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GENERAL40389
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Last modified
8/24/2016 7:59:35 PM
Creation date
11/23/2007 10:38:04 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981071
IBM Index Class Name
General Documents
Doc Date
3/30/1998
Doc Name
PROPOSED DECISION & FINDINGS OF COMPLIANCE FOR SL6
From
Phase II/III -Energy Mine No. 2 ā(Energy Mine No. 1 & Eckman Park)ā
Permit Index Doc Type
Findings
Media Type
D
Archive
No
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<br /> <br />11 <br />Post-m in ing/Post-reclamation: <br />Upstream: Site 16 4/96-9/96 xflow=33.6 cfs 1996 xTDS=426 mg/L <br />1996 pH range: 7.8-8.5 <br />Qualitya 996 x Ca= 69 mg/L <br />1996 x Fe=2514 ug/L <br />Downstream Site 1002 4/96-9/96 xflow= 3 <br />1996 pH range: 7.9-8.5 <br />Quality:l996 >< Ca=74 mg/L <br />1996 R Fe=5096 ug/L <br />1996 z Mg=41 mg/L 1996 z Na=22 mg/L <br />1996 x Mn=93.4 ug/L <br />i.0 cfs 1996 >< TDS=514 mg/L <br />1996 x Mg=47 mg/L 1996 x Na=164 mg/L <br />1996 x Mn=138 ug/L <br />Additional inputs into Fish Creek between Sites 16 and ]002 include mine dewatering (NPDES <br />permit No. CO-0042161, discharge no. OOIA) from the underground Foidel Creek Mine (C-82-056) <br />which underlies the Mine No. 2 azea, and Mine No. 2 spoil springs. Mine water discharge from the <br />Fish Creek Borehole ceased during the first quarter of 1996. Elevated iron levels at Site 1002 in 1996 <br />were recorded in the early portion of the second quarter. The TDS concentration measured during the <br />first quarter 1996 from the Fish Creek Borehole mine water discharge was 3295 mg/L, the mean <br />calcium concentration was 113 mg/Iā and the magnesium concentration was 39.8 mg/L. No measure <br />of sodium was recorded. Iron concentration in the Fish Creek Borehole discharge averaged 1,784 <br />ug/L with Mn averaging 318 ug/L. A distinct decline in iron level at site 1002 was recorded for the <br />remainder of 1996. <br />The Mine No. 2 spoil springs consist of T (6862000), Q (6861700), R, M2-87, M293-1, M293-2, and <br />two un-numbered spoil springs that report to permanent pond M. Spoil spring T is located at the <br />north end of the western block, and drains approximately 375 feet to Fish Creek. Spoil springs Q, R, <br />M2-87, M293-1 and M293-2 are located at the northeastern portion of the East Block, and drain to an <br />un-named drainage before flowing approximately 3250 feet north to Fish Creek. Colorado Yampa <br />Coal Company's sampling plan requires spoil spring water quality analysis when spoil spring flow <br />exceeds 35 gpm during the Spring and Seep survey conducted in May of each year. Spoil spring Q, <br />which discharges at the northern toe of the East Block slope was sampled for water quality. The <br />following values were measured from Spoil spring Q in May 1996: Flow= 24.4 gpm, TDS=1330 <br />mg/L, Ca=295 mg/L, Mg=99.5 mg/L, Na=23.4 mg/L, Fe=470 ug/L, and Mn=164 ug/L. <br />Review of the summarized data in Table 1 show upstream and downstream TDS levels in Fish Creek <br />have remained relatively consistent between pre-mining and post-reclamation condition. <br />Downstream flow has more than doubled from pre-mining to post-reclamation for the two years <br />compazed. Partial explanation for this increase in downstream flow in 1996 would be due to mine <br />water discharge at the Fish Creek Borehole location from the underground Foidel Creek Mine. <br />Upstream Site 16 demonstrates a marked increase in iron concentration from the 1979 data to [he <br />1996 data. Salinity components on calcium, magnesium and sodium have generally increased <br />slightly both upstream and downstream of Mine No. 2 in the post reclamation condition. SAR values <br />calculated from Ca, Mg, and Na concentrations remain low and not prohibitive to agricultural use. <br />
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