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3.21 Points of Compliance <br />Rule 4.05.13(1)(b) requires formal establishment of ground water points of compliance for coal operation which <br />has the potential for negatively impacting the quality of ground water for which quality standards have been <br />established by the Colorado Water Quality Control Commission. The Commision's Rule 41 sets forth Basic <br />Standards for ground Water. These Standards are applicable to ground water at the Foidel Creek Mine. In the <br />judgment of DRMS, these Standards are applicable to ground water at the Foidel Creek Mine, however it is also <br />the judgment of DRMS, the Foidel Creek Mine does not have the potential to negatively impact bedrock aquifers <br />due to the nature of the geology (i.e. synclinal basin) found at the mine's location. <br />Wells 008-AV-2 (Foidel Creek alluvium), 008-AU-3 (Fish Creek alluvium), and well 008-AT-1 (Trout Creek <br />alluvium) will be established to satisfy alluvial ground water points of compliance. <br />3.3 Surface Water Monitoring <br />Monitorino/Samplin2 Requirements: Table 32 presents a summary of surface water monitoring frequencies, <br />which was last updated for Permit Revision 6 (PR 03-06 Exhibits 14-7 through 14-10) in March of 2004. Site <br />locations are shown on Figure 2 (a.k.a. Map 13A), Hydrologic Monitoring Plan of TR03-42 (as well as in Figure <br />2 of this AHR). Table A of Exhibit 14 specifies three seasonal monitoring episodes (i.e. October to February, <br />March to May, and June to September), each of which are further divided into two general categories of sampling <br />frequency: 1) "Regular" monitoring that is done continuously, and 2) "Contingent" monitoring that is conducted <br />only when there is a discharge from underground mine pumping at surface discharge sites 109 and/or 115. Note <br />that discharge from site 109 has not occurred in several years, and is not anticipated to occur in the future. <br />2010 surface water data is provided in Tables 33 through 49. Water quality parameters for these sites were <br />typically within previously established ranges, unless otherwise discussed below. An historical summary of data <br />has been provided in Tables 35a through 51a. <br />Stream Gaging <br />Accurately monitoring flow at stream sites can be difficult due to continual damage of gage stations by cows, <br />horses, and weather effects. 2010 was no different. Many stations require repair on a regular basis. In addition, <br />erosion of stream channel banks impact flow calculations. In the summer of 2007, TCC hired consultants (Rivers <br />Unlimited, Inc. of Steamboat Springs, and Norwest Applied Hydrology of Denver) to assist with re-evaluating <br />key stream bed locations, including rating curves for ongoing stream gauging. This on-going study continued <br />into the spring summer and fall of 2010. A discussion of all the gage study results (including the 2011 year) will <br />be consolidated into a report and attached as an appendix in the 2011 AHR. In 2008 and 2010 the consultants <br />assisted with the temporary repair of some gage stations. In 2010, four protective enclosures were constructed at <br />historic flow meter recorder locations. New recorders will be installed and activated at these locations in the <br />10