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HomeMy WebLinkAboutDRC-2022-015041 - 0901a0688109e5e7.,‘ Vs‘ State of Utah SPENCER J. COX Governor DEIDRE HENDERSON Lieutenant Governor Department of Environmental Quality Kimberly D. Shelley Executive Director DIVISION OF WASTE MANAGEMENT AND RADIATION CONTROL Douglas J. Hansen Director D RC-2022- o15 34- TO: File THROUGH: Phil Goble, Manager FROM: Tom Rushing, P.G. DATE: June 16, 2022 MEMORANDUM P, 6 4,146b 06/16/2022 Thomas , 2022 09 55 MDT) 06/16/2022 SUBJECT: Review of the Energy Fuels Resources (USA) Inc. lst Quarter 2022 Ground Water Monitoring Report for the White Mesa Uranium Mill Review Summary: The Utah Division of Waste Management and Radiation Control ("Division") has reviewed the following documents submitted by Energy Fuels Resources (USA) Inc. ("EFR"): 1. EFR, May 5, 2022, Transmittal of .1sl Quarter 2022 Groundwater Monitoring Report Groundwater Quality Discharge Permit UGW370004 White Mesa Uranium Mill (Received by the Division on May 11, 2022). 2. EFR, May 2, 2022, State of Utah Ground Water Discharge Permit No. UGW370004 White Mesa Uranium Mill — Notice Pursuant to Part I.G.1(a) (Received by the Division cm May 4, 2022. The review was conducted to ensure compliance with all applicable parts of Utah Groundwater Discharge Permit No. UGW370004 ("Permit") issued for the White Mesa Uranium Mill located in Blanding, Utah (Mill). 1. Checklist of Significant Findings of the 1st Otr. 2022 Report and Related Actions at the White Mesa Uranium Mill: 1. The 1st Quarter 2022 Report was received on May 5, 2022, which was before the due date (Permit Part I.F.1 - due date of June 1). 2. DWMRC notes that samples were analyzed by American West Analytical Laboratories ("AWAL"), Chemtech-Ford Laboratories ("Chemtech") and for Gross 195 North 1950 West • Salt Lake City, UT Mailing Address: P.O. Box 144880 • Salt Lake City, UT 84114-4880 Telephone (801) 536-0200 • Fax (801)-536-0222 • T.D D (801) 536-4414 www deg utah gov Printed on 100% recycled paper EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 2 Alpha analyzed by GEL Laboratories LLC, Charleston, South Carolina. DWMRC verified that the laboratories have current Utah certification for the parameters analyzed. It was noted that GEL laboratories has addressed issues noted on previous reports regarding the method used for gross alpha radium and is now reporting that method 903.0 is used. This method is now included in the facility QAP, and GEL has current Utah certification to use that method. 3. Laboratory QA/QC flags were documented in the review period analytical data reports from the contract laboratories and an in-house QA/QC review was conducted by EFR regarding all field and laboratory data. Per DWMRC review it appears that all discrepancies were self-reported by EFR. 4. Per review of the 1st Qtr. 2022 groundwater head measurements, it was noted that Piez-3A shows an approximate 3 ft. rise in water elevation. Per follow up communication with EFR it was noted that the same rise is noted in the 1st Qtr. And 2nd Qtr. 2022 water elevations taken during sampling. EFR is investigating potential causes of the Piez-3A water elevation rise. 2. Accelerated Monitoring and POC Wells Exceeding GWCL's: When a monitoring well has a pollutant that exceeds a Ground Water Compliance Limit (GWCL) set forth in Table 2 of the Permit, it is in Probable Out-of-Compliance (POOC) status. According to the Permit, EFR is then required to immediately initiate accelerated sampling of that pollutant (see the Permit, Part I.G.1). When monitoring wells have parameters that have exceeded the Ground Water Compliance Limit (GWCL) two or more consecutive times they are in Out-of- Compliance (00C) status (see the Permit, Part I.G.2). In the event a constituent is in 00C status, EFR is required to prepare and submit within 30 calendar days to the Director a plan and time schedule for assessment of the sources, extent and potential dispersion of the contamination, and an evaluation of potential remedial action to restore and maintain groundwater quality to ensure that Permit limits will not be exceeded at the compliance monitoring point and that DMT or BAT will be re-established, in accordance with Part I.G.4(c) of the Permit. One new compliance parameter went into accelerated monitoring frequency (POOC) based on sampling during the St Quarter 2022 (Nitrate + Nitrite in Monitoring Well MW-11). Current Accelerated