 1.38 System Bias (% of span) 0.46 1.84 System Bias (% of span) 0.00 1.84 System Bias (% of span) 0.00 1.84 Drift (% of span) 0.46 0.00 Drift (% of span) 0.46 0.46 Drift (% of span) 0.00 0.46 Drift (% of span) 0.46 0.46 Drift (% of span) 0.46 0.00 Drift (% of span) 0.00 0.00 Analyrzer Response System Response Analyzer Response System Response Analper Response System Response Analper Response System Response 79 of 89 GPo8 1AS-039393-RT- 1619 Post-test #10 Bias Analyzer Response System Response (ppm) 0 1 1.8 (ppm) 0 12.1 System Bias (% of span) 0.00 1.38 System Bias (% of span) 0.00 54.38 System Bias (% of span) 0.00 54.38 Drift (% of span) 0.00 0.46 Drift (% of span) 0.00 55.76 Drift (% of span) 0.00 0.00 Post-test #11 Bias Analyzer Response System Response (ppm) 0 1 1.8 (ppm) Post-test #12 Bias Analper Response Sptem Response (ppm) 0 1'1.8 (ppm) 74 of 8B GPo8 1AS-039393-RT- 1619 Company Source Date Sample Gas Span UAMPS GE Frame 7EA Turbine - Combined Cycle 512912024 co 25.3 I I I I I I I I I t t t t I t I t I t Analvzer Calibration Cylinder Value (ppm) 0 12 25.3 lnitial Bias Analyzer Response (ppm) 0 11.9 Analger Response Absolute Difference (ppm) 0 11.9 25.3 (ppm) 0.0 0.1 0.0 System Bias (% of span) 0.40 0.79 System Bias (% of span) 1.19 1.19 System Bias (% of span) 1.19 0.00 System Bias (% of span) 1.98 0.00 Difference (% of span) 0.00 0.40 0.00 Drift (% of span) 1.19 0.40 Drift (% of span) 0.00 1.19 Drift (% of span) 0.79 0.00 System Response (ppm) 0.1 11.7 Pre-test #1 Bias Analyzer Response System Response(ppm) (ppm) 0 0.311.9 11.6 Post-test #2 Bias Analyzer Response System Response(ppm) (ppm)0 0.311.9 11.9 Post-test #3 Bias Analyzer Response System Response(ppm) (ppm)0 0.511.9 11.9 72 of 8A GP08 1AS-039393-RT- 16 19 t I I I t I I t I I I I I I I I I I I Post-test #4 Bias Anallzer Response System Response Analper Response System Response (ppm) 0 1 1.9 Post-test #5 Bias (ppm) 0 1 1.9 Post-test #6 Bias (ppm) 0 't 1.9 Post-test #7 Bias (ppm) 0 1 1.9 Post-test #8 Bias (ppm) 0 1 1.9 Post-test #9 Bias (ppm) 0 1 1.9 (ppm) 0.3 11.8 (ppm) 0.2 1 1.8 (ppm) 0.3 11.8 (ppm) o.2 11.7 (ppm) 0.1 11.7 (ppm) 0.2 11.7 System Bias (% of span) 1.19 0.40 System Bias (% of span) 0.79 0.40 System Bias (% of span) 1.19 0.40 System Bias (% of span) 0.79 0.79 System Bias (% of span) 0.40 0.79 System Bias (% of span) 0.79 0.79 Drift (% of span) 0.79 0.40 Drift (% of span) 0.40 0.00 Drift (% of span) 0.40 0.00 Drift (% of span) 0.40 0.40 Drift (% of span) 0.40 0.00 Drift (% of span) 0.40 0.00 Analyzer Response System Response Analyzer Response System Response Analper Response System Response Analyzer Response System Response 76 of 8A GP08 1AS-039393-RT- 1 619 Post-test #10 Bias Analyzer Response System Response I I I I I t I I t I T I I t I I I I I (ppm) 0 11.9 (ppm) 0.1 11.7 System Bias (% of span) 0.40 0.79 System Bias (% of span) 0.00 47.04 System Bias (% of span) 0.00 47.04 Drift (% of span) 0.40 0.00 Drift (% of span) 0.00 46.25 Drift (% of span) 0.00 0.00 Post-test #1'l Bias AnalSzer Response System Response (ppm) 0 11.9 (ppm) Post-test #12 Bias Analper Response System Response (ppm) 0 1 1.9 (ppm) 74 of 86 GP08 1AS-039393-RT- 1619 N02 (ppm) I I I I I I t I I t I I I I I I t I I MONTROSE AIR QUALIry SERVICES, LLC. 6823 South 3600 West 801-266-7111 Spanish Fork, Utah 84660 Plant Source Date Run NO2 Converter Gheck: UAMPS Nebo Power Station GE Frame 7EA Turbine - Combined Cycle 512912024 Post NO2 Conversion 0.60 % Date and Time 512912413:56 13.3 512912413:57 13.3 512912413:58 13.3 512912413:59 13.3 512912414:00 13.3 512912414:01 13.3 512912414:02 13.3 512912414:03 13.3 512912414:04 13.3 512912414:05 13.3 512912414:06 13.3 512912414:07 13.3 512912414:08 13.3 512912414:09 13.3 512912414:10 13.3 512912414:11 13.3 512912414:12 13.3 512912414:13 13.3 512912414:14 13.3 512912414:15 13.3 512912414:16 13.3 512912414:17 13.3 512912414:'18 13.3 512912414:19 13.3 512912414:20 13.3 512912414:21 13.3 512912414:22 13.2 512912414:23 13.3 512912414:24 13.2 512912414:25 13.2 Average: 0.60 78 of 8d GPo8 lAS-039393-RT-1 619 liaklog ou( world more trodu(thre ffi unde Gas & Equlpmenr tnc' f*'^";##"li;.',H Tet:323'58&2154 Far7t4-642'6589 I I I I t I I t I I I I t I T I I I I 'POvP P: fZoze DocNumbar: 561086 1. 