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HomeMy WebLinkAboutDAQ-2024-011127-(1,a Yr*gfls_g"nr Hunter Plant 1000 South Highway l0 P.O. Box 569 Castle Dale, UT 84513 August 14,2024 Mr. Bryce Bird, Director Utah Department of Environmental Quality Division of Air Quality 195 North 1950 West P.O. Box 144820 Salt Lake ciry, uT 84114-4820 Attention: Rob Leishman RE: Notification of the Annual Quality Assurance Relative Accuracy Test Audit Continuous Emission Monitoring Systems at PacifiCorp's Hunter Plant Units 1, 2, (Title V Permit #f 500101004) Dear Mr. Bryce Bird: Please be informed, the PacifiCorp Hunter plant is scheduling the annual quality assurance Relative Accuracy Test Audit (RATA) on the Continuous Emission Monitoring Systems (CEMS) on Units l, 2, and 3. The testing is scheduled to begin October 15,2024. Enclosed for your review is the testing protocol that will be followed by the stack testing team Montrose. Shown below is the testing schedule. Hunter Units 1-3 Testing Schedule - October 2024 on the and 3. UTAH DEPAR]I/FNI OF DIVISION OF AIR OI'AI ITY Unit Date Time Test Load Range (MWsl Load Target (MWs) Load Separation (MWe) 1 70/Lsl2024 07:00-09:00 Mid Load Flow RATA 277-334 300 98 O9:30-09:30 Drop to Low Load 700-277 195 N/A 09:30-18:00 Stratification Test, Low Load Gas and Flow RATA too-217 195 98 2 LOl76l2024 07:00-09:00 Mid Load Flow RATA 215-331 298 97 09:30-09:30 Drop to Low Load 100-215 794 N/A O9:30-18:00 Stratification Test, Low Load Gas and Flow RATA 100-215 194 97 3 LOltT/2024 07:00-09:00 Mid Load Flow RATA 206-332 299 105 09:30-09:30 Drop to Low Load 80-205 185 N/A O9:30-18:00 Stratification Test, Low Load Gas and Flow RATA 80-206 185 105 NOTE: Times are approximate and subject to change. REVIEWEDInitials: RL Date: 10/23/2024Status: ReceivedFile ID#: 10237-B5 Should you have any questions regarding this testing schedule, please contact Jay Howard at (435) 748- 6519 or Tom Wiscomb at (801) 220-2373. Managing Director, Hunter Power Plant Altemate Designated Representative Enclosures Cc: Youn Joo Kim - EPA Region VIII ilenclosure Tom Wiscomb - 210 NTO ilo enclosure Craig Kormylo - Montrose w/o enclosure Source Test Plan 2024 Relative Accuracy Test Audits Units L, 2 and 3 PacifiCorp Hunter Power Plant Castle Dale, Utah Prepared For: PacifiCorp L4O7 W North Temple, Suite 210 Salt Lake City, Utah 84116 Prepared By: Montrose Air Quality Services, LLC 990 West 43rd Avenue Denver, CO 80211 For Submission To: Utah Division of Air Quality 195 North 1950 West Salt Lake City, UT 84116 Document Number; GPO43AS-O36892-PP-9O5 Proposed Test Dates: October 15 - 17, 2fJ24 Submittal Date: September 15, 2lJ24 AUG 22 2024 ESttoBd.lcF.Sol srAeffi --irfiH DEPARTMENT oF E r.rvi io u n,t e urnu oturutty DIVISION OF AIR OUALITY M SgNT+PIT Review and Ceftification I certify that, to the best of my knowledge, the information contained in this document is complete and accurate and conforms to the requirements of the Montrose Quality Management System and ASTM D7036-04. Signature: Name: BlL2/2024 QA/QC Analyst I have reviewed, technically and editorially, details and other appropriate written materials contained herein. I hereby certify that to the best of my knowledge the presented material is authentic and accurate and conforms to the requirements of the Montrose Quality Management System and ASTM D7O36-04. ,). r';l ,, i .t /sionature= /' '/' '+-L ' / Date:- .-. 1 i -L'7./.-- L,.-\/Blt2/2024 Name:Tim Wojtach Title:Account Manager Matthew Parks GP043AS-036892-PP-905 Table of Contents Paoe 1.0 Introduction........ .,.................. 5 1.1 Summary of Test Program ............... 5 1.2 Applicable Regulations and Emission Limits ........6 1.3 Key Personnel.......... .............. 8 2.0 Plant and Sampling Location Descriptions...... ................9 2.t Process Description, Operation, and Control Equipment............ ........9 2.2 CEMS Description ........9 2.3 Flue Gas Sampling Locations .......10 2.4 Operating Conditions and Process Data..... .......10 2.5 PlantSafety......... .......10 2.5.1 Safety Responsibilities .......11 2.5.2 Safety Program and Requirements ............t2 3.0 Sampling and Analytical Procedures ............13 3.1 Test Methods....... ..........13 3.1.1 EPA Method 2G ......... .......,.13 3.1.2 EPA Method 2H...... .............,..15 3.1.3 EPA Method 4........ ....'..16 3.1.4 EPA Methods 3A, 6C, 7E, and 10 ...... ............t7 3.2 Process Test Methods............ .........19 4.0 Quality Assurance and Repofting......,. .........19 4.L QA Audits .........19 4.2 Quality Control Procedures .........19 4.2.1 Equipment Inspection and Maintenance .........19 4.2.2 Audit Samples .............19 4.3 Data Analysis and Validation ...............20 4.4 Sample Identification and Custody ..................20 4.5 Quality Statement .............20 4.6 Reporting ...............,.20 4.6.1 Example Report Format ................21 4.6.2 Example Presentation of Test Resu1ts.............. .......22 List of Appendices Appendix A Supporting Information .., ......23 Appendix A.1 Units and Abbreviations ................24 Appendix A.2 Accreditation Information/Certifications...,.. ..............32 Appendix "S" Field Work Safety Plan .............34 GP043AS-036892-PP-905 Page 3 of 48 List of Tables Table 1-1 Summary of Test Program and Proposed Schedule... .......... 5 Table 1-2 Reporting Units and Applicable Standards........... ............6 Table 1-3 Summary of Part60/75 RA Requirements....,.. .............,.. 7 Table 1-4 Test Personnel and Responsibilities.... .............8 Table 2-1 CEMS Information ................9 Table 2-2 Sampling Locations........... ..........10 Table 4-1 Example NOx (lblmmBtu) RATA Results - Unit Name .........22 List of Figures Figure 3-1 EPA Method 2 Sampling Train........ .............,.14 Figure 3-2 EPA Method 4 Sampling Train ...... ........16 Figure 3-3 EPA Methods 3A, 6C, 7E, and 10 Sampling Train ....,.18 Figure 4-1 Typical Report Format .........2L GP043AS-036892-PP-905 Page 4 of 48 1.O Introduction 1.1 Summary of Test Program PacifiCorp contracted Montrose Air Quality Services, LLC (Montrose) to perform a RATA program at Hunter Power Plant located near Castle Dale, Utah. Testing will be conducted in accordance with the testing requirements of Utah Department of Environmental Quality (UDEQ) Operating Permit 1500101004 and (as applicable) 40 CFR Parts 60 and 75. The specific objectives are to: . Peform annual Relative Accuracy Test Audits (RATAs) on the Continuous Emission Monitoring Systems (CEMS) installed on Units 1, 2 and 3 . Conduct the test program with a focus on safety Montrose will provide the test personnel and the necessary equipment to measure emissions as outlined in this test plan. Facility personnel will provide the process and production data to be included in the final report. A summary of the test program and proposed schedule is presented in Table 1-1. Table 1-1 Summary of Test Program and Proposed Schedule To simplify this test plan, a list of Units and Abbreviations is included in Appendix A. Throughout this test plan, chemical nomenclature, acronyms, and reporting units are not defined. Please refer to the list for specific details. >5 min 21 minto/Ls/2024 Volumetric Flow Rate RATA COz, SOz, NO,, CO RATAs EPA 1, 2G/H,3,4 EPA 34,6C,7E, 10 Volumetric Flow Rate MTA COz, SOz, NOr, CO MTAs EPA 1, 2G/H,3,4 EPA 3A, 6C,7E, LO70/1612024 