Monitoring Status: The table below (Table 1) lists monitoring wells with parameters currently in 00C or POOC status and therefore required to be sampled under the accelerated monitoring requirements: Table 1 - Wells Monitored Quarterly Accelerated to Monthly Monitoring Well Class *Position Parameter Date of First Exceedance of GWCL Date Accelerated Monitoring First Required MW-1 1 Class 11 water D-3 Chloride 3rd Quarter 2019 November 2019 EFR 1 st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 3 Well Class *Position Parameter Date of First Exceedance of GWCL Date Accelerated Monitoring First Required Sulfate Total Dissolved Solids Manganese Nitrate + Nitrite (as N) 3" Quarter 2019 3rd Quarter 2021 i -.rd .-", yuarter 2021 1" Quarter 2022 November 2019 November 2021 November 2021 June 2022 MW-25 Total Dissolved Solids 3rd Quarter 2021 November 2021 MW-26(a) Class III water C- 2 Nitrate + Nitrite (as N) Chloroform Chloride Carbon Tetrachloride Methylene Chloride Total Dissolved Solids February 2010 February 2010 February 2010 1' Quarter 2021 3" Quarter 2020 3rd Quarter 2021 May 2010 May 2010 May 2010 2nd Quarter 2021 August 2020 November 2021 MW-30 Class II water D-2 Nitrate + Nitrite (as N) Chloride Uranium Selenium Total Dissolved Solids February 2010 1" Quarter 2011 1" Quarter 2021 1" Quarter 2021 3rd Quarter 2021 May 2010 May 2011 2nd Quarter 2021 2nd Quarter 2021 November 2021 MW-31 Class III water D-2 Nitrate + Nitrite (as N) Chloride Total Dissolved Solids Sulfate Uranium 1" Quarter 2010 1' Quarter 2011 3" Quarter 2019 i -.rd ..-sti y after 2019 2nd Quarter 2020 May 2010 May 2011 November 2019 November 2019 August 2020 D = Down-gradient; U = Up-gradient; C = Cross-gradient; a = Monitoring well MW-26 is a pumping well for the Wells Monitored Semi-annually Accelerated to Quarterly 1,2,3,4A, 4B = Chloroform investigation Monitoring Date of First Exceedance of GWCL Cell # Date Accelerated Monitoring First Required Well Class *Position Parameter MW-12 Class III water D-3 Uranium Selenium 2' Quarter 2017 2nd Quarter 2020 3' Quarter 2017 3rd Quarter 2020 MW-24 Class III water D-1 Beryllium Cadmium Thallium Field pH Fluoride Nickel Manganese Sulfate Gross Alpha Total Dissolved Solids 4' Quarter 2017 2nd Quarter 2018 2nd Quarter 2018 2" Quarter 2018 4th Quarter 2018 4th Quarter 2018 4" Quarter 2019 1" Quarter 2020 4th Quarter 2020 2" Quarter 2021 1" Quarter 2018 3' Quarter 2018 3' Quarter 2018 3" Quarter 2018 3rd Quarter 2019 3rd Quarter 2019 1" Quarter 2020 3rd Quarter 2020 3rd Quarter 2021 3rd Quarter 2021 MW-27 Class III water U-1 Nitrate + Nitrite (as N) 2nd Quarter 2010 3rd Quarter 2010 MW-28 Class III water D-1 Chloride Cadmium Uranium Selenium 2" Quarter 2010 2' Quarter 2014 2" Quarter 2014 2nd Quarter 2019 3rd Quarter 2010 2nd Quarter 2014 2nd Quarter 2014 3rd Quarter 2019 EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 4 Well Class *Position Parameter Date of First Exceedance of GWCL Date Accelerated Monitoring First Required Nitrate + Nitrite (as N) 4th Quarter 2019 3rd Quarter 2020 MW-29 Class III water D-2 Uranium 4th Quarter 2020 3' Quarter 2021 MW-32 Class III water C-2 Chloride 1" Quarter 2015 2' Quarter 2014 * D = Down-gradient; U = Up-gradient; C = Cross-gradient; 1, 2, 3, 4A, 4B = Cell # Table 1 above is a comprehensive list of all Groundwater Monitoring Wells in Accelerated Status as of the 1st Quarter of 2022. EFR is required to notify the DWMRC on a quarterly basis regarding wells and parameters which went into accelerated monitoring during the period [Part I.G.1(a), Accelerated Monitoring Status Reports (AMSR)]. For the 1st Quarter 2022 monitoring, the AMSR was dated May 2, 2022. Review of the AMSR is included in a separate section below. 3. Monitoring Wells Purged for Two Casing Volumes Before Sample Collection: As stated in Section 6.2.7 of the EFR Quality Assurance Plan (QAP), Rev. 7.6, EFR has a choice regarding purge volumes as follows: "1. Purging three well casing volumes with a single measurement offield parameters 2. Purging two casing volumes with stable field parameters (within 10% RPD) 3. Purging a well to dryness and stability of a limited list offield parameters afier recovery" Per DWMRC review of the Report, the following purge methods were used during the 1st Quarter 2021 (including accelerated samples). Purge methods and volumes are summarized in Tab G, on Table G-1A and G-1B of the Report: Quarter # Purged 2 Casing # Purged to Dryness # Purged 3 Casing Volumes Volumes 1 st Qtr. 2022 21 3 3 (continuous pumping) When purging two casing volumes, the QAP directs EFR to first calculate the amount of time to evacuate two casing volumes and then to pump for that length of time. Per DWMRC cross-check of the field data sheets for each of the reports reviewed, it appears EFR correctly calculated the well casing volumes and evacuated the required two volumes (when 2 casing volume method selected) in monitoring wells prior to sample collection during the 1st Quarter 2022 monitoring period. Volumes are calculated according to measured pump rates and can be verified by calibration marks on the collection containers. During the 1st Quarter 2022 monitoring period three monitoring wells were pumped or bailed to dryness. In cases where wells are evacuated to dryness the QAP Rev. 7.4 (Attachment 2-3) requires that: "(vii) If the well is purged to dryness: EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 5 Record the number of gallons purged on the Field Data Worksheet. The well should be sampled as soon as a sufficient volume of groundwater is available to fill sample containers. Upon arrival at the well after recovery or when sufficient water is available for sampling measure depth to water and record on the Field Data Worksheet. Take one set of measurements offield parameters for pH, specific conductance, and temperature only. Collect the samples into the appropriate sample containers. Take an additional set of measurements offield parameters for pH, specific conductance and temperature after the samples have been collected. If the field parameters of pH, specific conductance and temperature are within 10% RPD the samples can be shipped for analysis. If the field parameters of pH, specific conductance and temperature are not within 10% RPD, dispose of the sample aliquots, and purge the well again as described above. Repeat this process, i f necessary, for three complete purging events. If after the third purging the event, the parameters of pH, specific conductance and temperature do not stabilize to within 10% RPD, the well is considered sufficiently purged and collected samples can be submitted for analysis." DWMRC staff verified that in cases where the monitoring well was evacuated to dryness and samples were collected, the number of gallons evacuated was recorded in compliance with the QAP. Additionally, depth to water before sample collection was recorded on all applicable field data worksheets which resolved past DWMRC comments. 4. Relative Percentage Difference Calculations and Radiological Comparisons for Blind Duplicate Analysis DWMRC conducted a review of the blind duplicate samples collected during the 1st Quarter 2022. Per the QAP, one blind duplicate must be collected with each sample batch. DWMRC confirmed that one blind duplicate was collected for each batch — 3 total during the quarterly event — one with the baseline samples (MW-31/MW-65 on 1/19/2022); and two with the accelerated samples, (MW-30/MW-65 on 2/9/2022) and (MW-11/MW-65 on 3/8/2022). The duplicates are required to be within 20% Relative Percent Difference (RPD), unless "the measured concentrations are less than 5 times the required detection limit (Standard Methods, 1998)." EFR 1 St Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 6 Per the QAP, if any of the samples do not meet the comparison criteria (and are not qualified according to the 5 times method detection limit criteria) then EFR is required to conform to the procedures for corrective action listed as follows: 1. Notify the laboratory, 2. Request the laboratory review all analytical results for transcription and calculation errors, and, If the samples are still within holding time, the QA Manager may request the laboratory re- analyze the affected samples. Per DWMRC cross check of the blind duplicate samples collected and analyzed during the lst Quarter 2022 sampling event all results conform to the Permit requirements (within 20% RPD). Radiological duplicate sample results met duplicate counting error requirements in the currently approved QAP for the 1st Quarter 2022. No additional action is required. It was noted that a few of the reported sample results did not meet the radiological counting error requirements of less than 20% of the result, however, in those cases no further action is required based on the QAP condition that the 20% criteria do not have to be met if the sum of the result and error is less than the GWCL. The sum was less than the GWCL in all samples which had a Permit GWCL for comparison. 