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HomeMy WebLinkAboutDAQ-2024-0043181 DAQC-1327-23 Site ID 12524 (B5) MEMORANDUM TO: CEM FILE – PACIFICORP – Currant Creek Power Plant THROUGH: Harold Burge, Major Source Compliance Section Manager FROM: Rob Leishman, Environmental Scientist DATE: December 8, 2023 SUBJECT: Source: Units CTG1A and CTG1B Contact: Erik Ricardo – 435-623-3816 Tom Wiscomb – 801-220-2373 Location: West 300 North, Mona, Juab County, UT Test Contractor: Montrose Air Quality Services, LLC FRS ID#: UT00000049002300026 Permit/AO#: AO DAQE-AN-1252400009-15 dated January 23, 2015 Subject: Review of RA/PST Protocol dated December 4, 2023 On December 4, 2023, Utah Division of Air Quality (DAQ) received an emailed protocol for a RA/PST (relative accuracy/performance specification test) of the Pacificorp Currant Creek Units CTG1A and CTG1B in Mona, Utah. Testing will be performed on January 30-31, 2024, to determine the relative accuracy of the NOX and CO monitoring systems. PROTOCOL CONDITIONS: 1. RM 3A used to determine dry molecular weight of the gas stream; OK 2. RM 7E used to determine NOX concentrations of emissions; OK 3. RM 10 used to determine CO concentrations of emissions; OK 4. RM 19 used to determine volumetric flow; OK DEVIATIONS: No deviations noted. CONCLUSION: The protocol appears to be acceptable. RECOMMENDATION: Send attached protocol review and test date confirmation notice. 1 8 2 Source Test Plan 2024 Compliance and RATA Testing CTG1A, CTG1B PacifiCorp Currant Creek Generating Station Mona, UT Prepared For: PacifiCorp 1407 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 Department of Environmental Quality, Division of Air Quality 195 North 1950 West Salt Lake City, UT 84116 Document Number: 043AS-022762-PP-770 Proposed Test Dates: January 30 & 31, 2024 Submittal Date: December 30, 2023 Review and Certification 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: Date: 12/1/2023 Name: Matthew Parks Title: 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 D7036-04. Signature: Date: 12/1/2023 Name: Tim Wojtach Title: Account Manager GP043AS-022762-PP-770 Page 2 of 46 Table of Contents Section Page 1.0 Introduction ........................................................................................................ 5 1.1 Summary of Test Program ............................................................................. 5 1.2 Applicable Regulations and Emission Limits ...................................................... 6 1.3 Key Personnel .............................................................................................. 7 2.0 Plant and Sampling Location Descriptions................................................................ 8 2.1 Process Description, Operation, and Control Equipment ..................................... 8 2.2 CEMS Description ......................................................................................... 8 2.3 Flue Gas Sampling Locations .......................................................................... 9 2.4 Operating Conditions and Process Data ........................................................... 9 2.5 Plant Safety ................................................................................................. 9 2.5.1 Safety Responsibilities .......................................................................... 9 2.5.2 Safety Program and Requirements ....................................................... 11 3.0 Sampling and Analytical Procedures ..................................................................... 12 3.1 Test Methods ............................................................................................. 12 3.1.1 EPA Methods 3A, 6C, 7E, and 10 .......................................................... 12 3.1.2 EPA Method 201A ............................................................................... 13 3.1.3 EPA Method 202 ................................................................................. 13 3.2 Process Test Methods .................................................................................. 15 4.0 Quality Assurance and Reporting .......................................................................... 16 4.1 QA Audits .................................................................................................. 16 4.2 Quality Control Procedures .......................................................................... 16 4.2.1 Equipment Inspection and Maintenance ................................................ 16 4.2.2 Audit Samples ................................................................................... 16 4.3 Data Analysis and Validation ........................................................................ 16 4.4 Sample Identification and Custody ................................................................ 17 4.5 Quality Statement ...................................................................................... 17 4.6 Reporting .................................................................................................. 17 4.6.1 Example Report Format ...................................................................... 18 4.6.2 Example Presentation of Test Results ................................................... 18 List of Appendices Appendix A Supporting Information ........................................................................... 21 Appendix A.1 Units and Abbreviations .................................................................. 22 Appendix A.2 Accreditation Information/Certifications ............................................ 30 Appendix “S” Field Work Safety Plan .......................................................................... 32 GP043AS-022762-PP-770 Page 3 of 46 List of Tables Table 1-1 Summary of Test Program and Proposed Schedule .......................................... 5 Table 1-2 Reporting Units and Emission Limits .............................................................. 6 Table 1-3 Summary of Part 60/75 RA Requirements ...................................................... 