Volumetric Flow Rate RATA COz, SOz, NO*, CO MTAs EPA 1, zG/H,3, 4 EPA 3A, 6C,7E, tO >5 min 21 minto/t7/2024 GP043AS-036892-PP-905 Page 5 of 48 1.2 Applicable Regulations and Emission Limits The results from this test program are presented in units consistent with those listed in the applicable regulations or requirements. The reporting units and emission limits are presented in Table 1-2. Table 1-2 Reporting Units and Applicable Standards Volumetric Flow Rate SOz, NO^, CO ppmvw, lblmmBtu, lblhr GP043AS-036892-PP-905 Page 6 of 48 The RA requirements are presented in Table 1-3. Table 1-3 Summary of Part 60175 RA Requirements (1) Alternate is for low flow (RM measurements are < 10.0 fps) (2) Alternate is for low emitter (average SOz or NOx RM concentrations are < 250 ppm, or average NOx RM emission rates are s 0.200 lblMMBtu) Paft 6O Sulfur Dioxide (SOz) lblhr PS.6 < 2O.Oo/o of RM or < 10.0olo of AS Nitrogen Oxides (NO, as NOz) lblhr PS.6 < 20.Oo/o of RM or < 10.0olo of AS Carbon Dlonoxide (CO) ppmvw PS.4A < 10o/o of RM or < 5o/o of AS or ldl + CC < 5 ppmvd CO lblhr PS-6 < 20.Oo/o of RM or < 10.0olo of AS lblmmBtu PS-6 < 2O.Oo/o of RM or < 10.0olo of AS Part 75 Carbon Dioxide (COz) o/o volume wet App. B Sect. 2.3.1.2 Annual: < 7.5o/o of RM or t 0,7o/o COz o/o volume wet App. A Sect.3.3.3 Semiannual: s 10.0% of RM or * 1.0olo COz Volumetric Flow wscfh App. B Sect. 2.3.1.2 Annual: < 7.5o/o of RM or + 1.5 fps(l) wscfh App. A Sect.3.3.4 Semiannual: < 10.0olo of RM or + 2.0 fps{1) Sulfur Dioxide (SOz) ppmvw App. B Sect. 2.3.1.2 Annual: < 7,5o/o of RM or + 12 ppm SOz{2) ppmvw App. A Sect. 3.3.1 Semiannual: < 10.0olo of RM or + 15.0 ppm SO2(2) Nitrogen Oxides (NOx as NOz) lblMMBtu App. B Sect. 2.3.1.2 Annual: < 7.5o/o of RM or + 0.015 lblMMBtu(2) lblMMBtu App. A Sect.3.3.2 Semiannual: < 10.0olo of RM or + 0,020 lblMMBtu(z) GP043AS-036892-PP-905 PageT of 48 1.3 Key Personnel A list of project participants is included below: Facility Information Source Location: PacifiCorp Hunter Power Plant State Highway 10 Castle Dale, Utah 84513 Tom Wiscomb Sr. Environmental Advisor PacifiCorp (801) 220-2373 Tom.Wiscom b@ pacificorp. com Utah Depaftment of Air Quality Rob Leishman (801) s36-4438 RLeishman@utah.gov Testing Company Information Jay Howard Sr. Environmental Analyst PacifiCorp (43s) 748-6sL9 Jay. Howard@ PacifiCorp.com Project Contact: Role: Company: Telephone: Email: Agency Information Regulatory Agency: Agency Contact: Telephone: Email: Testing Firm: Contact: Title: Telephone: Email: Montrose Air Quality Seruices, LLC Craig Kormylo District Manager (303) 49s-3936 CKormylo@ montrose-env. com Table 1-4 details the roles and responsibilities of the test team. Table 1-4 Test Personnel and Responsibilities Facility interface, test crew coordination Preparation, suppoft PM GP043AS-036892-PP-905 Page 8 of 48 2.O Plant and Sampling Location Descriptions 2.1 Process Description, Operation, and Control Equipment The Hunter Plant comprises three pulverized coal-fired boilers. Hunter Unit #1 is a dry- bottom, tangentially-fired boiler rated at 480 gross megawatts (GMW) and equipped with a fabric-filter baghouse for particulate matter (PM) control and a flue gas desulfurization (FGD) scrubber for sulfur dioxide (SOz) control. Hunter Unit #2 is a dry-bottom, tangentially-fired boiler rated at 480 GMW and equipped with low-NO* burners and overfire air for nitrogen oxides (NO,) control, a fabric filter baghouse for PM control and an FGD scrubber for SOz control. Hunter Unit #3 is a dry-bottom, wall-fired boiler rated at 495 GMW and equipped with low-NO, burners and overfire air for NOx control, a fabric filter baghouse for PM control and an FGD scrubber for SO2 control. In accordance with Conditions ILB.2 and II.B.3 of Utah Department of Environmental Quality (UDEQ) Operating Permit 1500101003, the Unit #1, Unit #2 and Unit #3 exhaust stacks are equipped with Continuous Emission Monitoring Systems (CEMS) to quantify carbon dioxide (COz), SOz and NO" emissions. Units 1, 2 and 3 are equipped with CEMS to quantify carbon monoxide (CO) emissions for comparison to UDEQ permit limits. 2.2 CEMS Description The CEMS analyzers are presented in Table 2-1. Table 2-1 CEMS Information Unit 1 Flow Teledyne Monitor Labs Model 150 105 COz Thermo Fisher Model 41OiQ 113 SOz Thermo Fisher Model 43iQ 111 NOx Thermo Fisher Model 42iQ tt2 CO Thermo Fisher Model 48iQ Unit 2 Flow Teledyne Monitor Labs Model 150 205 COz Thermo Fisher Model 41OiQ 2L3 SOz Thermo Fisher Model 43iQ 211 NOr Thermo Fisher Model 42iQ 2t2 CO Thermo Fisher Model 48iQ Unit 3 Flow Teledyne Monitor Labs Model 150 30s COz Thermo Fisher Model 410iQ 313 SOz Thermo Fisher Model 43iQ 311 NO,Thermo Fisher Model 42iQ 3L2 CO Thermo Fisher Model 48iQ cP043AS-036892-PP-905 Page 9 of 48 2.3 Flue Gas Sampling Locations Actual stack measurements, number of traverse points, and location of traverse points will be evaluated in the field as part of the test program. Table 2-2 presents the anticipated stack measurements and traverse points for the sampling locations listed. Table 2-2 Sampling Locations Sample location(s) are verified in the field to conform to EPA Method 1. Acceptable cyclonic flow conditions are confirmed priorto testing using EPA Method 1, Section 11.4. 2.4 Operating Conditions and Process Data Emission tests are performed while the source/units and air pollution control devices are operating at the conditions required by the applicable regulation. The units are tested when operating at greater than 50o/o of rated capacity, as required by 40 CFR Part 60 or within the load levels required by a0 CFR Paft 75. Plant personnel are responsible for establishing the test conditions and collecting all applicable unit-operating data. Data collected includes the following parameters: . Unit load (MW) . Relevant CEMS Parameters 2.5 Plant Safety Montrose will comply with all safety requirements at the facility. The facility Client Sponsor, or designated point of contact, is responsible for ensuring routine compliance with plant entry, health, and safety requirements. The Client Sponsor has the authority to impose or waive facility restrictions. The Montrose test team leader has the authority to negotiate any deviations from the facility restrictions with the Client Sponsor. Any deviations must be documented. Flow: 16 (a/port) Gaseous: 12 (3/port)3228 / 7O.O 2388 / 7.4 Flow: 16 (4/port) Gaseous: 12 (3/port) 3228 / t0.s 26t6 / 8.s Flow: 16 (4/port) Gaseous: f2 (3/port) GP043AS-036892-PP-905 Page 10 of 48 2.5.1 Safety Responsibilities Planning . Montrose must complete a field review with the Client Sponsor prior to the project date. The purpose of the review is to develop a scope of work that identifies the conditions, equipment, methods, and physical locations that will be utilized along with any policies or procedures that will affect our work . We must reach an agreement on the proper use of client emergency services and ensure that proper response personnel are available, as needed . The potential for chemical exposure and actions to be taken in case of exposure must be communicated to Montrose. This information must include expected concentrations of the chemicals and the equipment used to identify the substances. . Montrose will provide a list of equipment being brought to the site, if required by the client Project Day . Montrose personnel will arrive with the