5. Analytical Laboratories Used by EFR Certified by State of Utah to Perform Analysis for all Analytes: The analytical laboratories (GEL Laboratories LLC, Charleston, SC; Chemtech Ford Laboratory, Sandy, UT; and American West Analytical Laboratories, Salt Lake City, UT) were contracted by EFR to perform analysis on the samples collected during the 1 st Quarter 2021. Per DWMRC review of the National Environmental Laboratory Accreditation Management System Website (cross check of laboratory certification for specific parameters) it appears that the EFR contract laboratories were certified to perform analysis for the specified parameters (Per the laboratory data sheets): GEL Laboratories LLC Current Certification Basic Details Name GEL Laboratories, LLC Type of Lab Not Specified TNI Lab Code TNI00188 EPA Code SC00012 State ID 8037697376 Website Extended Details Primary AB responsible EFR 1St Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 7 for lab demographics Utah Department of Health GIS Location Description Comments Effective Date n/a Commercial Samples Yes Active Yes Location Address Company Contact Carey J. Bocklet Address 1 2040 Savage Road Address 2 City Charleston State South Carolina Zip 29407- Country USA Phone (843) 556-8171 Fax (843) 766-1178 Email cjb@gel.com American West Analytical Laboratories Current Utah Certification Basic Details Name American West Analytical Laboratories Type of Lab Not Specified TNI Lab Code TNI01955 EPA Code UT00031 State ID 8012638686 Website www.awal-labs.com Extended Details Primary AB responsible for lab demographics Utah Department of Health GIS Location Description Comments Effective Date n/a Commercial Samples Yes Active Yes Location Address Company Contact Kyle Gross Address 1 3440 South 700 West EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 8 Address 2 City Salt Lake City State Utah Zip 84119- Country USA Phone (801) 263-8686 Fax (801) 263-8687 Email kyle@awal-labs.com Chemtech Ford Laboratory Current Utah Certification Basic Details Name Chemtech Ford Laboratory Type of Lab Not Specified TNI Lab Code TNI01969 EPA Code UT00027 State ID 8012627299 Website http://www.chemtechford.com/ Extended Details Primary AB responsible for lab demographics Utah Department of Health GIS Location Description Comments Effective Date n/a Commercial Samples Yes Active Yes Location Address Company Chemtech Ford Laboratories Contact David Gayer Address 1 9632 South 500 West Address 2 City Sandy State Utah Zip 84070- Country United States Phone (801) 262-7299 Fax (866) 792-0093 Email dgayer@chemtechford.com 6. Laboratory Report Turn Around Times: EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 9 Per DWMRC review of EFR Table 1 included in the 1" Qtr. 2022 Report, it was noted that laboratory report turnaround times (from date of EFR sample submission to the contract laboratory) for normal frequency monitoring was approximately 30 days for all samples (not including re-submission/corrected reports). Per DWMRC review it was noted that EFR acted quickly to identify any deficiencies in the reports and request corrected versions. There is not a turnaround time requirement in the current QAP; therefore, current turnaround times are judgment based. DWMRC has raised concern over excessive laboratory turn-around times in the past and the Director may require a turn-around date be included in the facility QAP if any future concerns regarding analysis turnaround times are noted. Based on DWMRC review the turn-around times for the ist Quarter 2022, data turn-around times and EFR data review timelines appear to be reasonable/appropriate. 7. Sample Holding Times: Per the Report Section 3.4.2 and Table G-2A in Tab G of the Report, all method holding times and reporting limits were met for each analyte submitted for laboratory analysis (for baseline and accelerated samples). DWMRC staff cross checked all holding time requirements and verified that all samples/analytes appeared to be analyzed within holding times during the 1st Qtr. 2022 reporting period. 8. Sample Preservation: Per review of the 1t Quarter 2022 Report (Part 3.4.3, Tab G, and Laboratory Check-in Sheets) it appears that all samples required to be chilled (<6° C) met the temperature preservation requirements. Per review of the laboratory check in sheets and laboratory QA/QC, no issues related to sample preservation were noted. Per EFR information and method requirements, samples for gross alpha analysis do not have a sample temperature requirement. 