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volume of ground water entering the mine, both during and after mining, that could <br />potentially migrate laterally and create a new seep(s) within Lumsden Canyon. <br />20) Following construction of the first bulkhead the applicant must commit to monitoring <br />the water elevation in the decline until it reaches equilibrium. Construction of the <br />proposed second (higher) bulkhead may not proceed until equilibrium is reached and <br />shown to be below the elevation of the middle Brushy Basin aquifer. <br />a) The Applicant must commit to a contingency plan and bond for installation of <br />a water impounding bulkhead at the upper bulkhead location. If the water <br />level in the flooded decline equilibrates below the upper bulkhead elevation, <br />then installation of a concrete block wall as proposed in the application will <br />be acceptable. <br />b) The Applicant must commit to a contingency plan and bond for bulk heading <br />of the Pack Rat Mine. <br />c) A point of compliance for ground water quality must be established in the <br />lower aquifer of the Brushy Basin Member. This will involve the installation <br />of a monitoring well down gradient of the proposed bulkhead, between the <br />bulkhead and the canyon wall. Since the mine will not flood until the <br />bulkhead is installed at the time of mine closure, the collection of baseline <br />data from the point of compliance well can proceed concurrently with mining. <br />d) Cost estimates for the design, construction and monitoring of the bulk head <br />appear to be insufficient. Division experience indicates costs in the <br />magnitude of 40 to SO times the $7, 000.00 figure given. Enclosed is the <br />Division's estimate for the cost to construct one required and two contingency <br />bulkheads. Please clarify. <br />a. Water Monitoring and Elimination of Upper Bulkhead at Whirlwind Decline <br />Energy Fuels commits to monitoring the water elevation above the lower seal until it <br />reaches equilibrium. This will be done by manual measurement since the upper seal <br />will not be installed. The seal will be approximately 380 feet downdip (at a 6% grade) <br />of the ground water inflow into the decline. As discussed in Dick White's memo in <br />Attachment A, after sealing the water levels could potentially increase by a maximum <br />of approximately 15 vertical feet above the current inflow point. This is equivalent to <br />an additional 250 feet of flooded drift or about 630 feet of total drift that is partially <br />or totally under water. Given that the drift has nominal dimensions of 9 feet by 12 <br />feet and assuming the current inflow rate of 1.5 gpm will continue over time, the <br />expected time for the pool to form and equilibrate is about six to nine months. <br />The pool is not expected to migrate because it will be contained within low- <br />permeable Brushy Basin mudstones and shales. A schedule for taking water level <br />measurements and water quality samples will be proposed to DBMS and the BLM <br />prior to sealing based on the inflow rates measured at that time. Once the pool reaches <br />equilibrium, the portal will be backfilled and reclamation of the site can be <br />completed. <br />L::net•~~ 1:uels (~e5c~tu-ces C'<>rp{:~rat~c~n 44 t!t7ic~t~ t3~~~tli;t-ard, quite CiOt~ 17 <br />Lal:e~~~~:~~d, C;d;3 f~(}12~ t'hc~tz~; :303-t)7~-2~1~{} <br />