appropriate training and credentials for the activities they will be peforming and the equipment that they will operate . Our team will meet daily to review the Project Scope, Job Hazard Assessment, and Work Permits. The Client Sponsor and Operations Team are invited to participate. . Montrose will provide equipment that can interface with the client utilities previously identified in the planning phase and only work with equipment that our client has made ready and prepared for connection . We will follow client direction regarding driving safety, safe work permitting, staging of equipment, and other crafts or work in the area . As per 40 CFR Part 60 Subpart A, Section 60.8, the facility must provide the following provisions at each sample location: o Sampling pods, which meet EPA minimum requirements for testing, The caps should be removed or be hand-tight. o Safe sampling platforms o Safe access to the platforms and test ports, including any scaffolding or man lifts o Sufficient utilities to perform all necessary testing . Montrose will use the client communication system, as directed, in case of plant or pr{ect emergency . Any adverse conditions, unplanned shutdowns or other deviations to the agreed scope and project plan must be reviewed with the Client Sponsor prior GP043AS-036892-PP-905 Page 11 of48 to continuing work. This will include any safe work permit and hazard assessment updates. Completion . Montrose personnel will repoft any process concerns, incidents or near misses to the Client Sponsor prior to leaving the site o Montrose will clean up our work area to the same condition as it was prior to our arrival . We will ensure that all utilities, connection points or equipment have been returned to the pre-project condition or as stated in the safe work permit. In addition, we will walk out the job completion with Operations and the Client Sponsor if required by the facility. 2.5.2 Safety Program and Requirements Montrose has a comprehensive health and safety program that satisfies State and Federal OSHA requirements. The program includes an Illness and Injury Prevention Program, site- specific safety meetings, and training in safety awareness and procedures. The basic elements include: . All regulatory required policies/procedures and training for OSHA, EPA and FMCSA . Medical monitoring, as necessary . Use of Personal Protective Equipment (PPE) and chemical detection equipment . Hazard communication . Pre-test and daily toolbox meetings . Continued evaluation of work and potential hazards . Near-miss and incident reporting procedures as required by Montrose and the Client Montrose will provide standard PPE to employees. The PPE will include but is not limited to; hard hats, safety shoes, glasses with side shields or goggles, hearing protection, hand protections, and fall protection. In addition, our trailers are equipped with four gas detectors to ensure that workspace has no unexpected equipment leaks or other ambient hazards. The detailed Site Safety Plan for this project is attached to this test plan in Appendix "S". GP043AS-036892-PP-905 Page 12 of 48 3.O Sampling and Analytical Procedures 3.1 Test Methods The test methods forthis 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 Method 2G, Determination of Stack Gas Velocity and Volumetric Flow Rate with Two-Dimensional Probes EPA Method 2G is used to measure the velocity pressure and the yaw angle of the flow velocity vector in a stack or duct using a 2-D probe. Alternatively, these measurements are made by operating one of the three-dimensional (3-D) probes described in Method 2F,in yaw determination-only mode. From these measurements and a determination of the stack gas density, the average near-axial velocity of the stack gas is calculated. The near-axial velocity accounts for the yaw, but not the pitch, component of flow. The average gas volumetric flow rate in the stack or duct is then determined from the average near-axial velocity. Peftinent information regarding the performance of the method is presented below: . Target and/or Minimum Required Sample Duration: >5 minutes The typical sampling system is detailed in Figure 3-1. GP043AS-036892-PP-905 Page 13 of 48 Figure 3-1 EPA Method 2 Sampling Train THERMOCOUPLE I I + GP043AS-036892-PP-905 Page 14 of 48 3.1.2 EPA Method 2H, Determination of Stack Gas Velocity Taking into Account Velocity Decay Near the Stack Wall EPA Method 2H is used to measure the stack gas velocity for calculating the volumetric flow rate while taking wall effects into account. To do this, a wall effects adjustment factor is determined. The factor is used to adjust the average stack gas velocity obtained using EPA Method 2,2F, or 2G while taking velocity decay nearthe stack or duct wall into account. The method contains two possible procedures: a calculational approach which derives an adjustment factor from velocity measurements and a default procedure which assigns a generic adjustment factor based on the construction of the stack or duct. The calculational procedure derives a wall effects adjustment factor from velocity measurements taken using Method 2,2F, or 2G at 16 (or more) traverse points specified in EPA Method 1 and a total of eight (or more) wall effects traverse points specified under this method. The calculational procedure based on velocity measurements is not applicable for horizontal circular ducts where build-up of particulate matter or other material in the bottom of the duct is present. A default wall effects adjustment factor of 0.9900 for brick and mortar stacks and 0.9950 for all other types of stacks and ducts may be used without taking wall effects measurements in a stack or duct. When the calculational procedure is conducted as paft of a relative accuracy test audit (RATA) or other multiple-run test procedure, the wall effects adjustment factor derived from a single traverse (i.e., single RATA run) may be applied to all runs of the same RATA without repeating the wall effects measurements. Alternatively, wall effects adjustment factors may be derived for several traverses and an average wall effects adjustment factor can be applied to all runs of the same RATA. GP043AS-036892-PP-905 Page 15 of 48 3.1.3 EPA Method 4 Determination of Moisture Content in Stack Gas EPA Method 4 is a manual, non-isokinetic method used to measure the moisture content of gas streams. Gas is sampled at a constant sampling rate through a probe and impinger train. Moisture is removed using a series of pre-weighed impingers containing methodology- specific liquids and silica gel immersed in an ice water bath. The impingers are weighed after each run to determine the percent moisture. The typical sampling system is detailed in Figure 3-2. Figure 3-2 EPA Method 4 Sampling Train SATT'PLE LINE VACUUM LINE ADAPTOR (sladddlp) BY.PASS VALVE(,iNdt6.) VACUUM GAUGETHERMOCCXJPLESII VALVE(w*dlull) Iv|ANOITJETER -o GP043AS-036892-PP-905 Page 16 of 48 3.L.4 EPA Methods 3A, 6C,7E, and 1O Determination of Oxygen, Carbon Dioxide, Sulfur Dioxide, Nitrogen Oxides, and Carbon Monoxide Concentrations in Emissions from Stationary Sources (Instru mental Analyzer Procedures) Concentrations of Oz, COz, SOz, NOx, and CO are measured simultaneously using EPA Methods 3A, 6C, 7E, and 10, which are instrumental test methods. Conditioned gas is 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: . Method Options: o Sampling is performed using a dilution probe o NO and NOz are measured separately and summed to report NO* emissions o The alternative NOx converter efficiency test described in EPA Method 7E Section 16.2 may be used (bag procedure) o Gas stratification testing is performed across a grid of 12 points determined using EPA Method 1 in accordance with 40 CFR Part 60, Appendix B. PS2 68.1.3.2 and 40 CFR Part 75. Appendix A. 66.5.6.1. Stratification testing is performed for two minutes per traverse point in accordance with 40 CFR Part 75. Aooendix A.56.5.6.1(c). If diluent and pollutant concentrations are within 5o/o of their mean concentrations, subsequent gas MTA testing is performed at a single point in the stack as allowed by 40 CFR Part 60. Appendix B. PS2 68.1.3.2 and 40 CFR Part 75. Aooendix A 56.5.6.3(b). If diluent and pollutant concentrations are within l0o/o of their mean concentrations, RATA testing is performed at three points located 0.4 meter, 1.0 meter and 2.0 meters from the stack wall, as required by 40 CFR Part 60. Appendix B. PS2 68.1.3.2 and 40 CFR Part 75. Aooendix A. 66.5.6.1(a). The typical sampling system is detailed in Figure 3-3. GP043AS-036892-PP-90s Page 17 of 48 Figure 3-3 EPA Methods 3A, 6C,7E, and 1O Sampling Train SIG}IAL MASS FLOA/CONTROI.ER/ CAUEIATIOT GASMANIFOLO GP043AS-036892-PP-905 Page 18 of 48 3.2 Process Test Methods The applicable regulations do not require process samples to be collected during this test program. 4.O Quality Assurance and Reporting 4.1 QA Audits Montrose has instituted a rigorous QA/QC program for its air quality testing. Quality assurance audits are performed as part of the test program to ensure that the results are calculated using the highest quality data available. This program ensures that the emissions data we report are as accurate as possible. The procedures included in the cited reference methods are followed during preparation, sampling, calibration, and analysis. Montrose is responsible for preparation, calibration, and cleaning of the sampling apparatus. Montrose will also perform the sampling, sample recovery, storage, and shipping. Approved contract laboratories may peform some of the preparation and sample analyses, as needed. 4.2 Quality Control Procedures Montrose calibrates and maintains equipment as required by the methods performed and applicable regulatory guidance. Montrose follows internal procedures to prevent the use of malfunctioning or inoperable equipment in test programs. All equipment is operated by trained personnel. Any incidence of nonconforming work encountered during testing is reported and addressed through the corrective action system. 4.2.L Equipment fnspection and Maintenance Each piece of field equipment that requires calibration is assigned a unique identification number to allow tracking of its calibration history. All field equipment is visually inspected prior to testing and includes pre-test calibration checks as required by the test method or regulatory agency. 4.2.2 Audit Samples When required by the test method and available, Montrose obtains EPA TNI SSAS audit samples from an accredited provider for analysis along with the samples. Currently, the SSAS program has been suspended pending the availability of a second accredited audit sample provider. If the program is reinstated, the audit samples will be ordered. If required as part of the test program, the audit samples are stored, shipped, and analyzed along with the emissions samples collected during the test program. The audit sample results are reported along with the emissions sample results. GP0434S-036892-PP-90s Page 19 of 48 4.3 Data Analysis and Validation Montrose converts the raw field, laboratory, and process data to repofting units consistent with the permit or subpart. Calculations are made using proprietary computer spreadsheets or data acquisition systems. One run of each test method is also verified using a separate example calculation. The example calculations are checked against the spreadsheet results and are included in the final report. The "Standard Conditions" for this project are29.92 inches of mercury and 68 oF. 4.4 Sample Identification and Custody No samples are required to be recovered for this test program. 4.5 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 D7036-04 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 unceftainty within the documented limits in the test methods are met by using approved test protocols for each project as defined in D7036-04 Sections 7.2.1and 12.10. Additional quality assurance information is included in the appendices. The content of this test plan is modeled after the EPA Emission Measurement Center Guideline Document (GD-042). 4.6 Reporting Montrose will prepare a final report to present the test data, calculations/equations, descriptions, and results. Prior to release by Montrose, each report is reviewed and ceftified by the project manager and their supervisor, or a peer. Source test reports will be submitted to the facility or appropriate regulatory agency (upon customer approval) within 25 days of the completion of the field work. The report will include a series of appendices to present copies of the intermediate calculations and example calculations, raw field data, laboratory analysis data, process data, and equipment calibration data. 4.6.I Example Report Format The report is divided into various sections describing the different aspects of the source testing program. Figure 4-1 presents a typical Table of Contents for the final report. Figure 4-1 Typical Report Format Cover Page Ceftification of Repoft ble of Contents Section 1.0 Introduction 2.0 Plant and Sampling Location Descriptions 3.0 Sampling and Analytical Procedures 4.0 Test Discussion and Results 5.0 Internal QA/QC Activities Appendices A Field Data and Calculations B Facility CEMS and Process Data C Laboratory Analysis Data D Quality Assurance/Quality Control E Regulatory Information GP043AS-036892-PP-905 Page 21 of 48 4.6.2 Example Presentation of Test Results Table 4-1 presents the typical tabular format that is used to summarize the results in the final source test report. Separate tables will outline the results for each CEMS parameter/set of units and compare them to their respective RA requirements. Table 4-1 Example NOx (lblmmBtu) RATA Results - Unit Name I xx/xx/xxxx XXXX.XXXX xx xx XX X xx 2 XX/XX/XXXX xxxx-xxxx XX XX XX X XX 3 xxlxx/xxxx XXXX-XXXX xx xx xx x xx 4 XX/XX/XXXX XXXX.XXXX xx XX XX X xx 5 XX/XX/XXXX XXXX.XXXX xx XX xx X XX 6 XX/XX/XXXX XXXX-XXXX XX XX XX x XX 7 xx/xx/xxxx xxxx-xxxx xx xx xx x XX 8 XXlXX/XXXX XXXX-XXXX XX XX XX x XX 9 xx/xx/xxxx xxxx-xxxx xx xx xx X XX 10 xx/xx/xxxx XXXX-XXXX XX XX XX X XX 11 xx/xx/xxxx xxxx-xxxx XX XX xx X xx t2 XXlXX/XXXX xxxx-xxxx XX xx XX X XX Averages xx XX XX x xx Applicable Standard (AS)xx units Standard Deviation XX Confidence Coefficient (CC)xx Bias Adjustment Factor (BAF)XX Unit Load XX units RA based on mean RM value xx o/o M based on AS xx o/o RA based on difference plus CC XX units M based on absolute difference xx units GP043AS-036892-PP-90s Page 22 of 48 Appendix A Su pporting Information Appendix A.1 Units and Abbreviations GP043AS-036892-PP-905 Page 24 of 48 6/i\lt?.N,r+gLI UNITS AND ABBREVIATIONS @Xo 02 corrected to X% orygen (corrected for dilution air) lCCl absolute value of the confidence coefficient ldl