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Alameda Street LoBAngelos CA90058 Tel: 3?3-585-21tfFa* 7146426689 PGt P lD: F22023 Ft Datsolnlr'?]oz3 Lor rt mDcr 7008cgolfl)acrthtuswddute| ra @A5so Cylhdet Pns,/.no errd yair?ro: 2000 lsto 1Sl n3 GM|S / NO29287 20.00 ta lo.@ % oeto,n028 SRM ?88rs /7'l€-t9, FF22B31 20.u3%t$.a?lq.oullna?l DocNumbor: 533914 C erlifrc Ai on I nfo r m atio n :CortiticatlonDato:0210812023 lerm..g6Months Explntlon Date: 02108n031 Thls qindu sit Edllbd sc6{dln9 to lho 2ol2 EPA Tre8bflv Prob@|, Do{trml ,EPe{00n-1253r. uilngproodn G-1, urcrrhlot.bon b .ogrEsd 8t ablolrto sxpEndsdmrlrlnty c ! Lvd ol stldsm o, spProxbmbly sltla wth e cdtrig! iaaior k r 2. oo Not u* nu simjaJ?'i.o^ f" f""j ,ian r d'ripdG. - - *.- coz E Po.E lm boq mdod ,of orygm lR B@dcnlng r[6rt 02 Epo@ hlvo bm @rerrd br co2 htdf!8n6" Analytical Dato:(R=Rar@ro Srrrrdrrd, Z2Zem GEr, C=cN CwtcMrto) LOEPI(6 PROI'O UTHS' '2T1 S T{OUSTRIAL PKWY PROVO UT84006{136 1. cffiPo,tml: Crton doxtd. RaquatLd Col16lrsuon: t2 %Codbd Conof![oat 11.91 .A Arulfzrd By lrdrumnl Urad:Hoilbrvl 6108 Z)C1s/rwK Antlyt€l ll,.thod: ilDlR . |.!{ ^elupolil Cr6.!lon: 01 n7 n1?ts 0210ar2m3Z O R; 1428 C 1198 Corc:- lt.egR, 1427 Z: 0 C: 11.07 Corc: t.r-s7Z O C: t1.98 8t 1.t28 Cons: ,tl,06 UO& il MlrnT6tArlry: 115? % ComF,a.nE Ory0u R.quorlodCoMtr,,,E 20* C.rtfiodConEnt![oni 20.46.rt hr'lmal t &(t S-lelm Orvmst 0E S/N 7MB2O2ilAAo@CAtAmudElMothod: Pammrgn.fc Llif Mulpoht CdlbElbn: O1/27f2023 22 O R: 20.0 C: 20.44 Cone 20.46R: 20.89 Z; O C| 20.14 Coe: 20.45Z O C: 20.45 R: zOJO CoE 20,{o UOtf: * t.eTetA$.tE 20A6 % RoLDncoSiudrrd: TypcrCl,fndor* GMls'CCTTGSSO CoEntrluon / U@rtotnty, fi20 {.OZ .n. 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Alatmda Steet Los Angelsa CA 90058 Tel: 3?3€85.215'l Fax: 7l4d{it{689 PGVPID: FXNU I I I I I t I I I t I I I I I I I Catuaql& Ofialnformdoa LCEPKG PRCA'O UT }I!II2II S hIDUATRIAL PI(WY PROVO UT84flr&819{l Cdfi,b tuj,,E Drrc; o,,l0(t2024 Ltu ffiirltartu7276STlB Prr, l&rrr$tr Nl NO'|2MFAS G.tdoftlf,t PO Nut rben 807n1gl fl arlb: Ixl'tg/:&la Lorfllf|tlc 7(x!84{ngB C)ilners0/4r e otdtt AS CGA 8o{l CyMt Pd,ssea' afid yo,,/rrlo: 2m0 pdg 1'10 lul For Reference Only: Nox 11.81 ppm Cerfrficatbn fnformation; Ceftiftca;tlon Date:o4lo4l2O24 lerm.' 36 Months Expirafron Date: O IUDOT R.trnno8trndrd: Typo/cy{tdor* GM|S/DTUXE!0S ComnHbo / Unsrtdnly: 20.9 pPm rO: Ppm Eglt!0on D.b: 05/0t12020 Ttl€rbl. tD: SRM r/ SsmFl! *, qrhdclA 2020., flr-el7 / FF3l891 SRM Conantatbn / t oo.rfdrly: i&0e ppm rJo.lS Fr sRM Eblr.ion IIb: 1ui21nfrB c.ilfiod By ThLcyffirraortildacco]dnOtoth€2012EPATnea!fitytuocol,DoqlmfitrEP^.0o0rR-12/531,tEhgRoc.dr^5eGl.UrE tdntyrlov!bo|p,lls€desSofrbltfrdedmefihfy rtr lcvd ol mlucu-ol Ilprdndy 96tt glth a 6arngr bcb. k . Z Do Not UE thb St nd.td f PmE b Ls ttm tm P$O. Anatytical Dda:t. Cor@rrarf (R4albruncc Stanerd, zaorc Gag. C.Gae Caxfdt|€.) illtlo orld. R!$Et dconontilUm: '12pDm Csrtllsd Conontldm: 11.78 PPm h.fum0t Ur.d Th.m Ellctm 42LLS S/N 1G1O845077 Amty{hdfa.0tod: ChJlllurhulc. t,d rirEpoht CtlD.ltlort 0g/16/:m24 t sEly0cd mdD.L fipby.d rd b co.rCab b tha utd .f fh. .p.ctlo mt B p..lbm.4 sr mCG m mmtrly or rtpE ldoo B b lh. elrblly ol lha ta of lh. illrmrlo ,or sV ptrp6!. otth.ud05ffilllrdondfthodhlarhrrca.dfiaE ul.b[dEdforprclrl&Ea!.hlnfutmfon. 1Ot1 CyllnderNumben DToo5tzt6 Expanded Uncertainty 11.78 ppm Bahnco Nftrlc oxide Nltrogen ProSpecEZ Cert sRME:gLrion Dab: * 0 R: 20.9 C: 11.70 Coltc 11.79 * 20.9 z: 0 c'. 