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HYDRO29057
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HYDRO29057
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Last modified
8/24/2016 8:48:06 PM
Creation date
11/20/2007 10:17:37 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1988112
IBM Index Class Name
Hydrology
Doc Name
TABLE OF CONTENTS
Media Type
D
Archive
No
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Appendix D, Comment Letters and Public Meeting: BMRI Comments (Cont.): Page 5 <br />/3. Paragraph (e) of that same subsection describes the x~astex~ater sources. At the time of the permit application, there <br />were three actual or potential sources including the backfill, t/re curtain wells and the seep water. At this lime, the <br />contributing sources are the backfill x~el/s and the curtain x~el/s. At some paint, the downgradient containment wells <br />rngy be included in the sources. <br />Response: This updated infornration has been indicated in the rationale. <br />14. /V. B.4 -Discussion of Effluent Lirnitatiorrs, paragraph (e), Cyanide, Mercury and Silver <br />As noted in our cornrnents on the permit document, BMRI does not believe there is any evidence of documentation to <br />srtppon the development ojeither effluent limitations or monitoring and reponing requirements for cyanide, mercury or <br />silver. We request that the drree parameters be eliminated from the eJjluent lirnitanons lists and that the requirements <br />for monitoring and reporting 6e eliminated. /n the alternative, we request drat explicit language be included jar all <br />three parameters drat allows the limitations and rnorritoring and reponing requirements to be eliminated after a period <br />oJ6 months upon a demonstration of non-detects as defined by applicable analytical techniques during that period. <br />We reiterate that the cyanide process was never used in the backfill area, no materials that were in contact with n~anide <br />were returned to the backfill pit. /n fact, t/re facility was sired to eliminate the potential for cyanide to come in contact <br />with any waters of the state. Moreover, cyanide has never been confirmed in groundwater or surface water monitoring <br />at any of the Rito Seco or groundwater monitoring stations in the vicinity of the West Pit. <br />Response: Rejer to the previarts response discussion under comment 1. a. on page 1 oJAppendix D. <br />/5. !n the same section describing the /WCfor theJlox• rates, the distribution of wastewater versus receiving stream is <br />incorrect and should be 88% rather than 78%. <br />Response: 7Tre TWC value was changed. <br />/6. Paragraph 6, Economic Reasonableness Ei•aluation <br />There is a typographical error in the sentence that reads, in pan "that this is a new permit xhich was not in exist at the <br />time. " replace exist xith existence. <br />Response: This item was corrected. <br />/n a letter dated Julv /9, 2000, BMR! submitted a repon for a Whole Effluent Tonicity (WET) test for dre San Luis facility. This <br />test was conducted in April 2000jor both species, which resulted in passing tests for lethality and growth. BMRT requested that <br />WET testing be eliminated from the final permit. Since some toricity did occur, the Division determined that WET testing is still <br />required jar the penrrit. <br />8. USEPA Region V//I Comment Letter of May 5, 1000: The jol[oxing responses to cornrnents by the U. S. EPA are indexed <br />to the EPA comment letter by the roman numeral as indicated on this letter. <br />Comment: <br />I. Water Ouality Data in the Antidepradation Array: "It appears that the baseline water quality data used in the anti- <br />degradation review for developing effluent (irritations jar Outfall 001 was jrom station RS-5...... EPA believes a mare <br />appropriate baseline water quality condition would be derived from station RS-/, which is approzirnately 2 miles upstream of the <br />Battle Mountain mining activity. ..... ' <br />Response.• <br />Figure 5, which has now been added to dre permit, is a geologic map of the area encompassing the West Pit facilities at the San <br />Luis Project. The map was reproducedfrorn a Colorado School ojMines Ph.D. dissenadon that was completed in /9976y <br />Roben Benson in the Depanrnent aJGeo(ogy. The geologic map serves as the primary basis for the observation that historical <br />water quality data measured at the upgradient surface water monitoring station RS-1 would not reasonably reJiect the naturally <br />occurring hydrologic and geologic processes that ultimately result in ambient water quality conditions in the reach of the Rito <br />Seca that could be influenced by the discharge of waters associated with rater treatment activities in the West Pit. <br />As shox•n in this figure, the primary geologic formation in the vicinity ojthe RS-! location is the Precambrian bedrock. As a <br />result, the geornorplrologic character of the Rito Seco at the surface water station RS-1 is best described as a bedrock controlled <br />reach xith only a thin veneer of unconsolidated alluvial material overlying [he Precambrian bedrock channel. <br />/n addition, the valley sidewa!!s are steep resulting in a more V-shaped valley that is characteristic of river channels that have <br />jarred in weathering resistant, competent bedrock. <br />In contrast to [he geologic and geornorplrologic conditions present at surface water station RS-l, the region of the Rito Seco in <br />the vicinity of the West Pit is in a completely differeru geomorphologic regimen that is more characteristic of alluvial channels. <br />
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