absolute value of the mean differencesoC degrees CelsiusoF degrees FahrenheitoR degrees Rankine " HrO inches of water column 13.6 specific gravitY of mercury AH pressure drop across orifice meter, inches H2O AP velocity head of stack gas, inches H2O e total sampling time, minutespg microgram P" density of acetone, mg/ml p* density of water, 0.9982 g/ml or 0.002201 lb/ml acfm actual cubic feet of gas per minute at stack conditions An cross-sectional area ol nozzle, f( A" cross-sectional area of stack, square feet (ft') Btu British thermal unit B* proportion by volume of water vapor in gas stream Ca particulate matter concentration in stack gas, gr/acf Cr,s average unadjusted gas concentration, ppmv Coi, measured concentration of calibration gas, ppmv cf or ft3 cubic feetcfm cubic feet per minute Cc"" average gas concentration adjusted for bias, ppmv CM average of initial and final system bias check responses from upscale calibration gas, ppmv cm or mt cubic meters Crur actual concentration of the upscale calibration gas, ppmv Co average of initial and final system bias check responses from low-level calibration gas, ppmv Ce pitot tube coefficient C. particulate matter concentration in stack gas, gr/dscf CS calibration sPan, % or PPmvCs measured concentration of calibration gas, ppmv Cv manufactured certified concentration of calibration gas, ppmv D drift assessment, % of spandcf dry cubic feet dcm dry cubic meters Dn diameter of nozzle, inches Ds diameter of stack, inches dscf dry standard cubic feetdscfm dry standard cubic feet per minutedscm dry standard cubic meters Fd F-factor, dscf/MMBtu of heat input fpm feet per minutefps feet per secondft feet ft2 square feetg gramgal gallonsgr grains (7000 grains per pound) gr/dscf grains per dry standard cubic feet GP043AS-036892-PP-905 Page 25 of 48 6 l!"{?.N,I+gLE UNITS AND ABBREVIATIONS I percent of isokinetic samplingin inch k kilo or thousand (metric units, multiply by t03)K kelvin (temperature) K3 conversion factor 0.0154 gr/mg tq conversion factor 0.002668 ((in. Hg)(ftr))/((mlx'R)) kg kilogramKp pitot tube constant (85.49 fUsec) kwscfh thousand wet standard cubic feet per hourI literslb/hr pounds per hourlb/MMBtu pounds per million Btulpm liters per minutem meter or milliM thousand (English units) or mega (million, metric units) m3 cubic metersma mass of residue of acetone after evaporation, mg Md molecular weight of stack gas; dry basis, lb/lb-mole meq milliequivalentmg milligram Mg megagram (106 grams)min minute ml or mL millilitermm millimeterMM million (English units)MMBtu/hr million Btu per hour mn total amount of particulate matter collected, mg mol mole mol. wt. or MW molecular weight Ms molecular weight of stack gas; wet basis, lb/lb-mole MW molecular weight or megawattn number of data points ng nanogramnm nanometer Po, barometric pressure, inches Hg pS picogram Ps stack static pressure, inches H2O P. barometric pressure of dry gas meter, inches Hg ppb parts per billionppbv parts per billion, by volumeppbvd parts per billion by volume, dry basisppm parts per millionppmv parts per million, by volumeppmvd parts per million by volume, dry basisppmvw parts per million by volume, wet basis P" absolute stack gas pressure, inches Hg psi pounds per square inchpsia pounds per square inch absolutepsig pounds per square inch gauge P"ta standard absolute pressure, 29.92 inches Hg Q" volumetric flow rate, actual conditions, acfm Q. volumetric flow rate, standard conditions, scfm Q"to volumetric flow rate, dry standard conditions, dscfm R ideal gas constant 21.85 ((in. Hg) (ft3)y(('R) (lbmole)) GP043AS-036892-PP-905 Page 26 of 48 UNITS AND ABBREVIATIONS SBRn,r post-run system bias check, % of span SBr pre-run system bias check, % of span scf standard cubic feetscftr standard cubic feet per hour scfm standard cubic feet per minutescm standard cubic metersscmh standard cubic meters per hour sec second sf, sq. ft., or ft2 square feet std standardt metric ton (1000 kg) T o.grs t-value T" absolute average ambient temperature, oR (+459.67 for English) T, absolute average dry gas meter temperature, oR (+459.67 for English) ton or t ton = 2000 pounds tph or tons/hr tons per hour tpy or tons/yr tons per year Ts absolute average stack gas meter temperature, oR (+459.67 for English) Tsto absolute temperature at standard conditions 6ri\ l+?,N,T+gp.E- v" Vt" Vm(sto) Vro v" Vrc(sto) V*i("ta) Vreg(std) W wa Wr.p Wss volt volume of acetone blank, ml volume of acetone used in wash, ml total volume H2O collected in impingers and silica gel, grams volume of gas sampled through dry gas meter, ftr volume of gas measured by the dry gas meter, corrected to standard conditions, dscf stack gas volume sampled, acf volume collected at stack conditions through nozzle, acf average stack gas velocity, feet per second volume of water vapor condensed, conected to standard conditions, scf volume of water vapor in gas sampled from impingers, scf volume of water vapor in gas sampled from silica gel, scf watt weight of residue in acetone wash, mg total weight of impingers, grams total weight of silica gel, grams dry gas meter calibration factor, dimensionless GP043AS-036892-PP-905 Page 27 of 48 6 lYl?N,T+gp.E AAS ACDP ACE AD ADL AETB AS ASTM BACT BDL BHP BIF BLS CC CD CE CEM CEMS CERMS CET CFR CGA CHNOS CNCGco coc COMS CPM CPMS CT CTM CTO CVAAS D" DE Dioxins DLL DNCG ECD EIT ELCD EMPC EPA EPRI ES ESP EU FCCU FGD FI FIA FID FPD FPM FTIR FTPB FTRB Furans GC ACRONYMS atomic absorption spectroscopy air contaminant discharge permit analyzer calibration error, 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 confidence 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 conlinuous opacity monitoring system condensible 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-dioxins (pcdd's) detection level limited dilute non-condensable gas electron capture detector Engineer ln Training electoconductivity 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 fl ue gas desulfurization flame ionization fl ame ionization analyzer flame ionization detector flame photometric detector fi lterable particulate matter Fourier{ransform infrared spectroscopy field train proof blank field train recovery blank polychlorinated dibenzofurans (pcdfs) gas chromatography GP043AS-036892-PP-905 Page 28 of 48 6ri\ M?,N,T+ST.E ACRONYMS GC/MS gas chromatography/mass spectroscopyGFAAS graphite furnace atomic absorption spectroscopyGFC gas filter correlationGHG greenhouse gas HAP hazardous air pollutant HC hydrocarbonsHHV higher heating value HPLC high performance liquid chromatographyHRGC/HRMS high-resolution gas chromatography/high-resolution mass spectroscopyHRSG heat recovery steam generator lC ion chromatographyICAP inductively-coupled argon plasmography ICPCR ion chromatography with a post-column reactorICP-MS inductively coupled plasma-mass spectroscopylR infrared radiationISO lnternational Standards OrganizationkW kilowattsLFG landfill gas LHV lower heating valueLPG liquified petroleum gas MACT maximum achievable control technologyMDI methylene diphyenyl diisocyanateMDL method detection limitMNOC maximum normal operating conditionsMRL method reporting limitMS mass spectrometryNA not applicable or not availableNCASI National Council For Air And Steam lmprovementNCG non-condensable gases ND not detectedNDIR non-dispersive infraredNESHAP National Emissions Standards For Hazardous Air PollutantsNG