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2008-01-08_REPORT - C1980007
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2008-01-08_REPORT - C1980007
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Last modified
8/24/2016 3:20:45 PM
Creation date
1/8/2008 2:45:46 PM
Metadata
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Template:
DRMS Permit Index
Permit No
C1980007
IBM Index Class Name
REPORT
Doc Date
1/8/2008
Doc Name
2006 Annual Hydrology Report
From
HydroGeo Inc
To
DRMS
Annual Report Year
2006
Permit Index Doc Type
Hydrology Report
Media Type
D
Archive
No
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West Elk Mine 2006 Annual Hydrology Report 42 <br />5.2.1 Impacts to Water Quantity and Quality <br />Spring and seep flows in WY 2006 continued to be below normal compared to historical averages, <br />and in many cases below the flows measured in WY2005 (HydroGeo, 2006). Springs that were <br />flowing in WY 2005 but not in WY 2006 include Spring 11-2, Spring 15-1, and Spring G-26A. <br />These springs apparently have been affected by the drier climatic conditions occurring in WY <br />2006. Spring E14-1 located at the head of Box Canyon was permanently covered by the <br />construction of a new drill pad in the summer of 2006. This spring had been dry since 1998. Other <br />than Spring 14-1, there is no indication that of any changes to spring or seep flows were the result <br />of mining activities. <br />Water quality data from WY 2006 did not indicate significant changes from baseline conditions for <br />most of the monitored springs. However the following springs had slightly elevated TDS and\or <br />conductivity values that were also noted in WY2004 and WY2005. Spring 27-1 had a slightly <br />elevated conductivity of 624 µmhos/cm compared to the maximum baseline value of 437 <br />µmhos/cm and TDS of 450 mg/1 compared to the maximum baseline value of 300 mg/1. Spring G- <br />7 had a slightly elevated conductivity of 475 µmhos/cm compared to the maximum baseline value <br />of 414 µmhos/cm and TDS of 280 mg/1 compared to the maximum baseline value of 230 mg/1. <br />!~ Spring G-24 had a slightly elevated conductivity of 902 µmhos/cm compared to the maximum <br />baseline value of 564 µmhos/cm. Spring G-14 had a slightly elevated conductivity of 1,060 <br />µmhos/cm compared to the maximum baseline value of 682 µmhos/cm. Spring G-22 had a slightly <br />elevated conductivity of 1,270 µmhos/cm compared to the maximum baseline value of 640 <br />µmhos/cm and TDS of 790 mg/1 compared to the maximum baseline value of 516 mg11. Spring G- <br />31 had a slightly elevated conductivity of 981 µmhos/cm compared to the maximum baseline value <br />of 975 µmhos/cm and TDS of 620 mg/1 compared to the maximum baseline value of 505 mg/1. <br />Spring G-25 had a slightly elevated conductivity of 1,680 µmhos/cm compared to the maximum <br />baseline value of 1,320 µmhos/cm. Spring G-35 had a slightly elevated conductivity of 1,220 <br />µmhos/cm compared to the maximum baseline value of 1,130 µmhos/cm. Spring G-27 had a <br />slightly elevated conductivity of 1,950 µmhos/cm compared to the maximum baseline value of <br />1,800 µmhos/cm. Spring J-4 had a slightly elevated conductivity of 470 µmhos/cm compared to <br />the maximum baseline value of 429 µmhos/cm and TDS of 310 mg/1 compared to the maximum <br />baseline value of 300 mg/1. These increased concentrations are most likely due to low flow rates <br />during the sampling period in 2004, 2005 and 2006 and are not believed to be related to mining <br />operations. MCC will monitor the water quality of these springs to see if any water quality trends <br />occur. No mining-induced impacts to water quality or flows in the monitored springs are <br />anticipated in WY 2007. <br />December 2007 HydroGeo, Inc. <br />
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