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GENERAL32022
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Last modified
8/24/2016 7:54:49 PM
Creation date
11/23/2007 7:09:53 AM
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Template:
DRMS Permit Index
Permit No
M1983194
IBM Index Class Name
General Documents
Doc Name
COVER SHEET-2 PUBLIC COMMENTS ON DRAFT EIS & RESPONSES TO COMMENTS
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D
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2. RESPONSES TO PUBLIC COMMENTS <br />that the company keep all brines or increased levels of saline <br />minerals contained within [he boundaries of the lease and <br />that remedial action be taken i( monitoring wells detect <br />increases in dissolved solids migrating from the production <br />well field. For further details and clarification of monitoring <br />requirements, see monitoring summary in the TEXT <br />CHANGES section (Water Resources, Environmental <br />Consequences). In addition, please refer to Appendix C. <br />Response No. 18. Dedicated hydrologic monitoring <br />wells are those wells located outside of [he production weB <br />field and outside of the zone of influences of subsidence <br />for the purpose of gathering baseline values both up and <br />down gradient of the field. These may either be newly <br />completed we!!s, existing in-place wells, or a combination <br />of both. [o addition, if monitoring in the weB field indicates <br />increased dissolved solid concentrations, the dedicated <br />monitoring wells would be used to pick up or tract any <br />potential plume migrating from the fields. Therefore, BLM <br />feels that it is necessary to maintain a reliable monitoring <br />system surrounding the well field. <br />Response No. 29. The "General Development Compo- <br />vents" section in [he draft describes the project only as <br />proposed by WRC in their mine plan and only to the level <br />of detail contained in the mine plan. <br />BLM is in complete agreement with EPA's proposal and <br />will support same when the detailed monitoring plan is <br />submitted. <br />Response No. 30. In addition to monitoring the lowest <br />part of the lower aquifer, BLM believes that monitoring <br />of the B-Groove is essential in detecting any leaks that may <br />occur in well strings above the base of the lower aquifer. <br />Monitoring of the B-Groove would also provide a backup <br />system to the lower sampling interval and would aid in <br />detecting any potential increase in dissolved solid movement <br />and gradient Flow changes from the dissolution surface <br />upward into the lower aquifer. <br />Oil Shale <br />Response No. 31. The best interest of the United States <br />Government is the conscientious preservation, development, <br />and use of its resources, as appropriate. The multintineral <br />resource should be developed in such a manner that the <br />highest recovery of all resources will be attained. One <br />resource should not be foregone for the other. The Boles <br />Bed would not be recoverable by conventional mining <br />methods and no impacts to the oil shale resources are <br />predicted; therefore, the recovery of this nahcolite by solution <br />mining is a plus in the overall recovery of minerals in the <br />Piceance Basin. <br />Response No. 31. Modified In Situ (MIS) methods are <br />not conducive to heavily fractured ground as exists in the <br />sodium lease tract area. M[S retorts are subjected to high <br />negative pressure. Leakage of air from one retort to another, <br />or from mine air to the retort, can be very detrimental <br />to the process as well as create safety hazards. MIS has <br />not been sufficiently demonstrated in the basin to announce <br />it as a viable mining method in the basin. <br />Response No. 33. As stated in the referenced paragraph, <br />the poor rock quality has rendered the recovery of minerals <br />from the R-6 Zone within the sodium lease area unfeasible <br />by existing recovery methods, and the Mahogany Zone will <br />not be affected by the proposed nahcolite recovery of the <br />Boles Bed. Although the quantity figures for oil shale and <br />sodium resources are not in a table format, they are in <br />the narrative section you refer to. <br />Response No. 34, No change. The total thickness of <br />the identified minable zone is as much as 60 feet, of which <br />at least a 40-foot thickness would be extractable. The mining <br />of this zone would, by definitiam, include the dewatering <br />zone needed to mine this interval. <br />OB Shale/NahcoGte <br />Response No. 35. Because of the proximity of the Boles <br />Bed to the dissolution surface, that bed could not be recovered <br />by methods other than solution mining. A lowering of the <br />dissolution surface would take place over a very long period <br />of time and would not render the underlying oil shale beds <br />less minable. The distance from [he dissolution surface down <br />to the minable oil shale is sufficient so that necessary crown <br />pillars can be left without loss of resource. <br />Oil Shale/Wafer Resources <br />Response No. 36. The premise of the environmental <br />impact statement is the conservation of resources, both <br />mineral and environmental. The solution mining of the <br />nahcolite 8oies Bed presents virtually no risk to the detriment <br />of the future minability of the oil shale. The minable oil <br />shale would remain virtually intact, as it is today, and any <br />additional commingling of the aquifers, than exists today, <br />would not be inherent. The monitoring and mitigation <br />developed in this document will accomplish this goal. <br />Reclamation <br />Response No. 37. Considering [he potential limitations <br />on reclamation success (page 3-17 of the draft) and prescribed <br />reclamation goals (page 4-15 of the draft), monitoring <br />revegetation attempts over one growing season is not <br />considered adequate. Since reclamation bond release criteria <br />are predicated on relative production and crown cover of <br />perennial species, including seeded shrubs, it is highly <br />unlikely that the operator would be able to successfully <br />satisfy the performance criteria within 1 year. A minimum <br />2-46 <br />
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