natural gasNIOSH National lnstitute For Occupational Safety And HealthNIST National lnstitute Of Standards And TechnologyNMC non-methane cutterNMOC non-methane organic compoundsNMVOC non-methane volatile organic compoundsNPD nitrogen phosphorus detectorNSPS New Source Performance StandardsOSHA Occupational Safety And Health AdministrationPAH polycyclic aromatic hydrocarbonsPCB polychlorinated biphenyl compoundsPCWP plywood and composite wood products PE Professional EngineerPFAS per- and polyfluoroalkyl substances (PFAS)Pl photoionization PID photoionization detectorPM particulate matter PMro particulate matter less than 10 microns in aerodynamic diameter PMz.s particulate matter less than 2.5 microns in aerodynamic diameter POM polycyclic organic matterPS performance specificationPSD particle size distributionPSEL plant site emission limitsPST performance specification testPTE permanent total enclosurePTM performance test method GP043AS-036892-PP-905 Page 29 of 48 64\ |,}?.N,I+P"LE QfuQC 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 TTE ULSD UV VE voc VOST WC WWTP ACRONYMS quality assurance and quality control Qualified lndividual Qualified 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 sulfur chemiluminescent detector selective catalytic reduction system standard deviation semivolatile 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 identified 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 Page 30 of 48 64\ l,l?N,T+gp.E silver arsenic barium beryllium C carbonCd cadmiumCdS cadmium sulfide CH2O formaldehyde CH3CHO acetaldehyde CH3OH methanol CHr methane C2H4O ethylene oxide C3H4O acrolein CaH6O propionaldehyde CsHe propane C6H50H phenol CHEMICAL NOMENCLATURE Ag As Ba Be Se Soz Sos SO, TCDD TCDF TGOC THC TI TRS Zn selenium sulfur dioxide sulfur trioxide sulfur oxides tetrachlorodibenzodioxin tetrach lorod ibenzofuran total gaseous organic concentration total hydrocarbons thallium total reduced sulfur compounds zinc CzHe CI, ClO2 chlorine dioxide CO carbon monoxideCo cobalt CO, carbon dioxide Cr chromiumCu copperEtO ethylene oxideEIOH ethyl alcohol (ethanol) H2 hydrogen HzO water HrOz hydrogen peroxide HrS hydrogen sulfide H2SO4 sulfuric acid HCI hydrogen chlorideHg mercuryIPA isopropyl alcoholMDI methylene diphyenyl diisocyanate MeCl2 methylene chloride MEK methyl ethyl ketoneMeOH methanolMn manganese N2 nitrogen NH. ammonia Ni nickelNO nitric oxide NOz nitrogen dioxide NO, nitrogen oxides 02 orygen P phosphorusPb leadPCDD polychlorinated dibenzo-p-dioxinsPCDF polychlorinated dibenzofurans Sb antimony Page 31 of 48 Appendix A.2 Accreditation Informatio n / Certifications Page 32 of 48 o$(f)aoo)(,ltI,d Of,_- cP53F i ; U E. O ) c. 9 ! € lo B EE P ' o oE 9s 6 0 -F tl o. l c <E O or . > 'E .! ( ) c E 3! :z . E { O; ! oo e zE 3 9i chP P < e& ?p E =o ( J .! o t - O= O PE T * o. = b 8E 5 3E = a! uo = >+ o o Hs E " a. / ) i= J 6f 8 () 6- N I gx e 3X E a= _'; </ ) bg < =E8a ()Ic a14UF{ frrqaF' t lr {Fl )q&F{ rqac&Hzc oo=ooooo6o-c-JN tomh0 (r \op ) h)a .q )HF)Loop )aaot )FlLFNLo; ) \3q) h) ot ) \3q)Sc)q) coSot!oL-ooL-oSo\oooJo9-C.9*poot/ , lr tcoUr-oE aJboBLLobooAJ n<QN{c\q)Lq) 13q)*qtsLboLa.q)LtsqFl- r 6.9ao</ ,bP - F B3 x ?9 S R y/ l- co - o -@ U= EN <: ! > .f r t o E6 ? 2 a; z - ^ E UE P oa o ^ ^- tD .u -l l O * 1- . Y .9 X oE >' i O > rnoOlo-o-NOl@rO(noIU)aa$oo-(9 gln \tc{oNof_ooLLoooIF.N.@_c .+Ero+c0)oo- ,. ( 4, Appendix rrs" Field Work Safety Plan Page 34 of 48 M M?.,N,T+g[F' SITE SAFETY PLAN BOOKLET Project: Customer: Location: Units: CIient Project Manager: Revision Date: January 21,2022 GP043AS-036892-PP-905 l1v r Ntt)N I kt),r I Site Safety Plan and JHA Purpose and lnstructions Purpose Page 1 of 2 Employee safety is the top priority of Montrose Environmental Group. All employees must be trained to assess and mitigate hazards. The District Manager and Project Manager are responsible to ensure all hazards have been properly identified and managed. All employees have Stop Work Authority in all situations where an employee feels they or their co-worker cannot perform a job safely or if there is a task for which they have not been adequately trained. The Site Safety Plan (SSP) has been developed to help assist Montrose test crews with identifying physical and health hazards and determining how the hazards will be managed. Additionally, the SSP will help each crew manage the safety of the employees by providing emergency procedures and information. The booklet contains a several safety forms that may be required in the field. lnstructions The SSP consists of the following: 1. A Pre-Mobilization Test Plan - To be completed in it's entire$ by the client project Manager prior to the test. 2. A Job Hazard Analysis is a standardized, two-page, fillable form that is used to evaluated the tasUsite's particular hazards and controls. The form also includes a daily toolbox topic and daily hazard review with sign off by the team. The client Project Manager is responsible to complete the JHA form through section 8. Upon arrival at the test site, the team will review the form for accuracy, making any corrections required and complete the remainder of the JHA. Section 9 will require at least three tasks, hazards and controls be identified for the project. Each team member has the option to discuss making changes or adding to the JHA and must sign on the Job Hazard Analysis form in agreement and sign in Section 10. The JHA is to be modified when conditions change. A toolbox meeting with a daily topic in addition to a review of the hazard analysis is required daily for the duration of the test. An additional sheet of paper with the toolbox topic and signatures can be added to the SSP packet. 3. Hazard Control Matrix - contains useful information on both engineering and administrative controls that a crew can use to reduce or eliminate the hazards they have observed plus applicable PPE that may be required. 4. Emergency Action Plan - The Job Supervisor/ Client Project Manager (CPM) will complete the Emergency Action Plan form and ensure that all employees are familiar with the facility emergency and evacuation procedures, assembly/ rally points, alert systems, and signals prior to work commencing. ln the event of an emergency situation/ evacuation, the Job Supervisor/ CPM will maintain a roster and be responsible for accounting for all employees. The Job Supervisor/ CPM will ensure that this Emergency Action Plan Form is completed, communicated to all employees, signed, and posted. 