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.
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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.
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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
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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
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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
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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.
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Perform Oz, NOx and
CO MTAs
EPA,34,7E,
10, 19
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Table 1-2
Summary of Part 611175 RA Test Results - Nebo EU #2,lilay 29, 2024
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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
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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.
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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
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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
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Thermo Environmental Instruments
EU #2 CO/Oz Thermo Environmental Instruments
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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
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SIGNAL
-F!
.Mffi
BqaffiwfrMCffnqvf,E
wmmffi4vlE
tl,
%f'l\'uErcB.rc'MmwffudreVAE
12 of 85 cP08 1AS-039393-RT- 1619
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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
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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
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Table 4-2
Nitrogen Oxides (!b/MMBtu) RATA Results -
Nebo EU #2
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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
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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
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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
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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
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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
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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
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24 of 88 GPoslAS-03s393-RT-161s I
o2
gn
NOr
(ppm)
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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
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Average: 4.9 8.3
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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
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GP08 1AS-039393-RT-16 19
o2
{Ye)
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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
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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
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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)
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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
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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
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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)
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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
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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
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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
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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
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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
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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
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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
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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
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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
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N2
NHs
Ni
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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
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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
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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
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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
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Post-test #11 Bias
Analper Response System Response
(%)
0.1
10.2
(%)
6E of 88 GP08 1AS-039393-RT-1619
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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
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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
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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
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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
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(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)
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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
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'POvP P: fZoze
DocNumbar: 561086
1. CooE,oaac
Ll"a" tr.,o,o' o"rt: {n1DgB
Und! Otdot Ntr*,Df, T2SJ1B1Z"'* -' p* N-o* Nl co6o2oEi\s
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il'rnTutA$rY:
76 of 86 cP08 1AS-039393- RT- 1 6 1 9
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Maxlng uur rvqrl.J
motc Drlrductrye
Co dn@aa lsrm D tu: OZI 1 On0/Z3
l-b.la O^lqNm'.E 7alZ831A
P.rl Nun brr Nl CD12O23FAS
CuEld,ror lO Nuno,c,: 8lr3354i t
Llnde Gao & Equlpmont !nc.
5700 S. 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. Er(ptlttd Drt.: 01fZtF2(80
Tncortl, !r: .SRlr, # / Samptc t / Clhds {* NTRM / ll/A / CC7260S5
CRM Co,Ednrooi / Une.trlnty: tg3t!. / rO.OSta
SRU B.plElbn Drb: O1l1?.t&2t
Anrlyrb O.t.:'Z 0 fc d' C;' 0- Cone OR:tre0COConcloZ0C:OR:OCom:o
UoU: l( llctnT6tAssrF %
R.torH gtrndrrd: Irpc / Cy{hd6 #
Con6nbs0m / Urrtht:
E4rEton O!t!:Trc.rbl.lo: SR ,t # / SrrEle #/ C-ylhdq,t
SRM Con@ntr {or / Uhe*oht![
SR|II Elplalon DEt :
Crrrithd By
:1. .
malytlet mlhodr onrtoyrd ard L onpl.tr to tli dst irt 0r. 'foidfo smryicr per6nnco, w natr no'rimniy'i oprunid6n d !o th! .ldtlbllty o, thtrhchron'dbrbolt rddr'lh.udlil'dtne urruvuiJiluir-k6;;riG-iltri,;';;f;f;iif'ii'thl.*. rnrmisiar,',crhbt!6,o,',if"""1Tff:;ifj:Hf:irtoflhosofthrhtmlbnonlahcdhmtnaxiccduro'tercorrtm,trcorlerovrcngs.ir*mdho. rnrcryrrulEclEDlnyot Li
,'sgo.lor.l
' :I'CERTIFICA.TE OF' ANA L Y. S B V:WP A. ;Pno,r O.Co I : G A S
Cyllnder Numben DT0049452 61pandgd Uncsrta,nty
11.97 e/.
2O.45'/c
Balance
Carbon dioxlde
Oxygen
Nlkogen
*,0.04clo
*o,050/.