6 Table 1-4 Test Personnel and Responsibilities ............................................................... 7 Table 2-1 CEMS Information ....................................................................................... 8 Table 2-2 Sampling Locations ..................................................................................... 9 Table 4-1 Example Parameter Emissions Results - Unit Name ....................................... 19 Table 4-2 Example <Parameter> (Units) RATA Results - Unit Name .............................. 20 List of Figures Figure 3-1 EPA Methods 3A, 7E, and 10 Sampling Train ................................................ 13 Figure 3-2 EPA Methods 201A (PM10) and 202 Sampling Train ...................................... 15 Figure 4-1 Typical Report Format .............................................................................. 18 GP043AS-022762-PP-770 Page 4 of 46 1.0 Introduction 1.1 Summary of Test Program PacifiCorp contracted Montrose Air Quality Services, LLC (Montrose) to perform a Compliance and RATA emissions test program at PacifiCorp’s Currant Creek Utah Plant located in Mona, UT. The tests are conducted to evaluate compliance with the applicable emission limits in UDEQ Approval Order DAQE-AN125240009-15. The specific objectives are to: • Perform annual Particulate Matter (PM) compliance testing on the exhaust stacks of Units CTG1A and CTG1B in accordance with the requirements of UDEQ Approval Order DAQE-AN125240009-15 • Perform annual Relative Accuracy Test Audits (RATAs) on the Continuous Emission Monitoring Systems (CEMS) installed on Units CTG1A and CTG1B in accordance with the requirements of 40 CFR Parts 60 and 75 (as applicable) • 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 Proposed Test Date Unit ID/ Source Name Activity/Parameters Test Methods No. of Runs Duration (Minutes) 1/30/2024 CTG1A O₂, NOx, CO EPA M3A, 7E, 10 9-12 21 PM10, CPM EPA M201A, 202 3 120 1/31/2024 CTG1B O₂, NOx, CO EPA M3A, 7E, 10 9-12 21 PM10, CPM EPA M201A, 202 3 120 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. GP043AS-022762-PP-770 Page 5 of 46 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 Emission Limits Unit ID/ Source Name Parameter Reporting Units Emission Limit Emission Limit Reference CTG1A, CTG1B PM/PM10 lb/hr 13.3 DAQE-AN125240009-15 CTG1A, CTG1B PM/PM10 lb/mmBtu 0.066 DAQE-AN125240009-15 The RA requirements are presented in Table 1-3. Table 1-3 Summary of Part 60/75 RA Requirements Parameter/Units Regulatory Reference Performance Specification Part 60 Nitrogen Oxides (NOx as NO2) ppmvd @ 15% O2 PS-2 ≤ 20.0% of RM or ≤ 10.0% of AS lb/hr PS-6 ≤ 20% of RM or ≤ 10% of AS Carbon Monoxide (CO) ppmvd @ 15% O2 PS-4A ≤ 10% of RM or ≤ 5% of AS or |d̄|+CC ≤ 5 ppmvd CO lb/hr PS-6 ≤ 20% of RM or ≤ 10% of AS Part 75 Oxygen (O2) % volume dry App. B Sect. 2.3.1.2 Annual: ≤ 7.5% of RM or ± 0.7% CO2 Nitrogen Oxides (NOx as NO2) lb/mmBtu App. B Sect. 2.3.1.2 Annual: ≤ 7.5% of RM or ± 0.015 lb/MMBtu(1) (1) Alternate is for low emitter (average RM emission rates are ≤ 0.200 lb/MMBtu) GP043AS-022762-PP-770 Page 6 of 46 1.3 Key Personnel A list of project participants is included below: Facility Information Source Location: PacifiCorp Currant Creek Generating Station W 300 N Mona, Utah 84645 Project Contact: Tom Wiscomb Role: Environmental Advisor Company: PacifiCorp Telephone: (801) 220-2373 Email: Tom.Wiscomb@pacificorp.com Erik Ricardo Sr Environmental Analyst PacifiCorp (435) 623-3816 Erik.Ricardo@PacifiCorp.com Agency Information Regulatory Agency: Utah Department of Environmental Quality, Division of Air Quality Agency Contact: Rob Leishman Telephone: (801) 536-4438 Email: RLeishman@utah.gov Testing Company Information Testing Firm: Montrose Air Quality Services, LLC Contact: Craig Kormylo Title: District Manager Telephone: (303) 670-0530 Email: CKormylo@montrose-env.com Table 1-4 details the roles and responsibilities of the test team. Table 1-4 Test Personnel and Responsibilities Role Primary Assignment Additional Responsibilities Field Project Manager Operate mobile lab Facility interface, test crew coordination Technician Execute stack platform responsibilities Preparation, support PM GP043AS-022762-PP-770 Page 7 of 46 2.0 Plant and Sampling Location Descriptions 2.1 Process Description, Operation, and Control Equipment Currant Creek Generating Station comprises two combined-cycle combustion turbines designated CTG1A and CTG1B. 2.2 CEMS Description The CEMS analyzers are presented in Table 2-1. Table 2-1 CEMS Information Location Analyzer Type Manufacturer Model No. Part 75 ID CT1A O2 Thermo 48iQ 111 NOx Thermo 42iQ 112 CO Thermo 48iQ ––– CT1B O2 Thermo 48iQ 211 NOx Thermo 42iQ 212 CO Thermo 48iQ ––– GP043AS-022762-PP-770 Page 8 of 46 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 Sampling Location Stack Inside Diameter (in.) Distance from Nearest Disturbance Number of Traverse Points Downstream EPA “B” (in./dia.) Upstream EPA “A” (in./dia.) CTG1A 202 864 / (4.3 Diam) 168 / (0.8 Diam) Isokinetic: 12 (3/port) Gaseous: 12 (3/port) CTG1B 202 864 / (4.3 Diam) 168 / (0.8 Diam) Isokinetic: 12 (3/port) Gaseous: 12 (3/port) Sample locations are verified in the field to conform to EPA Method 1. Acceptable cyclonic flow conditions are confirmed prior to 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 permit. RATA tests are performed when the unit(s) are operating at greater than 50% of the maximum rated/normal capacity. Plant personnel are responsible for establishing the test conditions and collecting all applicable unit-operating data. Data collected includes the following parameters: • Unit Load (GMW) • Applicable CEMS data 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. 