11.n Conc 11.7 Z O c, 11.71 & 20, C$c ll.z UOg: ppflt L0nTslA...!,: ll.lt pgn RtrtAndr|rb D.tr: otb o3ul * o i:'--2os cr 11.76 coao: 'ti,z8 R: 2o.0 Z 0 c: 11.78 cffc ,l1.4 Z o C: t1.77 R 20.8 Cnq 11.79 uoL: Dtrn Imf6tAsry: 11,79 PPm 79 ot 86 cP08 1AS-039393-RT- 1619 liaklng ouj norld more productlye DocNumber: - 5671 74 Undo Gas & Equipment lnc, 5700 S. Alameda Street Los Angelss CA 90058 Tel: 323-585-214(rax:71&2a689- ""-" PGYPID:FA20?A I I Cuiloma &, Orda Inlomtador, LGEPXG PROVO UT HSlz.tl s tNousTRtAL PI(WY PROVO UT846066138 Co rdtate I auan6 Dato : OAI c4nu24 Udo ofdqNu&rctzla}sag Prtilurrbsr Nl NO23t E-AS Cuslomer PO ,\mbo| 8/J712flSB FilD€e,:@t14tm21' LotNwttEr. TmSE{N5O1 CyilndergwAOd* AS CGA060 Cylindet PNn ud Volwe: 2W *g l/fo n3 Gllls / ND87'B 47.4D8fi,0.2pDm 1W21n025 PRM / C1765710.01 I NPE,<1321323 50,04 ppm / iO2O pprn 1ltnta}?z S.sdd Andyrlt h, O.t t 0 R: 47.5 Cr 21.7 Cone 21.7R: 47.4 Z . O Ct 21.A Conc 21.8L O C: 21.E k 47.1 Corc: 2.t.8 UO}l: ppm Uun TotArlF 21.A ppm ,€ffi I I I I t I I t I I I I I I t t I zjoR:*, OA zl zjoc: UOI: ppm Ct .21.7 Ci 21.8 R: 47.3 X{n TdtA3xy: 02[23n024 21.7 21.6 21.7 21.7 ppm Gonc: CGs Conc: Anayed Ay Codn.d By .Exprrauon uare: $nq2o27 Cylinder Numbec Cc7553Os Nltric oxide Nltrogen Concentration For Refereace Only: C e rtifi c at i o n I nfo r m atio n :Iarm.' 36 Months Expiration Date: O3lO4l2O27 Thl8 Gyrrd'r wa €roff'd a@rdlno to tho 2ol2 EPA Tmablity Proto@|, ooofiEnt tEPA€oo/RJzs3l, uhg-p@duB Gi. Unartsinty lboE b cr9EElod u .b.o[ti. 60grd.dunqtdlttv at ! lcEa of qild€E ol sppErmidy 9594 wlth ! iwcng. iacrr t . 2 Do Not us tils studsrd t, p|um lr t6 ths ,l o0 pslc. ProSpec EZ Cert ffiffi 47.4 0 21-7 NOx 220 ppm Ce rtifr cation D ato : O3l M12024 AnAlVtiCAlDgtA: (R-Re,brEmsrrrdard,Z-zmcas,c.C6curthl,ate) 1. cmporJrr il&,lc orkt R.rffis stlrd.td: Typ! / cyflndc, *:Roq6stBd Concsnbstm 23 ppm CorEontratoa / Unceialnty:CodlfrodcmentEtht Z1.l ppn E([llEtjoo Dat6:loslrumsnt ussd: ThornD Elodron 42l-ls sN 1 0308/16077 Tncr.bt !o: sRIu # / srmce * / cyftd.r *:AmMlcal M.lhod. Ch.,rlUmlnffi SRM Coh6nt rua / Un@i.kty:l.rstMdtipohtcdryain u)13tit124 sRi,t Exptdijo Dsr!: mly06l mothod sBplovld End b Brd;t! !o oi exterl t oe ipiono oalia pcrformca, m mr. ;rilmt; Dprg..nbton s b h. lutrbltty ot rE u.€ ot oo trdormdon to. eny pupos. ot hc @ of [F mm.ton mHrrd h6ah ucoco up'tog rrt8b0"tr"d tordrtdhi;"tr-dbmr"ffi'--'- " -- - pago I ol,l 80 of 86 cP08 1AS-039393-RT- 1619 I I I I 00011295 Caslorna & Met laformdon:' PRN(AIR PKG PTIOENIXAZ HS 3918 W LINCOLN ST PHOENIX |z 85009- Praxair Order ifunbda 70432096 Customer P. O.|fuit*it: Cus tom er Rcfer enc e Numdet Prarrlr 5700 Sduth Alamcda Strcct hA"g"l..,CA 90058 Tet (323) 585-2154 Fa*(714) 542{689 PGVPID: F22017 Fllw* 12,/1m17 Partlffi* Nl @l2MErAS' L. ttntu 700867&t503 cyltdo&fl;&.onta: As cGA35{, QtttrtcPrxni&Yolmc 2000Pilg 140drtl.t I I I I I I I I I I I I I t Certifu tl Co ncentrstion : Explraflon Date: 1il6n025 Cyllnder Number: SASi86 NIST Traceable Analydcal UncertalntY: 12.0 ppm CARBON MONOXTDE !'O'7 % Batance NITROGEN cttifcdanlnformatioi: certificatton Date: '1z[f12}17 rerm.' 96 Mcnths ryy ?y: . 1'21612025 Ttrtscytnaeilarascedfledaccordingtothe2ol2-EmrraceabilttyPotocol,Document#PA.600r&12531;uslngProcadur€G1. DoNot Use thls Standard f Pressure ls less than '100 PSIG' AnoMcalDala: .(R-Relenndgend€'d,Z4ercGas'c=eaeMldats) 7, coraloncttE CaRBOil rc[OxrdE -: ' Requ6isd Conc€tita6on: 12 PPir c€rtfiEd co0d|Eatlon: 12.0 PPmlEfiumnturad: HorlbaVIA-610 a/N 616876016 Anafydcal Mothod: NDIR Iastt/tltpolntcallbra[m: l1nql'2017 f,damo€isndedType: GMIS '''':'''"-' Rcf.9d;Cyllndcr#: cc341o74 R.t std.com 9.039PPm Rcf. Std, Traesble to sRM # : 16Tlc SRMSEmPIg#: $'t42 sRMcrlnderf: CAL0'16337 RElAnrtYtl. Drrr: D.t : lUBl'lOl7 Z: o R: 97.1 c: 117 Com:.3 11.972 k {12 Z 0 c:"' 117 cone"r 11'972 z: o c: 117.3 R: 97.1 Conc' 12.003 uolt: ptrn '- iloan:IaitArslp"n 11'982ppm "' Analyzed by: lnform[oh contalnBd herdn har been pr8per€d at ]our roqu6t by quallfiEd €rPsr$ uihln Pranlr Dlgilbuton, lnc.Whlle tfl! b8tlovB hat he lnlbrnsdon ls ac.utab wllhln ho llrlt8 of the malyoal I&iLnafng ltr* tny uri of ttre lnb-matli:n lt 8t lho sls