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HomeMy WebLinkAboutDRC-2015-001767 - 0901a0688050fe61AiZr State of Utah GARY R HERBERT Governor SPENCER J. COX Lieutenant Governor Department of Environmental Quality Amanda Smith Executive Director DIVISION OF RADIATION CONTROL Rusty Lundberg Director DRC-2015-001767 MEMORANDUM TO: THROUGH FROM: DATE: SUBJECT: File C-2015-55 Phil Goble, Section Manager Russell J. Topham March 5, 2015 ft4 ^air ,P.B. /jf Engineering Module 75 A, Review of the 4th Quarter, 2015 (October-December, 2014) DMT Performance Standards Monitoring Report and Cell 4A and Cell 4B BAT Performance Standards Monitoring Report (Report). Groundwater Discharge Permit (GWDP) UG370004 - Energy Fuels Resources, Inc. (EFR) White Mesa Mill, Blanding, Utah This is a summary of Utah Division of Radiation Control (DRC) staff review of the EFR DMT Performance Monitoring Report and Cell 4A and Cell 4B BAT Performance Standards Monitoring Report dated January 27, 2015, and covering the 4th Quarter, 2014 (October-December, 2014) monitoring period (Report). DRC received the Report on January 29, 2015 in both hard copy and soft copy CD formats. Discussions in this document reference the White Mesa Mill Discharge Minimization Technology (DMT) Monitoring Plan, Revision 12.1 (DMT Plan), executed on July 25, 2012. After review of this report, DRC staff findings and recommendations are as follows: Findings 1. Weekly monitoring of Cell 1 solution pool elevations occurred as required. 2. The data presented in the report demonstrate EFR compliance with the solution pool operational requirements of the DMT/BAT plan in force during the quarter. 3. Data provided in Attachment C to the Report supports a conclusion that EFR has generally met the requirement to keep water levels in the Cell 2 slimes drain as low as reasonably achievable. However, the fluid level did show an uptick over the level identified in the lsl and 2nd quarters of 2014. The DRC should watch to see that this apparent trend reversal does not continue. Monitoring results indicate that the feedstock storage areas were dry at the time of weekly inspections. 4. EFR met the requirements for inspection of the liner systems. No damage was detected, and no repairs were undertaken. 195 North 1950 West • Salt Lake City, UT Mailing Address: P.O. Box 144850 • Salt Lake City, UT 84114-4850 Telephone (801) 536-4250 • Fax (801) 533-4097 • T.D.D. (801) 536-4414 www.cfeq.utah.gov Printed on 100% recycled paper Page 2 5. EFR has met the requirements for inspecting the New Decontamination Pad, finding no indication of leakage from secondary containment or other indicators of substandard performance. 6. EFR has met the requirements for inspecting the Old Decontamination Pad, finding no indications of substandard conditions. 7. EFR has met the monitoring requirements for Cell 4A and 4B BAT performance and detected no failures to meet those standards for the quarter. 8. The leak detection systems in Cells 1, 2, and 3 appear to have operated properly, and no fluids were detected therein during the 3rd quarter of 2014. Recommendations 1. The DRC should issue a closeout letter for the review of this report. 2. The DRC should request a revision to the DMT Plan to remove references to Roberts Pond, inasmuch as the pond has been permanently removed from service and will be backfilled with clean soil. 1.0 Tailings Wastewater Pool Elevation Monitoring and Roberts Pond Solution Level Monitoring Part I.E.7(a) ofthe GWDP requires EFR to monitor and record weekly the elevation of the wastewater pool in Tailings Cells 1 and 3 to ensure compliance with Condition 10.3 of the License. Part I.D.3(e) requires EFR to operate Roberts Pond to provide a minimum two feet of freeboard at all times. Part 3.1(d) of the DMT/BAT Plan requires EFR to measure the solution pool elevation in Cells 4A and 4B weekly, and the tailings beach maximum elevation and area within Cells 4A and 4B monthly. Cell 1 Attachment A to the Report contains weekly pool elevations for Cell 1 indicating compliance with the prescribed freeboard requirements. Cell 3 Tailings have nearly completely filled Cell 3. Recognizing this, letters from the Executive Secretary dated January 27, 2011 and March 14, 2011 formally eliminated the need for solution pool elevation measurement in Cell 3. The previously cited January 27, 2011 letter and another letter from the Executive Secretary dated March 15, 2011 concluded a process ending the need for freeboard-related solution pool elevation monitoring in Cell 4A. However, Part 3.1(a) of the DMT/BAT Plan requires monitoring solution pool elevations in Cells 4A and 4B to facilitate determination of compliance with FML leakage rate limitations. As noted above, no requirement for weekly solution pool elevation measurement at Cell 3 existed during the monitoring period. Attachment A to the report reflects no measurements for the reported quarter. Cell 4A Attachment A to the Report contains weekly solution pool elevations for Cell 4A in support of calculating acceptable leak rates for the liner system Page 3 Cell 4B Attachment A to the Report includes solution pool elevation readings for Cell 4B indicating compliance with the prescribed freeboard requirements. Roberts Pond Roberts Pond was dry during the quarter; therefore, no monitoring of water surface elevation was reported. Roberts Pond has been taken out of service following discovery of tears in the pond liner on March 13, 2014. EFRI has redirected all fluid flows previously destined for Roberts Pond to Cell 1. EFRI has completed cleanup of contaminants released from the pond as a result of the breached liner, and is preparing plans to backfill the pond with clean soil. The pond will remain permanently out of service. Findings: The data presented in the report demonstrate EFR compliance with the solution pool operational requirements of the DMT/BA T plan in force during the quarter. Recommendation: EFR should amend the DMT Plan to remove requirements for monitoring of Roberts Pond, inasmuch as the pond is permanently out of service and will be filled with clean backfill. 