5. Additional Forms, as applicable a. MEWP Lift lnspection Form b. Heat Stress Prevention Form Based on Heat lndex c. Extended Hours Form AQS.FRM-1.13R1 Page 36 of 48GP043AS-036892-PP-905 c^ lYlqf ItgPI Page2of 2 Site Safety Plan and JHA Purpose and Instructions The SSP is a living document. The Project Manager should continually update their SSPs as new information and conditions change or if new hazards are presented. Each completed SSP should be maintained with the Test Plan in the office for a period of 3 years. There will be an audit process developed for the Site Safety Plans. AQS.FRM-1.13R1 Page 37 of 48GP043AS-036892-PP-905 riv vVtUN l Rt )51 PRE-MOBILIZATION TEST INFORMATION Source Tvpe: New Source: _ Revisit:_ Prj#/Date/Tech: Coal Fired Electric Utility: _ Ethanol Plant: _ Chemical Mfg. of CemenUlime Kiln Plant: _ Specialty Mfg. of: Anticipated Effluent Composition - check all that apply and fill in expected concentration in ppm/% tr other lf other, explain: Flammable: Toxic: Corrosive: Dust: Engineering Controls to be lmplemented: Page 1 of2 tr co tr VOC tr SOz tr NOx PROJ ECT NAM E/LOCATION : TEST DATE: PROJECT #: PROJECT MANAGER: TEST SCOPE: SITE CONTACT: Name:Contact Phone: Additional Safety Equipment Required: Personal gas monitors: _ Respiratory Protection : Half Face_ Full Face_ HEPA Filters_ Supplied Air: - (Safety Dept. Approval) Approximate Flue Gas Temperatures, (F) below 210 210 to 450 450 to 950 above 950 other lf other, explain: Approximate Duct Pressure, (iwg): lf other, explain: AQS.FRM.1.17 trtrtrtr -3 -3 to +3 +3 to +7 above +7 other GP043AS-036892-PP-90s Page 38 of 48 O" \ M\)N I kt ).ll PRE.MOBILIZATION TEST INFORMATION Sampling Location: Stack Port _ Duct Port -Approximate Sampling Platform Height, (ft) Page 2 of 2 tr below 6 lf other, explain: nntrtr 6 to 50 50 to 100 above 100 other Access and Protection: Elevators: _ Ladders: - MEWP Lift: - Scaffold: - Equipment Hoist: - Describe how equipment will be mobilized to the sampling location: Other: Additional lnformation : Effluent Chemica! Requlatorv Limits Gas Name Chemical Formula Cal OSHA PELI (ppm) Cal OSHA STEL2 (oom) NIOSH REL TWA3 (ppm) Cal OSHA Ceiling(ooml IDLH4 (ppm) Carbon Monoxide CO 25 200 35 200 1,200 Nitric Oxide NO,25 ND5 25 ND 100 Sulfur Dioxide SOz 2 5 2 ND 100 Hvdroqen Chloride HCI 0.3 2 ND 2 50 Hydrogen Sulfide HzS 10 15 10 (10 min.)c 50 100 )alifomia Occupational Safety and Health Administration (OSHA) Permissible Exposure Limit (PEL) based on an B-hour shift; 2: Cal OSHA Shoftlenn Exposure Limit (STEL) based on a 1s-minute period: 3: National lnstitute for Occupational Safety and Health (NIOSH) Recommended Exposure Limit (REL) Time-weighted Average (TWA) based on an 8-hour shift; 4: lmmediately Dangerous to Life or Health (IDLH); 5: Not Defined (ND); C: Ceiling Limit - Maximum allowable human exposure limit for an airbome or gaseous subsrance, which is not to be exceeded, even momentarily. Prepared by: Reviewed by: Date: Date: AQS-FRM-1.17 GP043AS-036892-PP-905 Page 39 of 48 Slient 3ontact Name )ate =acility SSP Writer )M 3lient Rep I plete out the Heat Stress Prevention Form. Job Prepara [ .too site I sate w tion rWalk Through Completed E Site Specific Training Com crk Permit Received from Client lf the heat index is expected to be above 91 ", fil 1of3 1. /aY . r\1 (rr\ I lr\)\t Job Hazard Analysis Enor Rl* E Tlme Pressure f] Remoie Work Location E > 12 hrshlft [ worting > 8 consecutive days E Lack of procsdures E Extreme temps, wind >30mph E Personal illnessffatigue E Vague work guidance E Monotonous Activity El first aay back after time off El uuttipte joo locations El other: Hazards Dust Hazards Thermal Bum Electrical Hazards lnadequate Lighting Slip and Trip Hand Protection Secondary Permits Working ftom Heights Soo sl.o Soct,7 Electrical Lifring Respiratory See also Sect. I Hazards for Consideration Hazard Controls E] Dust Mask E Goggles E Other: E Hot Gloves E] Heat Shields E o&rer Protective Clothlng: E Connections Protected from Elements I External GFCI f]Other: E Xe nating Requirement E] lntrinsically Safe Requirement E hstall Temporary Lighting I Headlamps ! Housekeeping E Barricade Area E Other: El cut Resistant Gloves E pincn Rs. E C'eneral E ebcricat E lmpact Resistant E other: E Hot Work E Confined Space ! Excavation E fattng objecls ! Fall protection EJ Orop zone protection E] Phtform load ratings f] ScafoU inspeclion E Ladder inspection E] Baricades for equipment I Exposed wire/connector El Verify equipment grounding E Arc Flash ! Crane lift plan fl Rigging inspection EI fag lines used tf Hoists in place E Unexpected exposure E Chemical f] Dust (combustible) n PEL provided E C".tridoes or suoolied air available E Gas detection RequiredPPE DHardHats !safetyGlasses flSafetyToeShoe/Boot IHearingProtection lsafetySpotter E Hi-Vis Vests E Harness/Lanyard. E Goggles E Personal Monitor Type: E Metatarsal Guards E Hot Gloves ! Face Shield E Respirator Type: ENomex/FRC E Otner PPE: 2. 3. 4. 5. AOS-FRM-1.18 Page 40 of 48 Facility lnformation/Emergency Preparedness lf non+mergency medical attention is needed, call: AXIOM #: 877-502-9466. Plant Emergency # EMS Location Certified First Aid Person: Evacuation Routes Rally Point Severe Weather Shelter Location Eye Wash & Safety Shower Location Operational: EYes ENo Source lnformation: (list type): Stack Gas Temp. ("F) Stack Gas Press. ("H2O) Stack Gas Components: Stack Gas lnhalation Potential? EVes E ruo lf yes. see List of Hazard Chemicals GP043AS-036892-PP-905 rfvrMt)NIRL))t Additional Work Place Hazards Job Hazard Analysis 2of3 7. 8. Critical Procedures - check all that apply - *indicates additional form must be completed or collected from client E Heat Stress Prevention* E Confined Spacet E MEWP. E Roof Work E Scaffold E CoU Weather Work f] Hazardous Energy Control' E Exposure Monitoring E Other: Working From Heights Fall Protection Falling Objects Pptecdon Fall Hazard Communication iE f ixeO Guardrails/Toe boards E Fall Prevention PPE Warning Line System iEl e""ioaing E Netting ! House Keeping ETethered Tools ECatctr BlanketorTarp i D RojacenUOverhead Workers E Contractor Contact fl Client Contact Other Considerations Environmental Hazards - Weather Forecast E Heavcold ELigntning E Rain E snow E lce E Tornado I wind Speed Steps for Mitigation: Electrical Safety Plannlng ptant Hook up: f] t tov E 22ot24ov E +aov EI Generator E Hard wired into panel Electrical Classified Area: EYes fl No Trailer Grounded: E Yes E f'lo Plug Type Electrical Hook Up Responsibility: ist of Hazardous Chemicals E Acetone E ruitric Acid other chemicals: E Hydrogen Peroxide E Compressed Gases E Hexane E Sufiuric Acid E lsopropyl Alcohol I Flammable Gas E Toluene E Hydrochloric Acid E liqulo Nitrogen ! Non-Flammable Gas E Hzs E Carbon Monoxide Steps for Mitigation: lildlife/Fauna in Area E Poison lvy ! Poison oak Elnsects:!Wildlife: Personnel w/ known allergies to bees stings or other allergens? ! Yes E tto 9.Hazards and Mitigation 1 2 3 1 2 3 I 2 3 'l 2 3 1 2 3 1 2 3 1 2 3 1 2 3 AQS-FRM-1.18 Page 41 of 48GP043AS-036892-PP-905 ,' 3 of 36vrrVt()NlK\))l Job Hazard Analysis ,HA REVIEW: Crew Names & Slgnatures Printed Name Signature Date Printed Name Siqnature Date 11 JHA Meetino & Review to review: o Change in conditions o Extended work hours o Daily Safety Topic o New workers or contractors o Occurrence of near misses or injuries demonstratos that site conditions and hazards have not changed from the original SSP. lf changes did occur, make the updates to this JHA and add notes as applicable in Section 9. Day Dlrcucrlon Toplc lnl0dr 2 3 4 5 6 7 8 9 10 11 AQS.FRM-1.18 Page 42 of 48GP043AS-036892-PP-905 ljv i M()N I KL)\t Poge 1 of 2 EMERGENCY ACTION PLAN FORM The Job Supervisor/ Client Project Manager (CPM) will €nsure that all employees are familiar with the facility emergency and evacuation procedures, assembly/ rally points, alert systems, and slgnals prlor to work commencing. ln the event of an emergency sltuatlon/ evacuation, the Job Supervisor/ GPM will maintain a roster and be responsible for accounting for all employees. The Job Supervisor/ CPM wlll ensure that thls Emergency Action Plan Form ls completed, communlcated to all employees, and posted. .You must follow the client's em€rgoncy action plan first, and notify your Supervisor immediately. .lf incident ls life threatenlng, CALL 9'll IMMEDIATELLY .lf non-emergency medical attention is needed, call A)(IOM Medical number: 877-502-9466. AQS-FRM-1.11 GP043AS-036892-PP-905 1 MEG Job Supervisor/ CPM's Name: 2 MEG Job Supervisor/ GPM's Telephone Number: 3 MEG Job Safety Supervisor (if applicable): 4 MEG Job Safety Supervisor's Telephone Number: 5 Plant's Emergency Telephone Number: 6 Local Hospital/ Clinic Telephone Number: 7 Emergency Ops Radio Channel: 8 Plant's #1 Contact Person's Name: 9 PIant's #1 Contact Person's Telephone Number: 10 Plant's #2 Contact Person's Name: 11 Plant's #2 Contact Person's Telephone Number: 12 Designated Assembly Point Location : 13 Evacuation Routes: 14 Severe Weather Shelter Location: 15 Eye Wash and Safety Shower Location: 16 the First Aid Kit is Located: 17 The Fire Extinguisher is Located: Page 43 of 48 ,6rrM()NlKt))t Poge 2 of 2 EMERGENCY EVACUATION AND ASSEMBLY MAP 1 Facility Name: 2 Facility Alarm (Circle):YES or NO 3 Alarm Tones: FIRE: SHELTER.IN.PLACE: AfUED. 