9. Sample Trip Blank Evaluation: Per Section 3.4.6 of the Report and Tables in Tab G of the 1st Quarter 2022 Report all trip blank results associated with the quarterly, semi-annual, and accelerated samples were nondetect for volatile organic compounds except for the March monthly trip blank which had a reported concentration of 1.9 µg/L. Per EFR findings regarding the trip blank detection it was noted that since the trip blank results were less than an order of magnitude of the of the sample results, the trip blanks were within the acceptance limits of the QAP. No additional action is warranted. 10. Laboratory QA/QC Flags — 1st Quarter 2022: QA/QC issues and DWMRC findings for the 1" Quarter 2022 are summarized below: EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 10 Non-Conformance-,, , : Summary Self- ' Identified? EFR Corrective Action :. Summary DWMRC Findings r Laboratory reporting limits were raised for various samples/parameters. Y EFR states that the raised RL's are due to sample dilution and qualifies the data based on all sample results being above the raised RL. The EFR QAP allows for raised RL's if due to the need for dilution. DWMRC verified that in all cases when the RL was raised above the QAP required RL the sample result was higher in concentration. Radiological counting error > 20% Y Per the Permit, if the value of the result is less than the appropriate GWCL then the counting error can be > 20% (Table G-8A). The EFR QAP Part 9.1.4.b allows that if the applicable result is less than the GWCL then the counting variance can be greater than 20%. Matrix Spike % recovery outside of range for various wells/parameters. Y Per AWAL Data Sheet: Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS. EFR included the data qualifiers in the footnotes of the Report Tab G. Per the QAP Part 8.1.2(a) matrix spikes are required but there are no requirements which would disqualify the laboratory data. Data was reported with a qualifier. Laboratory Duplicate % Recovery Comparison Outside of Range for various wells/parameters. Y Same AWAL comments as per the matrix spike % recovery item above. EFR included the data qualifiers in the footnotes of the Report Tab G. Data was reported with a qualifier. Note: DWMRC reviewed the holding time summary chart; no exceedances of holding times were noted. DWMRC reviewed the temperature check charts, all sample batches were received by the laboratory <6° C. 11. Review of Time-Concentration Plots The Permit Part I.F.1.g requires EFR to submit Time-Concentration Plots for each monitoring well for primary indicators of cell leakage; chloride, fluoride, sulfate, and uranium. DWMRC notes that per the discussions with EFR, it was agreed to that EFR need not plot trend lines on the Time Concentration Plots and that all data is included on the plots (no data culled from the set). Per DWMRC review of the 1st Qtr. 2022 Report, the reviewed plots appear to be in conformance with the agreed upon changes. P•1 MOD Pa. 1.1,, Pords: P 1 P 2 (bahoem) P (v.,. abonsmsa 20,22 P (*sib Pnsta. 20161 EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 11 12. Review of Depth to Groundwater Measurements and Water Table Contour Maps Per DWMRC cross checks of groundwater elevation measurement calculations used for the 1st Quarter 2022, approximately 5% of wells cross checked, comparing surface casing measured elevations minus measured static levels with plotted elevations, no errors were noted. The upper wildlife ponds at the White Mesa Mill were taken offline (pond recharge from Recapture Reservoir discontinued) during the 4th Quarter 2011 to re-establish groundwater contours. Hydrographs of the upper wildlife pond ground water piezometers (Water Level Elevation vs. Time) are included below (Northern piezometers and southern piezometers). It was also noted that the static water levels in several monitoring wells close to the upper wildlife ponds showed significant decrease in water levels since the ponds were taken offline. These declines can be attributed to natural dissipation of the area ground water mound and/or ground water pumping activities related to corrective action of nitrate and chloroform contamination plumes (development of cone of depressions around pumping wells). Per