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 GP043AS-022762-PP-770 Page 9 of 46 • 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 performing 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 ports, 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 project emergency • Any adverse conditions, unplanned shutdowns or other deviations to the agreed scope and project plan must be reviewed with the Client Sponsor prior to continuing work. This will include any safe work permit and hazard assessment updates. Completion • Montrose personnel will report any process concerns, incidents or near misses to the Client Sponsor prior to leaving the site • Montrose will clean up our work area to the same condition as it was prior to our arrival GP043AS-022762-PP-770 Page 10 of 46 • 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-022762-PP-770 Page 11 of 46 3.0 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, 7E and 10 Determination of Oxygen, Carbon Dioxide, Nitrogen Oxides, and Carbon Monoxide Concentrations in Emissions from Stationary Sources (Instrumental Analyzer Procedures) Concentrations of O₂, CO₂, NOx, and CO are measured simultaneously using EPA Methods 3A, 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: o A dry extractive sampling system is used to report emissions on a dry basis o A paramagnetic analyzer is used to measure O₂ o A nondispersive infrared analyzer is used to measure CO₂ o A chemiluminescent analyzer is used to measure NOx o A gas filter correlation nondispersive infrared analyzer is used to measure CO o NO and NO₂ are measured separately and summed to report NOx emissions The typical sampling system is detailed in Figure 3-1. GP043AS-022762-PP-770 Page 12 of 46 Figure 3-1 EPA Methods 3A, 7E, and 10 Sampling Train 3.1.2 EPA Method 201A Determination of PM10 and PM2.5 Emissions from Stationary Sources (Constant Sampling Rate Procedure) To measure PM10, extract a sample of gas at a predetermined constant flow rate through an in-stack sizing device. The particle-sizing device separates particles with nominal aerodynamic diameters of 10 micrometers. To minimize variations in the isokinetic sampling conditions, you must establish well-defined limits. After a sample is obtained, remove uncombined water from the particulate, then use gravimetric analysis to determine the particulate mass for each size fraction. 3.1.3 EPA Method 202 Dry Impinger Method for Determining Condensable Particulate Emissions from Stationary Sources The CPM is collected in dry impingers after filterable PM has been collected on a filter maintained as specified in either Method 5 of Appendix A-3 to 40 CFR 60, Method 17 of Appendix A-6 to 40 CFR 60, or Method 201A of Appendix M to 40 CFR 51. The organic and GP043AS-022762-PP-770 Page 13 of 46 aqueous fractions of the impingers and an out-of-stack CPM filter are then taken to dryness and weighed. The total of the impinger fractions and the CPM filter represents the CPM. Compared to the version of Method 202 that was promulgated on December 17, 1991, this method eliminates the use of water as the collection media in impingers and includes the addition of a condenser followed by a water dropout impinger immediately after the final in- stack or heated filter. This method also includes the addition of one modified Greenburg Smith impinger (backup impinger) and a CPM filter following the water dropout impinger. CPM is collected in the water dropout impinger, the modified Greenburg Smith impinger, and the CPM filter of the sampling train as described in this method. The impinger contents are purged with nitrogen immediately after sample collection to remove dissolved SO₂ gases from the impinger. The CPM filter is extracted with water and hexane. The impinger solution is then extracted with hexane. The organic and aqueous fractions are dried and the residues are weighed. The total of the aqueous and organic fractions represents the CPM. The potential artifacts from SO₂ are reduced using a condenser and water dropout impinger to separate CPM from reactive gases. No water is added to the impingers prior to the start of sampling. To improve the collection efficiency of CPM, an additional filter (the “CPM filter”) is placed between the second and third impingers The typical sampling system is detailed in Figure 3-2. GP043AS-022762-PP-770 Page 14 of 46 Figure 3-2 EPA Methods 201A (PM10) and 202 Sampling Train 3.2 Process Test Methods The applicable regulations do not require process samples to be collected during this test program. GP043AS-022762-PP-770 Page 15 of 46 4.0 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 perform 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. 4.2.1 Equipment Inspection 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. 4.3 Data Analysis and Validation Montrose converts the raw field, laboratory, and process data to reporting 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 are 29.92 inches of mercury and 68 °F. GP043AS-022762-PP-770 Page 16 of 46 4.4 Sample Identification and Custody The on-site Field Project Manager will assume or assign the role of sample and data custodian until relinquishing custody. The sample custodian will follow proper custody procedures before departing from the test site including: • Assign the unique sample identification number to each sample • Attach sample labels and integrity seals to all samples • Complete COC form(s), ensuring that the sample identification numbers on the samples match the sample identification numbers on the COC • Pack and store samples in accordance with the test method requirements in appropriate transport containers for protection from breakage, contamination, or loss • Keep samples in a secure locked area if not in the direct presence of Montrose staff The sample custodian will follow proper custody procedures upon arriving at the Montrose office including: • Remove samples and COC documents from vehicles and check into designated secure sample holding areas • Store samples requiring additional measures such as refrigeration or dry ice appropriately 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 uncertainty within the documented limits in the test methods are met by using approved test protocols for each project as defined in D7036-04 Sections 7.2.1 and 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 certified by the project manager and their supervisor, or a peer. Source test reports will be submitted to the facility within 25 days of the completion of the field work. The report will GP043AS-022762-PP-770 Page 17 of 46 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. 