4 Designated Shelter(s) Description: 5 Designated Assembly Point(s) Description: N*+, s EMERGENCY ACTION PIAN FORM AND EVACUATTON ASSEMBTY MAP REVIEW: Crew Names and Signatures Printed Nome:Signature:Dote:Printed Name:Signoture:Date: AQS-FRM-1.11 GP043AS-036892-PP-905 Page 44 of 48 .,tvl [v r r!1\rN I irt,l\t Page 1 of 1 Daily MEWP Lift lnspection Form All checks must be completed prior to each work shift, before operation of the MEWP lift. This checklist must be used atthe beginning of each shift or following 6 to 8 hours of use. MEWP Lift Model#:Serial Number: Make:Rented or Owned: . Check "Yes" if an item is adequate, operational, and safe.. Check "No" to indicate that a repair or other corrective action is required prior to use.o Check "N/A" to indicate "Not Applicable." Items to be lnspected 1. All MEWP lift components are in working condition (i.e. no loose or missing parts, torn or loose hoses, etc.) - if something can be easily loosened by hand then it is not sufficient. 2. Hydraulic fluid level is sufficient, with the platform fully lowered 3. Hydraulic system pressure (see manufacturer specs) is acceptable. lf the pressure is low, determine cause and repair in accordance with accepted procedures as outlined in service manual. 4. Tires and wheel lug nuts (for tightness) 5. Hoses and cables (i.e. wom areas or chafing) 6. Platform rails and safety gate (no damage present) 7. Pivot pins secure 8. Welds are not cracked and structural members are not bent or broken 9. Warning and instructional labels are legible and secure, and load capacity is cleady marked. 10. Manufacturer's lnstruction Manual is present inside the bucket 11. Base controls (switches and push buttons) can be properly operated 12. Platform conditions are safe (i.e. not slippery) 13. Fire extinguisher is present, mounted and fully charged, located inside the bucket 14. Headlights, safety strobe light and back-up alarm are functional 15. Workplace is free of hazards (overhead powerlines, obstructions, level surface, high winds, etc.) *Do not operate if winds are 20 mph, unless otherwlse specifled by manufacturer recommendations. Yes ! D D tr u tr n u n D ! tr tr tr tr N/A tr tr tr No tr ! tr trtr DN trtr ND trtr utr trn ntr Dtr utr un trtr Operator Name & Signature Location Date Ground Control Name & Signature Location Date Harness lnspectlons: Printed Name Signature Date Printed Name Signature Date Printed Name GP043AS-036892-PP-905 Date AQS-FRM.1.16 Page 45 of 48 Signature a- .lY c/,\ MONTROSE Page 1 of 1 Extended Hours Safety Audit Project Number:Date:Time: When a project is expected to extend past a 14-hour work day, this form must be completed to evaluate the condition of the crew, and the safety of the work environment. Permission to proceed into extended work hours must come from a District Manager (DM) or Regional Vice President (RVP). Technical RVPs can authorize moving forward, if they are in the field or if they are managing the project. 1. Hold test crew meetinq Test crew initials: . Temperature and weather . Hoisting. Lighting . PPE (i.e. respirators, etc.). Working from Heights . Pollutant concentration in ambient air (SOz, HzS, ect.) Notifv DM or RVP The PM must contact either the DM or RVP to discuss the safety issues that may arise due to the extended work period. lf the DM is the acting PM on the job site, they must contact the RVP. During this time, they can come to an agreement on how to proceed. ltemsto discuss include: a a I a Reason for extended hours Reason for delay Production limitations lmpending Weather Contact the client The PM, DM or RVP must discuss with client any identified safety concerns, the client's needs and mutually agree on how to proceed. Discussion should also include the appropriate rest period needed before the next day's work shift can begin. The DM and/or a RVP must be informed on the final decision. FinalOutcome: Approver: 2. 3. OOlAS-SAFETY-FM.3 Page 46 of 48 The test leader should look for signs of the following in their crews: . lrritability. Lack of motivationo Headaches. Giddiness . Fatigue. Depression. Reduced alertness, lack of concentration and memory The test leader should assess the environmental and hazardous concerns: GP043AS-036892-PP-905 1. 2. MUN I RUsb Page 1 of 1 Heat Stress Prevention Form This form is to be used when the Expected Heat lndex is above 91" F, and is to be kept with project documentation. Proiect Manaoer (PM):Exoected Hiqh Temp: Date(s):Exoected Heat lndex: Review the signs of Heat Exhaustion and Heat Stroke lf Heat lndex is above 91'F:r Provide cold water and/or sports drinks to allfield staff (avoid caffeinated drinks and energy drinks which can increase core temperature). o Bring no less than one gallon of water per employee. lf employee(s) are dehydrated, on blood pressure medication or not acclimated to heat, ensure they are aware of the heightened risk for heat illnesso Provide cool head bands/vests/etc.. Have ice available to employees. lmplement work shift rotations and breaks, particularly for employees working in direct sunlight.. Provide as much shade at the jobsite as possible, including tarps, tents or other acceptable temporary structures.. PM should interview each field staff periodically to evaluate for signs of heat illness lf Heat lndex is above 103' F:. Employees must stop for drinks and breaks every hour (about 4 cups/hour). Employees are not permitted to work alone for more than one hour at a time without a break offering shade and drinkso Employees should wear cool bands and vests if working outside more than one hour at a time. PM should interview each field staff every 2 hours to evaluate for signs of heat illness 3. r:**:. -ffffili8t ,raau-a qwmltlni ffi Naulr or @mldna R.pld,s.kpuls - Rapld,strcogpul* MusL d.mps r.,r.y fo* (I) OOlAS-SAFETY-FM.5 Page 47 of 48GP043AS-036892-PP-90s 1n. This is the Last Page of This Document If you have any questions, please contact one of the following individuals by email or phone. Na me : Cra ig Kormylo Title: District Manager Region: USA - Stack - Great Plains - Operations Email : CKormylo@montrose-env.com Phone: (303) 495-3936 Name: Glen Capra Title: Vice President Region: USA - Stack Email : GCapra@montrose-env.com Phone: (5t2) 772-6450 UTAH DFPNRTVTTT OrEI vlRo_ryM.E-NfAL a uA L I rY AUG 2 2 ?a24 D,VISION OF AIR QUAI ITY GP043AS-036892-PP-905 Page 48 of 48