Conq o
Conc a
Conq 0
UOil: t6 ilon T$t Atny! eL
sosnd AnlbEl. D.t :
Z:0&OC:0R:OZ0C:0zocoRo
77 of 86 cP08 1AS-039393-RT- 15 19
PRAXATRPKG PHOENXAZHS
3918 W UNCOLN STPHOENIX M S600$
Praxatr Ordq Nunbc 104920S6
Cttstoma P, O. Nut&it:
Qttton* Refeaue Nrorrliir
Cerdfred @nceniafion:
Prorrlr
57& S0utb Alamcds StrErr
Ls Aogolcs, CA 90058
FAU4 1u1tm17pdNtabd Nl O()12t\rEAa!' 4th,b Z@S6/$603
Ctllndcstt;rotta: AA CGA35o(WldqAac&yolua 20@pqt9 . 14oo.i.
::F'APNA*A//R
D*ltrnrb"" OOOI17/9S
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Exdratoo Dats: 1at8y'masGyllnderNumben SASIB6
N|STTnaceable
Ana$cal Uncertalnty
12,;O ppm C.ARBON ilONOXDE t}-z %Balance ilffROcEN
certifutioaL{otrdori: @tilfrCI,tlon Date: .1?*Yn17 lerm: 96 Mnhs &fra tb Date: 12liiizJ2sThle cv'llnder ruaa coltflod accotdlng to ths 2ol 2 EPrt rraceabl[ty protocot, 6ocument rsn;-;oan 1 Zsoi; ir"r"g p;u. Gl . Do NotUse ihls Standardlf fteseura ls less tran 1Oo psic. -- -' -"- . -
Antlt'd@tMt: -fFrfi.{brr,6&rrdld,Zszmaoac4lB6',tdk,.t)t. oqrymrr canaonrcnoide.-. -.
Rcqnrbdcononrta[or: 12ppnrCffiircotEfrdm tz.Oppm
ilortbc vtActo 8/ltt Fr6sr80t5
NDIR
ffocno€bndtdflpa. .GUI'S
Rd.S6,'C),[ndrrf : el341fit4Rrt BU.@E g.BgppmRd.Sld.Tlusblst/c8Rilt: 16noSRMSlrpbl: $,t426Rlioy0nd.rt: CrCt-Ot6ifff,
lrfiriln&a.t
Arlrnod M.thod:biftuilpobtcdbrr0oo. fingzfll
Rrrf An lyrltDdr: D.b: tfADnll
Z O R: 07.1 C: 1i7 CoE3 tlfnk C72 Z, O e.t 11t Conc.J i.lJt2Z O C: 717,3 R: 9/.! Com,' t2lb3lJOL pFr '.' fa..n.?aar4..lyi.* tr.982!iln
Analrcd brr:
:, .ii.-rUi
mt0ro.brddrdbmdoudrc-irogtuitnrycuclifuF.'iii#r-a--rc*ioffiilriii#ironrrorrsd.bnlyo,rh.,'c.arhrhtbr.ronrsruynrpco. niffi*mrmbGrrdd,lh'idud;rt&tcrn.rry,r."ro.-ffifi;rmrorarcatqrarthlu-[,Jil*. hnoffiil.hrrtitL!.bogdpilerDbt&rrb.Ll,...drhgouror0,atta otthhtctrthnoorrrrdhlrdnadadoiilic"aui*iJiiJifriirdgsornrormettn'-- ._i . r
s*qldArdyrLDalf Dafa:
Z 0 ft \O;. C; 0 CoD:. O
$ 0 . Z 0, .: C:..!r .O Colt3: O3 O, C: 0 .R:..-.0 Com OWrU: ppm :"'.. ltln.Trda;;Cl l" op[m
78 of 86 cPos 1AS-03e393- RT- Gi9
I
I lfahng our wodd
more productlve
DocNumbon 569740
Llnde Gac & Equlpment lnc.
5700 S. Alatmda Steet
Los Angelsa CA 90058
Tel: 3?3€85.215'l
Fax: 7l4d{it{689
PGVPID: FXNU
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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
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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
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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
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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
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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
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5700 S. Al.m.dr Strtat
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Tol: 323{8li-2154
Fax 714{{26680
PGVP lD: EI2OZ3
CERTIFICATE OF ANALYSIS / EPA PROTOCOL GAS t
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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
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Appendix C.3
Accreditation Informatio n I Certifications
89 of 88 GP08 1AS-039393-RT- 1519
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This is the Last Page of This Document
If you have any questions, please contact one of the following
individuals by email or phone.
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
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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
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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
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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%