dl$Eton and dsk of tho uss'*l hmln e@d the tu BlabltthEd for Dmvtdilu sucfi lniortEtlon. on I !o lha rultrblllty of the uE of lh! ffibn[dil ,or my pttr?6. Tho ln no ewni shall lha llabillty of PraEh Dlstlbu0on, lnc., rdslng out ot tha * Ji6" im*aUm on dnsd hareln cmcd tha b. 6labtlthed for pmvtdilxg srJcfi ln orrEtlon. cP08 1AS-039393- RT- 1 5 1 9 lnfo'rlg[oh contalnBd hordn het bosn papet€d at ],ow ruque8l Dy qBlmil E)Pw uorrr rl matirodr anPtoyaA anO lr onplolg b.lil€ ;xtsnt of tho spcdffo trdy86,Plrbmd' m makr fnforrnton tt oi*"0 wttr Urc irnOeadnahg that lrry ulo ot tht lnlbnEtlon lt 8t lhs mle dls ssond AmlFlt D!tr: Zi O R: \oi. c: 0 R:OZ0":Cl-r!0' Z O, C: 0 ' R:-'-.0 UOM: ppt :" t'Moan:Tccl 0'0'o o ppm 81 of 86 lilil(rlq our t"utld more p(odu(live Docllumb.r: 55{iI76 I ILindo Gaa & EqulPmont lnc 5700 S. Al.m.dr Strtat Los Angolec CA9005E Tol: 323{8li-2154 Fax 714{{26680 PGVP lD: EI2OZ3 CERTIFICATE OF ANALYSIS / EPA PROTOCOL GAS t I I I I I I I t t T I I I t I I CertifrcAion Information: Ceililication Date:08tO1t2O2Q. Ierm; 96 Months Expinrion Oare; 08/01/2031 Thb 6/,f0duw Bl0tt d.sdtng to Ura mt2 EPAT@UUy Proio@t, Ooumntrcpl+oon-f2r531, ulrE.tto€dm G't. UHi.lnty.bos borpEsld u.blolutc op€nded u-rlirf,ty .t r tmt of mrdlm -ot app@lrnrtdy 05ta 'if0l r 4fl6g. Ldor k r 2. Oo t5t UE. thb SlDd.td It PrusE It 16 th.n too PSIG' Custo rrq & Oda f afort atlo t LGEPKO PFOI'O UT HSr2llslNousTRl LPl(wY PRO\aO Ur 418066i3€ A,rllf4d BY Aill@lo lsuffi DDto: O0n1n0zJ Llnde N,Nw'6,eE 72:5iDg7 PrdrrrurflDr Nl CO?jME+S CudqEr PO wrDDor 80GlZ2,t6 F, D.It: gf fi2nqB tol rvunbc 7@*i:120804 Cylhdcrsw&Ou,tu:rA CGA3sll Cy,tndor Paffi ,N yo&rnti 2d)0 Flg tao tui Giils / I,T000E388 25J0 ppm io.t.l PPD orl9f?030 2rs5. r 5&E3a, FFt686 24-Ol2 pp6 , d.029 PPM uEnno8 Anglydcol DgU.' (R--Rolnr,@ sto''doltt, z'Zffi G!t' ccts cladldrb) I . Com,Dml: Cribon mdorld. R.rcDnB Slrnd.rd: .rlq, I cyl,nda * RlquELd Co.rntrdm: 5 prri Cartld CoEiHm 26J PFrt ![ttMt t rod: Horlbr VIA€10 gN t6878015 ABryriol MotEd: ND8 Lan MunDoltt Cdb.rt of, : ol 28tm2i Gornt tuo / lrnE t lniy: ErPlolbn Otb: Tr6.Urto: sRx lrs.dPSt/Crhd.rl: sfr,M Cd6nlrdld, t nort ht)[ SRAI EtCntloo D.t.: C.rrm.d By D.l. 7d- 0- RO ZO t O C:- 0 ConB 0 z: o C: 0 Conc: 0 c:OR:0conco Uol,t: ppm tLln T€a&trYl PFn - -'::-.:'(-' 30ch!nr Gmng lnfqrflliltfitrtmtf hmhhs!.!opBparddrurr.quf,tbysrrtr.roryarrrwlhln Und.G8&Equhmntlne WhU!sb.gm0lsttho&rlqmthnb'@Etrwlthhih'lnitsolue smlyflcal mt,lodr mployldara 15 drolab b ucslrnl of tho rPacfitcet 6 prfu(Dd, l! mro rc'rinu*yor rcpltutstm s tolhc rubbmy otlh! l8! ot0u Homltbn tut uy pupoJo olthc mdlh. hffiim 6fit brd h.oiD Md 0ltb...ubf$.d k Prwldhg tuch lnttrndbrL Ptoa 1 ol l CyllnderNumbon DTSOOEg7S Expanded Uncerlalnty 25.3 ppm Carbon monoxlde t 0.2 PPm Balance Nlllogen PrcSpecEZ Cert 2-i,3 - 2 25.3 D16. 2t C! 25.b coEo C1 252 Corc:25J Il: 25 conc 2iOkR: 25 Z;z;oc: UoL ppo ll{n Tat Asryl 263 PPn 82 of 86 cP08 1AS-039393-RT- 1 6 19 Appendix C.3 Accreditation Informatio n I Certifications 89 of 88 GP08 1AS-039393-RT- 1519 I ,' T toHI gHT =e1 IIII oBEIIIIIttItI +iq)trq)uodLLoqoQq)p(BUFJLiLIAIq)Lq) lJ\IJq) \J$(.)o(adLqooLa,oB13q)L()Idu) FF{ o)o'Eoar )-:bP - E 33 x !u S R Su cc D ;- i o -c o X: E o N ;o _ o > \# - L .. fr t o -d \ ) )6 Xz h EX o o E< E : ^- o. 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Name: Cheyney Guymon Title: Field Project Manager Region: Great Plains Region, Utah Office Email : chguymon@montrose-env.com Phone: 801-362-4978 Name: Title: Region: Email: Phone: Beckie Hawkins District Manager Great Plains Region, Utah Office behaw ki ns@ mo ntrose-env. com 80L-794-2950 UTeH OTPRRTMENT E NVr R o N ME NIA!