4.6.1 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 Certification of Report Table 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 4.6.2 Example Presentation of Test Results Table 4-1 presents the typical tabular format that is used to summarize the compliance results in the final source test report. Separate tables will outline the results for each target analyte and compare them to their respective emissions limits. GP043AS-022762-PP-770 Page 18 of 46 Table 4-1 Example Parameter Emissions Results - Unit Name Parameter/Units Run 1 Run 2 Run 3 Average Date XX XX XX XX Time XX XX XX XX Process Data parameter 1, units XX XX XX XX parameter 2, units XX XX XX XX Sampling & Flue Gas Parameters sample duration, minutes XX XX XX XX O2, % volume dry XX XX XX XX CO2, % volume dry XX XX XX XX flue gas temperature, °F XX XX XX XX moisture content, % volume XX XX XX XX volumetric flow rate, dscfm XX XX XX XX <Parameter> ppmvd XX XX XX XX ppmvd @ 15% O2 XX XX XX XX lb/hr XX XX XX XX tons/yr XX XX XX XX lb/MMBtu XX XX XX XX GP043AS-022762-PP-770 Page 19 of 46 Table 4-2 presents the typical tabular format that is used to summarize the RATA 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 4-2 Example <Parameter> (Units) RATA Results - Unit Name Run No. Date Time RM CEMS Difference Run used (Y or N) Unit Load (units) 1 XX/XX/XXXX XXXX-XXXX XX XX XX X XX 2 XX/XX/XXXX XXXX-XXXX XX XX XX X XX 3 XX/XX/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 XX/XX/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 12 XX/XX/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 % RA based on AS XX % RA based on difference plus CC XX units RA based on absolute difference XX units GP043AS-022762-PP-770 Page 20 of 46 Appendix A Supporting Information GP043AS-022762-PP-770 Page 21 of 46 Appendix A.1 Units and Abbreviations GP043AS-022762-PP-770 Page 22 of 46 @ X% O2 corrected to X% oxygen (corrected for dilution air) |CC|absolute value of the confidence coefficient |d|absolute value of the mean differences ºC degrees Celsius ºF degrees Fahrenheit ºR degrees Rankine " H2O inches of water column 13.6 specific gravity of mercury ΔH pressure drop across orifice meter, inches H2O ΔP velocity head of stack gas, inches H2O θ total sampling time, minutes µg microgram ρa density of acetone, mg/ml ρw 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 of nozzle, ft2 As cross-sectional area of stack, square feet (ft2) Btu British thermal unit Bws proportion by volume of water vapor in gas stream Ca particulate matter concentration in stack gas, gr/acf CAvg average unadjusted gas concentration, ppmv CDir measured concentration of calibration gas, ppmv cf or ft3 cubic feet cfm cubic feet per minute CGas average gas concentration adjusted for bias, ppmv CM average of initial and final system bias check responses from upscale calibration gas, ppmv cm or m3 cubic meters CMA actual concentration of the upscale calibration gas, ppmv CO average of initial and final system bias check responses from low-level calibration gas, ppmv Cp pitot tube coefficient Cs particulate matter concentration in stack gas, gr/dscf CS calibration span, % or ppmv CS measured concentration of calibration gas, ppmv CV manufactured certified concentration of calibration gas, ppmv D drift assessment, % of span dcf dry cubic feet dcm dry cubic meters Dn diameter of nozzle, inches Ds diameter of stack, inches dscf dry standard cubic feet dscfm dry standard cubic feet per minute dscm dry standard cubic meters Fd F-factor, dscf/MMBtu of heat input fpm feet per minute fps feet per second ft feet ft2 square feet g gram gal gallons gr grains (7000 grains per pound) gr/dscf grains per dry standard cubic feet hr hour UNITS AND ABBREVIATIONS GP043AS-022762-PP-770 Page 23 of 46 UNITS AND ABBREVIATIONS I percent of isokinetic sampling in inch k kilo or thousand (metric units, multiply by 103) K kelvin (temperature) K3 conversion factor 0.0154 gr/mg K4 conversion factor 0.002668 ((in. Hg)(ft3))/((ml)(°R)) kg kilogram Kp pitot tube constant (85.49 ft/sec) kwscfh thousand wet standard cubic feet per hour l liters lb/hr pounds per hour lb/MMBtu pounds per million Btu lpm liters per minute m meter or milli M thousand (English units) or mega (million, metric units) m3 cubic meters ma mass of residue of acetone after evaporation, mg Md molecular weight of stack gas; dry basis, lb/lb-mole meq milliequivalent mg milligram Mg megagram (106 grams) min minute ml or mL milliliter mm millimeter MM 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 megawatt n number of data points ng nanogram nm nanometer Pbar barometric pressure, inches Hg pg picogram Pg stack static pressure, inches H2O Pm barometric pressure of dry gas meter, inches Hg ppb parts per billion ppbv parts per billion, by volume ppbvd parts per billion by volume, dry basis ppm parts per million ppmv parts per million, by volume ppmvd parts per million by volume, dry basis ppmvw parts per million by volume, wet basis Ps absolute stack gas pressure, inches Hg psi pounds per square inch psia pounds per square inch absolute psig pounds per square inch gauge Pstd standard absolute pressure, 29.92 inches Hg Qa volumetric flow rate, actual conditions, acfm Qs volumetric flow rate, standard conditions, scfm Qstd volumetric flow rate, dry standard conditions, dscfm R ideal gas constant 21.85 ((in. Hg) (ft3))/((°R) (lbmole)) GP043AS-022762-PP-770 Page 24 of 46 UNITS AND ABBREVIATIONS SBfinal post-run system bias check, % of span SBi pre-run system bias check, % of span scf standard cubic feet scfh standard cubic feet per hour scfm standard cubic feet per minute scm standard cubic meters scmh standard cubic meters per hour sec second sf, sq. ft., or ft2 square feet std standard t metric ton (1000 kg) T 0.975 t-value Ta absolute average ambient temperature, ºR (+459.67 for English) Tm 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) Tstd absolute temperature at standard