2.0 Slimes Drain Water Level Monitoring Part I.F.2 of the GWDP requires EFR to include in the Report, all DMT performance standards monitoring detailed in Parts I.D.3 and I.E.7 ofthe GWDP. Part I.D.3(b)(l) of the GWDP requires EFR to maintain the fluid level in the slimes drain of Cells 2 and 3 as low as reasonably achievable at all times, and to demonstrate that performance through adherence to the current DMT Monitoring Plan. Part I.E.7(b) of the GWDP requires monthly monitoring and recording of the depth to wastewater in the slimes drain access pipe as described in Part I.D.3 of the GWDP and the current DMT Monitoring Plan. Part 3.1(b)(v) of the DMT Monitoring Plan requires EFR to monitor and record weekly the depth to wastewater in the Cell 2 slimes drain access pipe to determine maximum and minimum head before and after a pumping cycle, respectively. Section 4.1 of the Report asserts that the above discussed monitoring requirements only pertain to Cell 2 for the reporting period, as dewatering operations have not commenced in Cell 3.1 concur with this assessment. Weekly water level monitoring of the Cell 2 slimes drain is not required as part of the DMT plan, but is required under Part I.D.3(b)(l) of the GWDP. EFR retains records of Cell 2 slimes drain monitoring at the mill. Attachment C to the Report contains data from the quarterly recovery head measurements (discussed in the next paragraph). The recovery head monitoring data provides indirect evidence that EFR has maintained the fluid level in the Cell 2 slimes drain as low as reasonably achievable, as required in GWDP, Part I.D.3(b)(l). From the graph of slimes drain recovery head data in Appendix D, it is apparent that the downward trend that has occurred since May of 2011 did not continue through to September, 2014. However, the downward trend has resumed, as evidenced by monitoring results from the 4lh Quarter. With resumption of the downward trend in fluid level, no action from the DRC is needed. Finding: Data provided in Attachment C to the Report supports a conclusion that EFR has generally met the requirement to keep water levels in the Cell 2 slimes drain as low as reasonably achievable. Page 4 3.0 Feedstock Storage Monitoring This section addresses both bulk conventional feedstock (ore) and alternate feed stored onsite. Ore is stored on the ore pad. Part I.D. 11 of the GWDP anticipates and governs storage of alternate feed outside the confines of the ore pad. Weekly inspection revealed no evidence of ore beyond the boundaries of the ore pad. Storage practices for alternate feeds appeared compliant with GWDP requirements. No standing water was noted in feedstock storage areas during the quarter. Finding: Monitoring of the feedstock storage area occurred as required. The data support a conclusion that no feedstock existed outside the designated feedstock storage areas. 4.0 Tailings Cells and Pond Liner System Repairs Inspection of all cells occurred weekly during the period covered in the report. The report indicated no case of liner damage in the tailings cells discovered or repaired during the quarter. Finding. EFR met the requirements for inspection of the liner. 5.0 Decontamination Pads Weekly inspection of the New Decontamination Pad occurred as required under Part 1.F.12 of the GWDP. The monitoring portals were dry during all inspections, indicating no leakage from primary containment. Finding: EFR has met the routine and annual requirements for inspecting both the Old and New Decontamination Pads, finding no indication of leakage from secondary containment. 6.0 Cells 4A and 4B BAT Performance Standards Monitoring Requirements for measuring BAT performance for Cells 4A and 4B include verifying that leak detection system equipment operates appropriately, verifying that fluid head in the leak detection system sumps does not exceed 1 foot above the lowest point in the secondary (lower) flexible membrane liner, and recording the volume of fluid pumped from the leak detection systems for the two cells. EFR must also record the fluid head in Cell 4B for compliance purposes, and in Cell 4A for computation of acceptable leakage rate in Cell 4A. The data provided in the report and its attachments provide evidence of compliance with the Cells 4A and 4B BAT performance monitoring standards in place during the monitoring period. Finding: EFR has met the monitoring requirements for Cell 4A and 4B BAT performance and detected no failures to meet those standards for the quarter. 7.0 Cells 1,2 and 3 Leak Detection System Monitoring Leak detection system monitoring requirements for Cells 1, 2 and 3 appear in the Radioactive Materials License rather than the GWDP. For consistency, the DRC requested that this monitoring be included as part of the quarterly report and EFR has consented to do so. The report and its attachments contain weekly monitoring data for the operational status of the leak detection system equipment, fluid levels detected in the leak detection systems, and volumes of fluid pumped. From the data, EFR represents that no failures of the monitoring equipment occurred that were Page 5 not corrected within 24 hours. Leak detection systems for the three cells measured dry; therefore, no fluids were pumped therefrom. Finding: The leak detection systems in Cells 1, 2 and 3 appear to have operated properly, and no fluids were detected therein during the 3rd quarter of 2014.