_QUAL! rY JUL - I 2024 DIVISION OF AIR OUALITY 86 of 89 GPo8 1AS-039393-RT- 1619 UAMPS Nebo EU#2 RATA RM 3A, 7E, 10, & 19 (tested 5-29-2024) Reference Methods 2, 3A, 6C, 7E, 10, & 19 Source Information Company Name UAMPS NEBO Power - Combined Cycle Company Contact:Scott D. Jeffryes Contact Phone No.801-925-4003 Stack Designation:HSRG Stack Test & Review Dates Test Date:5/29/2024 Review Date: 12/2/2024 Observer:Not Observed Reviewer:Rob Leishman Emission Limits Emission Rates SO2 NOX CO SO2 NOX CO lbs./MMBtu lbs./hr. ppm 5.0 10.00 4.591 8.349 %O2 Correction as a whole #15.00 15.00 Test Information Stack I.D. inches As ft^2 Y Dl H @ Cp Pbar Pq (static) Ps Stack Pressure 197.00 211.670 0 Contractor Information Contact:Andrew Bruning Contracting Company: Montrose Air Quality Services Address: 990 W 43rd Avenue, Denver, CO 80211 Phone No.: 303-810-2168 Project No.: 8710 Division of Air Quality Instrumental Reference Methods - Gaseous Measurements Round Method 19 - F factors for Coal, Oil, and Gas Fd Fw Fc dscf/MMBtu wscf/MMBtu scf/MMBtu Diluent F factor used O2 CO2 Anthracite 2 Bituminous 2 Lignite Natural Propane Butane 10100 COAL OIL GAS 9780 9860 9190 8710 8710 8710 10540 10640 11950 320 10610 10200 10390 1970 1800 1910 1420 1040 1190 1250 Wet CEM Correct For O2 CO2 Interference w/CO Yes Yes Yes UAMPS Nebo EU#2 RATA RM 3A, 7E, 10, & 19 (tested 5-29-2024) Company UAMPS NEBO Power - Combined Cycle Point Source HSRG Stack Test Date 5/29/24 Start Time End Time Run CO PPM NOx PPM NOx lb/MMBtu O2 % Load MW Gas Flow 100 SCF Headers Here Headers Here Headers Here Headers Here Headers Here Headers Here 8:26 8:47 1 9 4.49 0.016 14.7 106 7071.2 8:57 9:18 2 8.3 4.5 0.017 14.7 106 7030.1 9:27 9:48 3 8 4.48 0.016 14.7 106 7008.2 9:57 10:18 4 8.3 4.5 0.017 14.7 106 7004.1 10:29 10:50 5 8.2 4.55 0.017 14.7 106 7008.2 11:01 11:22 6 8.1 4.49 0.017 14.7 106 7001.3 11:32 11:53 7 8.3 4.44 0.016 14.6 106 6976.3 12:20 12:41 8 8.6 4.58 0.017 14.9 106 6967.4 12:50 13:11 9 8.4 4.5 0.017 15 106 6956.7 13:20 13:41 10 8.5 4.5 0.017 15 106 6946 11 12 13 14 15 16 UAMPS Nebo EU#2 RATA RM 3A, 7E, 10, & 19 (tested 5-29-2024) Division of Air Quality NSPS Relative Accuracy Performance Specification Test - CEMS Certification UAMPS NEBO Power - Combined Cycle HSRG Stack SO2 Analyzer:Serial No.: CO2 Analyzer:Serial No.: Acquisition System:Serial No.: Acquisition System: Serial No.: Equivalent Emission Limit: Test Date SO2 Dry SO2 Dry SO2 Test Date % CO2 Dry 5/29/2024 RM CEMS Diff RM CEMS Diff RM CEMS Diff 5/29/2024 RM CEMS Diff Run#Start Time End Time ppm @ % O2 lbs./MMBtu lbs./hr. Run# Start Time End Time %c %c 1 8:26 8:47 1 8:26 8:47 2 8:57 9:18 2 8:57 9:18 3 9:27 9:48 3 9:27 9:48 4 9:57 10:18 4 9:57 10:18 5 10:29 10:50 5 10:29 10:50 6 11:01 11:22 6 11:01 11:22 7 11:32 11:53 7 11:32 11:53 8 12:20 12:41 8 12:20 12:41 9 12:50 13:11 9 12:50 13:11 10 13:20 13:41 10 13:20 13:41 11 11 12 12 13 13 14 14 15 15 16 16 Average = Average = Sd Standard Deviation = Sd Standard Deviation = Sd Standard Deviation = Sd Standard Deviation = Confidence Coefficient = Confidence Coefficient = Confidence Coefficient = Confidence Coefficient = RA - Relative Accuracy = RA RA RA - Relative Accuracy = n = 0 0 0 n = 0 or RA of 1% t0.975 = t0.975 = E.L. Relative Accuracy = a For steam generators;b Average of three samples;0 c Make sure that RM and M data are on a consistent basis either wet or dry. 40 CFR 60 Performance Specification 2 For SO2 and NOx Continuous Emission Monitoring Systems 13.2 Relative accuracy Performance Specification. The RA of the CEMSS must be not greater than 20 percent when RM is used in the denominator of Eq. 2-6 (average emissions during test are greater than 50 percent of the emission standard)or 10 percent when the applicable emission standard is used in the denominator of Eq. 2-6 (average emissions during test are less than 50 percent of the emission standard). Up dated January 17, 2006 40 CFR 60 Performance Specification 3 For O2 and CO2 Continuous Emission Monitoring Systems 13.2 CEMS Relative Accuracy Perfromance Specification. The RA of the CEMS must be no grater than 20 percent of the mean value of the reference method (RM) data. 1 percent O2 or CO2. The results are also acceptable if the absolute value of the difference between