conditions V volt Va volume of acetone blank, ml Vaw volume of acetone used in wash, ml Vlc total volume H2O collected in impingers and silica gel, grams Vm volume of gas sampled through dry gas meter, ft3 Vm(std)volume of gas measured by the dry gas meter, corrected to standard conditions, dscf Vma stack gas volume sampled, acf Vn volume collected at stack conditions through nozzle, acf Vs average stack gas velocity, feet per second Vwc(std)volume of water vapor condensed, corrected to standard conditions, scf Vwi(std)volume of water vapor in gas sampled from impingers, scf Vwsg(std)volume of water vapor in gas sampled from silica gel, scf W watt Wa weight of residue in acetone wash, mg Wimp total weight of impingers, grams Wsg total weight of silica gel, grams Y dry gas meter calibration factor, dimensionless GP043AS-022762-PP-770 Page 25 of 46 AAS atomic absorption spectroscopy ACDP air contaminant discharge permit ACE analyzer calibration error, percent of span AD absolute difference ADL above detection limit AETB Air Emissions Testing Body AS applicable standard (emission limit) ASTM American Society For Testing And Materials BACT best achievable control technology BDL below detection limit BHP brake horsepower BIF boiler and industrial furnace BLS black liquor solids CC confidence coefficient CD calibration drift CE calibration error CEM continuous emissions monitor CEMS continuous emissions monitoring system CERMS continuous emissions rate monitoring system CET calibration error test CFR Code of Federal Regulations CGA cylinder gas audit CHNOS elemental analysis for determination of C, H, N, O, and S content in fuels CNCG concentrated non-condensable gas CO catalytic oxidizer COC chain of custody COMS continuous opacity monitoring system CPM condensible particulate matter CPMS continuous parameter monitoring system CT combustion turbine CTM conditional test method CTO catalytic thermal oxidizer CVAAS cold vapor atomic absorption spectroscopy De equivalent diameter DE destruction efficiency Dioxins polychlorinated dibenzo-p-dioxins (pcdd's) DLL detection level limited DNCG dilute non-condensable gas ECD electron capture detector EIT Engineer In Training ELCD electoconductivity detector (hall detector) EMPC estimated maximum possible concentration EPA US Environmental Protection Agency EPRI Electric Power Research Institute ES emission standard (applicable limit) ESP electrostatic precipitator EU emission unit FCCU fluid catalytic cracking unit FGD flue gas desulfurization FI flame ionization FIA flame ionization analyzer FID flame ionization detector FPD flame photometric detector FPM filterable particulate matter FTIR Fourier-transform infrared spectroscopy FTPB field train proof blank FTRB field train recovery blank Furans polychlorinated dibenzofurans (pcdf's) GC gas chromatography ACRONYMS GP043AS-022762-PP-770 Page 26 of 46 ACRONYMS GC/MS gas chromatography/mass spectroscopy GFAAS graphite furnace atomic absorption spectroscopy GFC gas filter correlation GHG greenhouse gas HAP hazardous air pollutant HC hydrocarbons HHV higher heating value HPLC high performance liquid chromatography HRGC/HRMS high-resolution gas chromatography/high-resolution mass spectroscopy HRSG heat recovery steam generator IC ion chromatography ICAP inductively-coupled argon plasmography ICPCR ion chromatography with a post-column reactor ICP-MS inductively coupled plasma-mass spectroscopy IR infrared radiation ISO International Standards Organization kW kilowatts LFG landfill gas LHV lower heating value LPG liquified petroleum gas MACT maximum achievable control technology MDI methylene diphyenyl diisocyanate MDL method detection limit MNOC maximum normal operating conditions MRL method reporting limit MS mass spectrometry NA not applicable or not available NCASI National Council For Air And Steam Improvement NCG non-condensable gases ND not detected NDIR non-dispersive infrared NESHAP National Emissions Standards For Hazardous Air Pollutants NG natural gas NIOSH National Institute For Occupational Safety And Health NIST National Institute Of Standards And Technology NMC non-methane cutter NMOC non-methane organic compounds NMVOC non-methane volatile organic compounds NPD nitrogen phosphorus detector NSPS New Source Performance Standards OSHA Occupational Safety And Health Administration PAH polycyclic aromatic hydrocarbons PCB polychlorinated biphenyl compounds PCW P plywood and composite wood products PE Professional Engineer PFAS per- and polyfluoroalkyl substances (PFAS) PI photoionization PID photoionization detector PM particulate matter PM10 particulate matter less than 10 microns in aerodynamic diameter PM2.5 particulate matter less than 2.5 microns in aerodynamic diameter POM polycyclic organic matter PS performance specification PSD particle size distribution PSEL plant site emission limits PST performance specification test PTE permanent total enclosure PTM performance test method GP043AS-022762-PP-770 Page 27 of 46 ACRONYMS QA/QC quality assurance and quality control QI Qualified Individual QSTI Qualified Source Testing Individual RA relative accuracy RAA relative accuracy audit RACT reasonably available control technology RATA relative accuracy test audit RCTO rotary concentrator thermal oxidizer RICE stationary reciprocating internal combustion engine RM reference method RTO regenerative thermal oxidizer SAM sulfuric acid mist SCD sulfur chemiluminescent detector SCR selective catalytic reduction system SD standard deviation Semi-VOST semivolatile organic compounds sample train SRM standard reference material TAP toxic air pollutant TBD to be determined TCA thermal conductivity analyzer TCD thermal conductivity detector TGNENMOC total gaseous non-ethane non-methane organic compounds TGNMOC total gaseous non-methane organic compounds TGOC total gaseous organic compounds THC total hydrocarbons TIC tentatively identified compound TO thermal oxidizer TO toxic organic (as in EPA Method TO-15) TPM total particulate matter TSP total suspended particulate matter TTE temporary total enclosure ULSD ultra-low sulfur diesel UV