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REP07588
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REP07588
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Last modified
8/24/2016 11:37:44 PM
Creation date
11/26/2007 11:40:03 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1982056
IBM Index Class Name
Report
Doc Date
2/2/2001
Doc Name
2000 ANNUAL HYDROLOGY REPORT
Annual Report Year
2000
Permit Index Doc Type
Hydrology Report
Media Type
D
Archive
No
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/ ~~ <br />97012TC and 97013TC, also required water quality sampling on asemi-annual basis. All monitoring <br />requirements were completed at these sites during 2000. However, well FCM#2 was replaced in_the fall of 1995 <br />by monitoring well 95M001, with semi-annual monitoring during 2000 occurring at well 95M001 in lieu of FCM o'ie <br />#2. Tables 14 through 20 provide summaries of the 2000 Water Year data collected at each site. Table 14a <br />provides the period of record statistical summary of collected data at well 001-83-106 with Tables 17a through <br />20a providing the period of record statistical summaries of collected data at wells 95M001, FBR-2-E, 97012TC <br />and 97013TC. Figures 29 through 39 provide graphical representations of water levels and selected water quality <br />parameters recorded at each site. <br />The continuous pumping of well 001-83-106 (Figure 29) complicates [he po[entiometric surface in the Trout <br />Creek Sandstone. The po[entiometric surface trends prevalent in the Twentymile Sandstone and Wadge <br />Overburden aquifers are not evident in [he monitored Trout Creek wells. The previously monitored well 006-83- <br />48C routinely exhibited water levels in the 7100 ft elevation range while replacement well FCM#2 returned <br />levels around elevation 6520 during 1995. In the fall of 1995, well 95M001 was established in part to address the <br />apparent discrepancy in water levels between wells 006-83-48C and FCM#2. Water levels remmed from well <br />95M001 confirm that levels recorded from well FCM #2 were accurate (Figure 31). Inflows from the Trout <br />Creek Sandstone into the mine workings have not been encountered to date to account for the apparent lowering <br />of the potentiometric surface in the Trout Creek formation as indicated by the water level data previously <br />recorded for well 006-83-48C. Some dewatering of the aquifer does occur from [he pumping of well 001-83-106 <br />to supply [he mine with domestic water. During 2000, the southernmost Trout Creek well, 001-83-107 (Figure <br />30), continued to exht tte ower water levels in the 6840 fi elevation range, while the northernmost well, 008- <br />75-EFC (Figure 32), remained around the 6620 fi elevation level. Well FBR-2-E (Figure 34) continued to <br />returned levels around 6670 fr elevation during 2000, which is appreciably lower than the 6720 ft level typical <br />prior to the 1999 Water Year. Well 001-83-107 (Figure 30) continued to show lower water levels than those <br />typical prior [0 1992. Well 001-83-106 (Figure 29) remains drawn down presumably due to consistent pumping. <br />Well 95M00] (Figure 31) returned levels around 6460 ft elevation during 2000, which is appreciably lower than <br />[he historical level of 6510 ft. Well 97012TC (Figure 36) continued the steady decline apparent since monitoring <br />began in [he 1998 Water year. Well 97013TC (Figure 38) continued [o show the minor fluctuations apparent <br />since monitoring began in the 1998 Water year. <br />Field measurements are presented in Tables 15 and 16 for wells 001-83-107 and 00875-EFC. Field parameter <br />measurements on these Trout Creek Sandstone welts monitored during 2000 returned values within anticipated <br />ranges with no mine related impacts evident. Field measurements and water quality parameters for wells 001-83- <br />106, 95M001, FBR-2-E, 97012TC, and 97013TC are provided on Table 14, and Tables 17 through 20. At well <br />001-83-106 (Table 14) new maximum values were recorded far lab conductivity, sulfate, dissolved selenium, <br />nitrite, and ortho-diss phosphate. The historically elevated pH readings for this sight seem [o have moderated <br />slightly. At well 95M001 (Table 17) new minimum values were recorded for dissolved magnesium and <br />dissolved iron. New maximum values were recorded for field pH, carbonate, and nitrite. The 2000 pH readings <br />continue to be relatively high at this site. At well FBR-2-E (Table 18) new minimum values were recorded for <br />• field pH and dissolved iron, New maximum values were recorded for dissolved selenium and nitrite. High pH <br />readings appear typical for this well also. Well 970] 2TC (Table 19) and 97013TC (Table 20) established many <br />new maximum and minimum values for tested parameters in 2000, due to the limited period for which values <br />4 <br />
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