the mean RM value and the mean CEMS value is less than or equal to 1.0 percent O2 (or CO2). Up dated September 14, 2016 40 CFR 60 Performance Specification 6 For Continuous Emission Rate Monitoring Systems (CERMS) 13.2 CERMS Relative Accuracy. The RA of the CERMS shall be no greater than 20 percent of the mean value of the RM's test data in terms of the nits of the emission standard, or 10 percent of the applicable standard, which err is greater. Up dated January 17, 2006 Ac t i v a t e R u n ? Ac t i v a t e R u n ? Ac t i v a t e R u n ? Ac t i v a t e R u n ? UAMPS Nebo EU#2 RATA RM 3A, 7E, 10, & 19 (tested 5-29-2024) Division of Air Quality Relative Accuracy Test Audit of UAMPS NEBO Power - Combined Cycle HSRG Stack NOX Analyzer:Serial No.: O2 Analyzer:Serial No.: Acquisition System:Serial No.: Acquisition System: Serial No.: Equivalent Emission Limit:5.00 Date NOx Dry NOx Dry NOx Test Date % O2 Dry 5/29/2024 RM CEMS Diff RM CEMS Diff RM CEMS Diff 9/30/2014 RM CEMS Diff Run#Start Time End Time ppm @ 15% O2 lbs./MMBtu lbs./hr. Run# Start Time End Time %c %c 1 8:26 8:47 5.0 4.49 0.018 0.016 #VALUE!1 8:26 8:47 Y 15.0 14.7 0.255 2 8:57 9:18 Y 4.5 4.5 0.0 Y 0.017 0.017 0.000 #VALUE!2 8:57 9:18 Y 14.8 14.7 0.130 3 9:27 9:48 Y 4.8 4.48 0.3 Y 0.018 0.016 0.002 #VALUE!3 9:27 9:48 Y 14.9 14.7 0.204 4 9:57 10:18 Y 4.7 4.5 0.2 Y 0.017 0.017 0.000 #VALUE!4 9:57 10:18 Y 14.9 14.7 0.229 5 10:29 10:50 Y 4.6 4.55 0.1 Y 0.017 0.017 0.000 #VALUE!5 10:29 10:50 Y 14.9 14.7 0.154 6 11:01 11:22 Y 4.6 4.49 0.2 Y 0.017 0.017 0.000 #VALUE!6 11:01 11:22 Y 14.9 14.7 0.154 7 11:32 11:53 Y 4.6 4.44 0.2 Y 0.017 0.016 0.001 #VALUE!7 11:32 11:53 14.9 14.6 8 12:20 12:41 Y 4.4 4.58 -0.2 Y 0.016 0.017 -0.001 #VALUE!8 12:20 12:41 Y 14.9 14.9 -0.046 9 12:50 13:11 Y 4.4 4.5 -0.1 Y 0.016 0.017 -0.001 #VALUE!9 12:50 13:11 Y 14.9 15 -0.096 10 13:20 13:41 Y 4.3 4.5 -0.2 Y 0.016 0.017 -0.001 #VALUE!10 13:20 13:41 Y 14.8 15 -0.171 11 11 12 12 13 13 14 14 15 15 16 16 Average = 4.6 4.5 0.047 0.017 0.017 0.000 Average = 14.870 14.780 0.090 Sd Standard Deviation = 0.18 Sd Standard Deviation = 0.001 Sd Standard Deviation = Sd Standard Deviation = 0.15 Confidence Coefficient = 0.135 Confidence Coefficient = 0.001 Confidence Coefficient = Confidence Coefficient = 0.118 RA - Relative Accuracy =4.00%Relative Accuracy =5.90%Relative Accuracy = RA - Relative Accuracy =1.39% n = 9 9 0 n = 9 or RA of 1%0.09% t0.975 = 2.306 t0.975 = 2.306 t0.975 = t0.975 = 2.306 E.L. Relative Accuracy = 91% EMRA EMRA a For steam generators;b Average of three samples; c Make sure that RM and M data are on a consistent basis either wet or dry. 40 CFR 60 Performance Specification 2 For SO2 and NOx Continuous Emission Monitoring Systems 4. Performance and Equipment Specifications 4.3 Relative accuracy. The RA of the CEMSS shall be no grater than 20 percent of the mean value of the RM test data in terms of the units of the emission standard or 10 percent of the applicable standard, whichever is greater For SO2 emission standards between 0.30 and 0.20 lbs./MMBtu use 15 Percent of the applicable standard; For SO2 emission standards below 0.20 lbs./MMBtu use 20 Percent of the emission standard; 40 CFR 60 Performance Specification 3 For O2 and CO2 Continuous Emission Monitoring Systems 12. Calculate the arithmetic difference between the RM and the CEMSS output for each run. The average of the nine (of more) data sets constitute the RA. 13.2 Relative accuracy. The RA of the CEMSS must be no grater than 1 percent O2 or CO2. 