ultraviolet radiation range VE visible emissions VOC volatile organic compounds VOST volatile organic sample train W C water column W WTP waste water treatment plant GP043AS-022762-PP-770 Page 28 of 46 Ag silver Se selenium As arsenic SO2 sulfur dioxide Ba barium SO3 sulfur trioxide Be beryllium SOx sulfur oxides C carbon TCDD tetrachlorodibenzodioxin Cd cadmium TCDF tetrachlorodibenzofuran CdS cadmium sulfide TGOC total gaseous organic concentration CH2O formaldehyde THC total hydrocarbons CH3CHO acetaldehyde Tl thallium CH3OH methanol TRS total reduced sulfur compounds CH4 methane Zn zinc C2H4O ethylene oxide C2H6 ethane C3H4O acrolein C3H6O propionaldehyde C3H8 propane C6H5OH phenol Cl2 chlorine ClO2 chlorine dioxide CO carbon monoxide Co cobalt CO2 carbon dioxide Cr chromium Cu copper EtO ethylene oxide EtOH ethyl alcohol (ethanol) H2 hydrogen H2O water H2O2 hydrogen peroxide H2S hydrogen sulfide H2SO4 sulfuric acid HCl hydrogen chloride Hg mercury IPA isopropyl alcohol MDI methylene diphyenyl diisocyanate MeCl2 methylene chloride MEK methyl ethyl ketone MeOH methanol Mn manganese N2 nitrogen NH3 ammonia Ni nickel NO nitric oxide NO2 nitrogen dioxide NOx nitrogen oxides O2 oxygen P phosphorus Pb lead PCDD polychlorinated dibenzo-p-dioxins PCDF polychlorinated dibenzofurans Sb antimony CHEMICAL NOMENCLATURE GP043AS-022762-PP-770 Page 29 of 46 Appendix A.2 Accreditation Information/Certifications GP043AS-022762-PP-770 Page 30 of 46 Accredited Air Emission Testing Body A2LA has accredited MONTROSE AIR QUALITY SERVICES In recognition of the successful completion of the joint A2LA and Stack Testing Accreditation Council (STAC) evaluation process, this laboratory is accredited to perform testing activities in compliance with ASTM D7036:2004 - Standard Practice for Competence of Air Emission Testing Bodies. Presented this 4th day of February 2022. _______________________ Vice President, Accreditation Services For the Accreditation Council Certificate Number 3925.01 Valid to February 29, 2024 This accreditation program is not included under the A2LA ILAC Mutual Recognition Arrangement. A merican Association for Laboratory Accreditation GP043AS-022762-PP-770 Page 31 of 46 Appendix “S” Field Work Safety Plan GP043AS-022762-PP-770 Page 32 of 46 SITE SAFETY PLAN BOOKLET Project: _____________________ Customer: ___________________ Location: ____________________ Units: _______________________ Client Project Manager: ______________________ Revision Date: January 21, 2022 GP043AS-022762-PP-770 Page 33 of 46 Page 1 of 2 Site Safety Plan and JHA Purpose and Instructions Purpose 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. Instructions The SSP consists of the following: communicated to all employees, signed, and posted. Supervisor/ CPM will ensure that this Emergency Action Plan Form is completed, CPM will maintain a roster and be responsible for accounting for all employees. The Job to work commencing. In the event of an emergency situation/ evacuation, the Job Supervisor/ emergency and evacuation procedures, assembly/ rally points, alert systems, and signals prior the Emergency Action Plan form and ensure that all employees are familiar with the facility 4. Emergency Action Plan - The Job Supervisor/ Client Project Manager (CPM) will complete observed plus applicable PPE that may be required. administrative controls that a crew can use to reduce or eliminate the hazards they have 3. Hazard Control Matrix - contains useful information on both engineering and with the toolbox topic and signatures can be added to the SSP packet. the hazard analysis is required daily for the duration of the test. An additional sheet of paper modified when conditions change. A toolbox meeting with a daily topic in addition to a review of sign on the Job Hazard Analysis form in agreement and sign in Section 10. The JHA is to be Each team member has the option to discuss making changes or adding to the JHA and must Section 9 will require at least three tasks, hazards and controls be identified for the project. form for accuracy, making any corrections required and complete the remainder of the JHA. complete the JHA form through section 8. Upon arrival at the test site, the team will review the daily hazard review with sign off by the team. The client Project Manager is responsible to task/site’s particular hazards and controls. The form also includes a daily toolbox topic and 2. A Job Hazard Analysis is a standardized, two-page, fillable form that is used to evaluated the prior to the test. 1. A Pre-Mobilization Test Plan – To be completed in it’s entirety by the client project Manager AQS-FRM-1.13R1 Extended Hours Formc. Heat Stress Prevention Form Based on Heat Indexb. MEWP Lift Inspection Forma. Additional Forms, as applicable5. GP043AS-022762-PP-770 Page 34 of 46 Page 2 of 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 GP043AS-022762-PP-770 Page 35 of 46 Page 1 of 2 PRE-MOBILIZATION TEST INFORMATION Source Type: New Source: ____ Revisit: ____ Prj#/Date/Tech: __________________________ Coal Fired Electric Utility: ____ Ethanol Plant: ____ Chemical Mfg. of _________________________ Cement/Lime Kiln Plant: ____ Specialty Mfg. of: ___________ Other: _______________ Anticipated Effluent Composition – check all that apply and fill in expected concentration in ppm/% CO NOX SO2 VOC other If other, explain: _______________________________________________________ Flammable: _______ Toxic: ________ Corrosive: _______ Dust: __________ Engineering Controls to be Implemented: ______________________________________________________________________________________ __________________________________________________________________________________ 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 If other, explain: _______________________________________________________ Approximate Duct Pressure, (iwg): below -3 -3 to +3 +3 to +7 above +7 other If other, explain: _______________________________________________________ PROJECT NAME/LOCATION: ______________________ PROJECT #: ____________________ TEST DATE: ______________________ PROJECT MANAGER: ___________________ TEST SCOPE: _________________________________________________________________ SITE CONTACT: Name: _____________________ Contact Phone: _________________________ AQS-FRM-1.17 GP043AS-022762-PP-770 Page 36 of 46 Page 2 of 2 PRE-MOBILIZATION TEST INFORMATION Sampling Location: Stack Port ____ Duct Port ____ Approximate Sampling Platform Height, (ft) Effluent Chemical Regulatory Limits Gas Name Chemical Formula Cal OSHA PEL1 (ppm) Cal OSHA STEL2 (ppm) NIOSH REL TWA3 (ppm) Cal OSHA Ceiling (ppm) IDLH4 (ppm) Carbon Monoxide CO 25 200 35 200 1,200 Nitric Oxide NOx 25 ND5 25 ND 100 Sulfur Dioxide SO2 2 5 2 ND 100 Hydrogen Chloride HCl 0.3 2 ND 2 50 Hydrogen Sulfide H2S 10 15 10 (10 min.)C 50 100 1: California Occupational Safety and Health Administration (OSHA) Permissible Exposure Limit (PEL) based on an 8-hour shift; 2: Cal OSHA Short-term Exposure Limit (STEL) based on a 15-minute period; 3: National Institute for Occupational Safety and Health (NIOSH) Recommended Exposure Limit (REL) Time-weighted Average (TWA) based on an 8-hour shift; 4: Immediately Dangerous to Life or Health (IDLH); 5: Not Defined (ND); C: Ceiling Limit - Maximum allowable human exposure limit for an airborne or gaseous substance, which is not to be exceeded, even momentarily. Prepared by: Date: Reviewed by: Date: ______________________________________________________________________________ ______________________________________________________________________________ Additional Information: ______________________________________________________________________________ ______________________________________________________________________________ Describe how equipment will be mobilized to the sampling location: Other:_____________________________________________________________________________ Guardrails: ____ Toe plate: ____ Engineered Tie Off Points: ____ Heat Shield: ____ Elevators: ____ Ladders: ____ MEWP Lift: ____ Scaffold: ____ Equipment Hoist: ____ Access and Protection: If other, explain: _______________________________________________________ below 6 6 to 50 50 to 100 above 100 other AQS-FRM-1.17 GP043AS-022762-PP-770 Page 37 of 46 Job Hazard Analysis 1 of 3 1. Client Rep Job Preparation Job Site Walk Through Completed Site Specific Training Complete Safe Work Permit Received from Client 2.Facility Information/Emergency Preparedness If non-emergency medical attention is needed, call: AXIOM #: 877-502-9466. Plant Emergency # Certified First Aid Person: EMS Location Evacuation Routes Rally Point Severe Weather Shelter Location Eye Wash & Safety Shower Location Operational: Yes No Source Information: (list type): Stack Gas Temp. (oF)Stack Gas Press. ("H2O)Stack Gas Components: Stack Gas Inhalation Potential?Yes No If yes, see List of Hazard Chemicals. 3.Error Risk Time Pressure Remote Work Location > 12 hr shift Working > 8 consecutive days Lack of procedures Extreme temps, wind >30mph Personal illness/fatigue Vague work guidance Monotonous Activity First day back after time off Multiple job locations Other: 4.Physical Hazards Hazard Controls Dust Hazards Dust Mask Goggles Other: Thermal Burn Hot Gloves Heat Shields Other Protective Clothing: Electrical Hazards Connections Protected from Elements External GFCI Other: XP Rating Requirement Intrinsically Safe Requirement Inadequate Lighting Install Temporary Lighting Headlamps Slip and Trip Housekeeping Barricade Area Other: Hand Protection Cut Resistant Gloves Pinch Pts.General Electrical Impact Resistant Other: Potential Hazards for Consideration Secondary Permits Hot Work Confined Space Excavation Working from Heights Falling objects Fall protection Drop zone protection Platform load ratings See also Sect. 7 Scaffold inspection Ladder inspection Barricades for equipment Electrical Exposed wire/connector Verify equipment grounding Arc Flash Lifting Crane lift plan Rigging inspection Tag lines used Hoists in place Respiratory Unexpected exposure Chemical Dust (combustible)PEL provided See also Sect. 8 Cartridges or supplied air available Gas detection equipment 5.Required PPE Hard Hats Safety Glasses Safety Toe Shoe/Boot Hearing Protection Safety Spotter Hi-Vis Vests Harness/Lanyard*Goggles Personal Monitor Type: Metatarsal Guards Hot Gloves Face Shield Respirator Type: Nomex/FRC Other PPE: Client Contact Name Date Facility SSP Writer PM If the heat index is expected to be above 91°, fill out the Heat Stress Prevention Form. All hazards and mitigation steps must be documented. If this JHA does not cover all the hazards identified, use Section 9 to document that information. AQS-FRM-1.18 GP043AS-022762-PP-770 Page 38 of 46 Job Hazard Analysis 2 of 3 Additional Work Place Hazards 6.Critical Procedures – check all that apply – *indicates additional form must be completed or collected from client Heat Stress Prevention*Confined Space*Roof Work Scaffold Cold Weather Work Hazardous Energy Control*Other: 7.Working From Heights Fall Protection Fixed Guardrails/Toe boards Fall Prevention PPE Warning Line System Falling Objects Protection Barricading Netting House Keeping Tethered Tools Catch Blanket or Tarp Fall Hazard Communication Adjacent/Overhead Workers Contractor Contact Client Contact 8.Other Considerations Environmental Hazards - Weather Forecast Heat/Cold Lightning Rain Snow Ice Tornado Wind Speed Steps for Mitigation: Electrical Safety Planning Plant Hook up:110V 220/240V 480V Generator Hard wired into panel Electrical Classified Area: Yes No Trailer Grounded: Yes No Plug Type Electrical Hook Up Responsibility: List of Hazardous Chemicals Other Chemicals: Acetone Nitric Acid Hydrogen Peroxide Compressed Gases Hexane Sulfuric Acid Isopropyl Alcohol Flammable Gas Toluene Hydrochloric Acid Liquid Nitrogen Non-Flammable Gas H2S Carbon Monoxide Steps for Mitigation: Wildlife/Fauna in Area Poison Ivy Poison Oak Insects:Wildlife: Personnel w/ known allergies to bees stings or other allergens?Yes No 9.Observed Hazards and Mitigation Steps Task Potential Hazard(s)Steps for Mitigation ● 1 1 2 2 3 3 ● 1 1 2 2 3 3 ● 1 1 2 2 3 3 ● 1 1 2 2 3 3 Exposure Monitoring MEWP* AQS-FRM-1.18 