review of the 1st Qtr. 2022 groundwater elevations, it was noted that Piez-3A shows an approximate 3 ft. rise in water elevation. Per follow up communication with EFR it was noted that the same rise is noted in the 1st Qtr. And 2nd Qtr. 2022 water elevations taken during sampling. EFR is investigating potential causes of the Piez-3A water elevation rise. It/C While MesaMU Flydrographs: Plesansters Cs North W Write Ponds 553 5.532 5531 5530 5525 5,526 5,527 5,526 5525 5.524 5 523 5 522 5521 5 5,515 5515 5514 i EFR 1 st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 12 IUC Wham Mesa Min hlythographs. Pleeofneters kl2, South Wildlife Ponds Nitrate and Chloroform Corrective Action Plan Pumping Wells: Ground water elevations are being impacted by effects from ground water pumping for the nitrate and chloroform contamination plume remediation. The following monitoring wells have been converted to active pumping wells: Nitrate Pumping Wells — TW4-22, TW4-24, TW4-25, TWN-2 (The nitrate pumping project was initiated during January 2013). Chloroform Pumping Wells — MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4- 20, TW4-21, TW4-22, TW4-24, TW4-25, TW4-37, TW4-39. The pumping wells for both the nitrate and chloroform projects are set up with a delay device wherein the wells purge for a set amount of time then shut off to let the well recharge. All pumping wells include a flow meter which records the volume of water pumped from the well in gallons. Quarterly nitrate and chloroform reports are prepared by EFR and include pump volumes and delineation of pump capture zones based on kriged water contours. DWMRC expects that ground water elevation contours will continue to adjust in response to the pumping activities and discontinuance of recharge to the upper wildlife ponds. 13. EFR May 2, 2022, Notice Pursuant to the Permit Part I.G.1(a) The EFR May 2, 2022, Notice Pursuant to the Permit Part I.G. I (a) ("Notice") discusses the status of monitoring wells and parameters in probable out-of-compliance ("POOC") and out-of- EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 13 compliance ("00C") status, as updated through the 1" Quarter 2022. DWMRC notes that the Notice was submitted timely regarding currently agreed upon schedules, reporting of exceedances within 30 days after the end of the monitoring quarter, and has been updated based on issuance of the current modified GWDP (Issued effective March 8, 2021) in effect during the monitoring period. Per the Notice, one new parameter went into POOC or 00C status during the 15` Quarter 2021 (Nitrate + Nitrite as N in MW-11). Based on DWMRC review of the Notice it appears that all requirements of the Permit were met. 14. Conclusions and Recommendations Based on DWMRC staff review of the above listed documents and review the following will be included in a close-out letter: 1. Close-out regarding DWMRC review of the EFR May 5, 2022, 1t Quarter 2022 Groundwater Monitoring Report. 2. Close-out regarding DWMRC review of the EFR May 2, 2022, Notice Pursuant to Part I.G. 1 (a). 15. References 'Energy Fuels Resources (USA) Inc., May 5, 2022, lst Quarter2022 Groundwater Monitoring Report, Groundwater Discharge Permit UGW370004, White Mesa Uranium Mill. 2 Energy Fuels Resources (USA) Inc., May 2, 2022, State of Utah Ground Water Discharge Permit No. UGW370004 White Mesa Uranium Mill — Notice Pursuant to Part I.G.1(a). 3 Energy Fuels Resources (USA) Inc., May 14, 2019, White Mesa Uranium Mill Ground Water Monitoring Quality Assurance Plan (QAP), Revision 7.6. 4 INTERA Incorporated, 2007, Revised Background Groundwater Quality Report: Existing Wells for Dension Mines (USA) Corp. 's White Mesa Uranium Mill Site, San Juan County, Utah. 5 INTERA Incorporated, 2007, Background Groundwater Quality Report: New Wells for Denison Mines (USA) Corp.'s White Mesa Uranium Mill Site, San Juan County, Utah. 6 Hurst, T.G., and Solomon, D.K., 2008. Suinmary of Work Completed, Data Results, Interpretations and Recommendations for the July 2007 Sampling Event at the Denison Mines, USA, White Mesa Uranium Mill located near Blanding Utah. Prepared by University of Utah Department of Geology and Geophysics. EFR 1st Quarter 2022 Groundwater Monitoring Report DWMRC Review Memo Page 14 7 Utah Department of Environmental Quality, March 8, 2021, Modified Utah Ground Water Discharge Permit No. UGW370004 issued for the Energy Fuels Resources (USA) Inc. White Mesa Uranium Mill.