40 CFR 60 Performance Specification 6 For Continuous Emission Rate Monitoring Systems (CERMS) 13.2 CERMS Relative Accuracy. The RA of the CERMS shall be no greater than 20 percent of the mean value of the RM's test data in terms of the nits of the emission standard, or 10 percent of the applicable standard, which err is greater. Up dated January 17, 2006 Ac t i v a t e R u n ? Ac t i v a t e R u n ? Ac t i v a t e R u n ? Ac t i v a t e R u n ? PassedPassedPassed 1501663828Thermo - 42ILS - ANSSPCA Thermo - 48I - AGPCA 1501663829 UAMPS Nebo EU#2 RATA RM 3A, 7E, 10, & 19 (tested 5-29-2024) Division of Air Quality Relative Accuracy Test Audit of UAMPS NEBO Power - Combined Cycle HSRG Stack CO Analyzer:Serial No.: Acquisition System: Acquisition System: Serial No.: Equivalent Emission Limit:10.00 Date CO Dry CO Dry CO 5/29/2024 RM CEMS Diff RM CEMS Diff RM CEMS Diff Run#Start Time End Time ppm @ 15% O2 lbs./MMBtu lbs./hr. 1 8:26 8:47 Y 8.95 9 0.05 0.020 #VALUE! 2 8:57 9:18 8.05 8.3 0.018 #VALUE! 3 9:27 9:48 Y 8.01 8 -0.01 0.018 #VALUE! 4 9:57 10:18 Y 8.39 8.3 -0.09 0.019 #VALUE! 5 10:29 10:50 Y 8.16 8.2 0.04 0.018 #VALUE! 6 11:01 11:22 Y 7.96 8.1 0.14 0.018 #VALUE! 7 11:32 11:53 Y 8.33 8.3 -0.03 0.019 #VALUE! 8 12:20 12:41 Y 8.57 8.6 0.03 0.019 #VALUE! 9 12:50 13:11 Y 8.54 8.4 -0.14 0.019 #VALUE! 10 13:20 13:41 Y 8.53 8.5 -0.03 0.019 #VALUE! 11 12 13 14 15 16 Average = 8.38 8.38 0.00 Sd Standard Deviation = 0.08 Confidence Coefficient = 0.063 RA - Relative Accuracy =0.80% n = 9 0 0 t0.975 = 2.306 E.L. Relative Accuracy = 84% a For steam generators;b Average of three samples; c Make sure that RM and M data are on a consistent basis either wet or dry. 40 CFR 60 Performance Specification 4 For Carbon Monoxide (CO) Continuous Emission Monitoring Systems applicable emission standard is used to calculate RA. 40 CFR 60 Performance Specification 4A For Carbon Monoxide (CO) Continuous Emission Monitoring Systems 13.2 Relative accuracy. The RA of the CEMSS must be no greater than 10 percent when the average RM value is used to calculate RA, 5 percent when the applicable emission standard is used to calculate RA, or within 5 ppmv when the RA is calculated as the absolute average difference between the RM and CEMSS plus the 2.5 percent confidence coefficient. 40 CFR 60 Performance Specification 6 For Continuous Emission Rate Monitoring Systems (CERMS) 13.2 CERMS Relative Accuracy. The RA of the CERMS shall be no greater than 20 percent of the mean value of the RM's test data in terms of the nits of the emission standard, or 10 percent of the applicable standard, which err is greater. Up dated January 17, 2006 13.2 Relative accuracy. The RA of the CEMSS must be no grater than 10 percent when the average of the RM value is used to calculate RA or 5 percent when the Passed Ac t i v a t e R u n ? Ac t i v a t e R u n ? Ac t i v a t e R u n ? Thermo - 48I - AGPCA 1501663829 UAMPS Nebo EU#2 RATA RM 3A, 7E, 10, & 19 (tested 5-29-2024) Division of Air Quality NSPS Relative Accuracy Performance Specification Test - CEMS Certification UAMPS NEBO Power - Combined Cycle HSRG Stack Average Emission Dry SO2 NOX CO lbs./MMBtu 0.017 0.019 Average % concentration lbs./hr.CO2 O2 ppm corrected for %O2 4.59 8.35 14.88 Run 1 Enter O2 or CO2 Dry SO2 NOX CO CO2 O2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.83E-02 2.01E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.963E-07 6.553E-07 lbs./hr.14.96 ppm corrected for %O2 4.95 8.95 15.00 Run 2 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.66E-02 1.81E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.534E-07 6.020E-07 lbs./hr.14.83 ppm corrected for %O2 4.50 8.05 14.70 Raw Value Run 3 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.77E-02 1.80E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.815E-07 5.918E-07 lbs./hr.14.90 ppm corrected for %O2 4.79 8.01 14.70 Raw Value Run 4 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.73E-02 1.88E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.663E-07 6.172E-07 lbs./hr.14.93 ppm corrected for %O2 4.68 8.39 14.70 Raw Value Run 5 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.70E-02 1.83E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.640E-07 6.081E-07 lbs./hr.14.85 ppm corrected for %O2 4.61 8.16 14.70 Raw Value Corrected For Cal. Drift Raw Value Corrected For Cal. Drift Corrected For Cal. Drift Corrected For Cal. Drift Corrected