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2012-06-28_REPORT - C1982057
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2012-06-28_REPORT - C1982057
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Last modified
8/24/2016 5:02:03 PM
Creation date
7/3/2012 2:38:14 PM
Metadata
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Template:
DRMS Permit Index
Permit No
C1982057
IBM Index Class Name
Report
Doc Date
6/28/2012
Doc Name
2011 Annual Hydrology Report Part 1 through Appendix B
From
Peabody Energy
To
DRMS
Annual Report Year
2011
Permit Index Doc Type
Hydrology Report
Email Name
SLB
SB1
Media Type
D
Archive
No
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Dry Creek March -April 3.04 mg /l <br />" May - February 1.11 mg /l <br />Lower Sage Creek year round 1.00 mg /1 <br />Upper Sage Creek year round 1.25 mg /l <br />The break between Upper and Lower Sage Creek is the west border of <br />Section 18, T5N, R87W. SCC's outfalls for the Seneca II -W Mine discharge <br />into Lower Sage Creek. SCC's outfalls for the Yoast Mine discharge into <br />Upper Sage Creek. The exceedances for TR iron noted at the NPDES sites <br />in May in this AHR would be above the new approved standards. This is <br />due to the fact that the snowmelt season extended into May this year due <br />to near record snowpack. <br />Four samples from NPDESI7 exceeded the aquatic life chronic selenium <br />standard, 4.6 ug /1, with values of 10, 7. 6, 8 and 6 ug /l. The acute <br />standard, 18.4 ug /l, was not exceeded. One sample from NPDES6 exceeded <br />the chronic selenium standard with a value of 4.8 ug /l. See the <br />following NPDES Effluent section for a discussion of these excursions. <br />The sulfide data presented in Appendix E are the total of both the <br />ionized (S -) and un- ionized (HzS) forms of hydrogen sulfide. The un- <br />ionized form is the potentially toxic form, and is what the CDPHE water <br />quality standard is based upon. A procedure for calculating the un- <br />ionized form may be found on the website: <br />http: / /www.mullalyengineering .com.au /imaqes /product /file /Problem of Hvdr <br />o en Sulphide in Sewers. df page 5, Table 1. No excursions of the 0.002 <br />mg /l un- ionized sulfide standard occurred this year. <br />The aquatic life ammonia standard is dependent on pH and temperature. <br />The detection limit for ammonia is 0.05 mg /l. All values above detection <br />limit are compared to table standards found on this website, page 87: <br />http: / /www.epa.gov /waterscience /criteria /ammonia /99update.pdf <br />No ammonia excursions occurred this year. <br />One mercury value this year was above the detection limit, 0.2 ug /l. <br />Sage Creek stream site WSSF3 had a value of 1.6 ug /l in April. This <br />21 <br />
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