GP043AS-022762-PP-770 Page 39 of 46 Job Hazard Analysis 3 of 3 10.JHA REVIEW: Crew Names & Signatures 11.Daily JHA Meeting & Review Items to review: ● Change in conditions ● Extended work hours ● Daily Safety Topic ● New workers or contractors ● Occurrence of near misses or injuries Printed Name Signature 2 Discussion TopicDay Initialing demonstrates that site conditions and hazards have not changed from the original SSP. If changes did occur, make the necessary updates to this JHA and add notes as applicable in Section 9. Initials 9 8 7 6 3 Date Printed Name Signature Date 5 4 11 10 AQS-FRM-1.18 GP043AS-022762-PP-770 Page 40 of 46 1 2 3 4 5 6 Local Hospital/ Clinic Telephone Number: 7 8 9 10 11 12 13 14 15 16 17 MEG Job Supervisor/ CPM's Telephone Number: Plant's #1 Contact Person's Name: Plant's #1 Contact Person's Telephone Number: MEG Job Safety Supervisor's Telephone Number: Plant's Emergency Telephone Number: Emergency Ops Radio Channel: The Fire Extinguisher is Located: Eye Wash and Safety Shower Location: The First Aid Kit is Located: Page 1 of 2 The Job Supervisor/ Client Project Manager (CPM) will ensure that all employees are familiar with the facility emergency and evacuation procedures, assembly/ rally points, alert systems, and signals prior to work commencing. In 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, and posted. • You must follow the client’s emergency action plan first, and notify your Supervisor immediately. •If incident is life threatening, CALL 911 IMMEDIATELLY • If non-emergency medical attention is needed, call AXIOM Medical number: 877-502-9466. EMERGENCY ACTION PLAN FORM MEG Job Supervisor/ CPM's Name: MEG Job Safety Supervisor (if applicable): Evacuation Routes: Severe Weather Shelter Location: Plant's #2 Contact Person's Name: Plant's #2 Contact Person's Telephone Number: Designated Assembly Point Location: AQS-FRM-1.11 GP043AS-022762-PP-770 Page 41 of 46 1 2 4 5 Signature:Date:Printed Name:Signature:Date: EVACUATE:____________________________________; OTHER:_______________________________________; Alarm Tones: EMERGENCY ACTION PLAN FORM AND EVACUATION ASSEMBLY MAP REVIEW: Crew Names and Signatures Printed Name: Draw the evacuation and assembly map here Page 2 of 2 EMERGENCY EVACUATION AND ASSEMBLY MAP 3 Designated Shelter(s) Description: Designated Assembly Point(s) Description: YES or NO Facility Name: Facility Alarm (Circle): FIRE:_________________________________________; CHEMICAL/ GAS:_______________________________; SHELTER-IN-PLACE:_____________________________; AQS-FRM-1.11 GP043AS-022762-PP-770 Page 42 of 46 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. • Check “N/A” to indicate “Not Applicable.” Yes No N/A ☐ ☐ ☐ 2. Hydraulic fluid level is sufficient, with the platform fully lowered ☐ ☐ ☐ 3. Hydraulic system pressure (see manufacturer specs) is acceptable. If 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. worn 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 clearly marked. ☐ ☐ ☐ 10. Manufacturer’s Instruction 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 otherwise specified by manufacturer recommendations. ☐ ☐ ☐ Number Item to be Inspected Operator Name & Signature Location Date Ground Control Name & Signature Location Date Harness Inspections: Printed Name Signature Date Printed Name Signature Date Printed Name Signature Date Daily MEWP Lift Inspection Form Page 1 of 1 at the beginning of each shift or following 6 to 8 hours of use. All checks must be completed prior to each work shift, before operation of the MEWP lift. This checklist must be used MEWP Lift Model #: loose hoses, etc.) – if something can be easily loosened by hand then it is not sufficient. 1. All MEWP lift components are in working condition (i.e. no loose or missing parts, torn or Items to be Inspected AQS-FRM-1.16 GP043AS-022762-PP-770 Page 43 of 46 Page 1 of 1 001AS-SAFETY-FM-3 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 meeting Test crew initials: The test leader should look for signs of the following in their crews: • Irritability • Lack of motivation • Headaches • Giddiness • Fatigue • Depression • Reduced alertness, lack of concentration and memory The test leader should assess the environmental and hazardous concerns: • Temperature and weather • Lighting • Working from Heights • Hoisting • PPE (i.e. respirators, etc.) • Pollutant concentration in ambient air (SO2, H2S, ect.) N • Reason for extended hours • Reason for delay ▪ Production limitations • Impending Weather 3. 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. Final Outcome: Approver: During this time, they can come to an agreement on how to proceed. Items to discuss include: extended work period. If the DM is the acting PM on the job site, they must contact the RVP. The PM must contact either the DM or RVP to discuss the safety issues that may arise due to the Notify DM or RVP2. GP043AS-022762-PP-770 Page 44 of 46 Page 1 of 1 001AS-SAFETY-FM-5 Heat Stress Prevention Form This form is to be used when the Expected Heat Index is above 91° F, and is to be kept with project documentation. Project Manager (PM): Expected High Temp: Date(s): Expected Heat Index: 1. Review the signs of Heat Exhaustion and Heat Stroke 2. If Heat Index is above 91° F: • Provide cold water and/or sports drinks to all field staff (avoid caffeinated drinks and energy drinks which can increase core temperature). o Bring no less than one gallon of water per employee • If employee(s) are dehydrated, on blood pressure medication or not acclimated to heat, ensure they are aware of the heightened risk for heat illness • Provide cool head bands/vests/etc. • Have ice available to employees • Implement 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 3. If Heat Index 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 drinks • 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 GP043AS-022762-PP-770 Page 45 of 46 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: Craig Kormylo Title: District Manager Region: Great Plains Email: ckormylo@montrose-env.com Phone: (303) 670-0530 GP043AS-022762-PP-770 Page 46 of 46