For Cal. Drift O2 CO2 Clear lbs./MMBTU UAMPS Nebo EU#2 RATA RM 3A, 7E, 10, & 19 (tested 5-29-2024) Division of Air Quality NSPS Relative Accuracy Performance Specification Test - CEMS Certification UAMPS NEBO Power - Combined Cycle HSRG Stack O2 CO2 Clear lbs./MMBTU Run 6 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.71E-02 1.79E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.675E-07 5.930E-07 lbs./hr.14.85 ppm corrected for %O2 4.64 7.96 14.70 Raw Value Run 7 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.71E-02 1.87E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.640E-07 6.183E-07 lbs./hr.14.88 ppm corrected for %O2 4.63 8.33 14.70 Raw Value Run 8 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.62E-02 1.92E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.385E-07 6.383E-07 lbs./hr.14.85 ppm corrected for %O2 4.40 8.57 14.70 Raw Value Run 9 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.61E-02 1.91E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.306E-07 6.308E-07 lbs./hr.14.90 ppm corrected for %O2 4.37 8.54 14.70 Raw Value Run 10 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)1.60E-02 1.91E-02 E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft 5.327E-07 6.383E-07 lbs./hr.14.83 ppm corrected for %O2 4.34 8.53 14.70 Raw Value Run 11 Dry SO2 NOX CO CO2 O2 Atomic Weight 64 46 28 lbs./MMBtu (O2)E=Cd x Fd x (20.9/(20.9-%O2d)) lbs./MMBtu (CO2)E=Cd x Fc x (100 / % CO2d) lbs./cu.ft lbs./hr. ppm corrected for %O2 Raw Value Corrected For Cal. Drift Corrected For Cal. Drift Corrected For Cal. Drift Corrected For Cal. Drift Corrected For Cal. Drift Corrected For Cal. Drift UAMPS Nebo EU#2 RATA RM 3A, 7E, 10, & 19 (tested 5-29-2024) Calibration Error Test Test Date May 29, 2024 O2 CS - Cal. Span 20.45 Units % Cylinder No. Expiration Date Cal. Gas CV- Certified Concentration CDir or CS - Measured Concentration Difference ACE Eq. 7E-1 Analyzer Cal. Error Status Low-level 0.00 0.10 0.10 0.49% Passed Cal. Mid-level 10.07 10.20 0.13 0.64% Passed Cal. High-level 20.45 20.40 0.05 0.24% Passed Cal. % of Span Sec. 8.2.1 Cal Gas Verification 0 to 20% of CS - Cal. Span Low-Level 0.00% 40 to 60% of Cal. Span Mid-level 49.24% 100% of Cal. Span High-level 100.00% Test Date CO2 CS - Cal. Span Units % Cylinder No. Expiration Date Cal. Gas CV- Certified Concentration CDir or CS - Measured Concentration Difference ACE Eq. 7E-1 Analyzer Cal. Error Status Low-level Mid-level High-level % of Span Sec. 8.2.1 Cal Gas Verification 0 to 20% of Cal. Span Low-Level 40 to 60% of Cal. Span Mid-level 100% of Cal. Span High-level Test Date SO2 CS - Cal. Span Units ppm Cylinder No. Expiration Date Cal. Gas CV- Certified Concentration CDir or CS - Measured Concentration Difference ACE Eq. 7E-1 Analyzer Cal. Error Status Low-level Mid-level High-level % of Span Sec. 8.2.1 Cal Gas Verification 0 to 20% of Cal. Span Low-Level 40 to 60% of Cal. Span Mid-level 100% of Cal. Span High-level Test Date May 29, 2024 NOx CS - Cal. Span 21.70 Units ppm Cylinder No. Expiration Date Cal. Gas CV- Certified Concentration CDir or CS - Measured Concentration Difference ACE Eq. 7E-1 Analyzer Cal. Error Status Low-level 0.00 0.00 0.00 0.000% Passed Cal. Mid-level 11.78 11.80 0.02 0.092% Passed Cal. High-level 21.70 21.70 0.00 0.000% Passed Cal. % of Span Sec. 8.2.1 Cal Gas Verification 0 to 20% of Cal. Span Low-Level 0.00% 40 to 60% of Cal. Span Mid-level 54.29% 100% of Cal. Span High-level 100.00% Test Date May 29, 2024 CO CS - Cal. Span 25.30 10 Units ppm Cylinder No. Expiration Date Cal. Gas CV- Certified Concentration CDir or CS - Measured Concentration Difference ACE Eq. 7E-1 Analyzer Cal. Error Status Low-level 0.00 0.00 0.00 0.000% Passed Cal. Mid-level 12.00 11.90 0.10 0.395% Passed Cal. High-level 25.30 25.30 0.00 0.000% Passed Cal. % of Span Sec. 8.2.1 Cal Gas Verification 0 to 20% of Cal. Span Low-Level 0.00% 40 to 60% of Cal. Span Mid-level 47.43% 100% of Cal. Span High-level 100.00%