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(D) Monitoring for additional water quality constituents may be required b <br /> y the Division based upon site - specific conditions, approved postmining land use, or for good cause shown. <br /> III HYDROLOGIC MONITORING PROGRAM <br /> TCC will conduct a program of surface and ground water monitoring in the Foidel Creek Mine Permit and <br /> adjacent areas. A detailed discussion of monitoring procedures and the schedule for monitoring activities is <br /> presented as Exhibit 14, Hydrologic Monitoring Plan. Monitoring activities will continue on a regular basis <br /> until the effects of mining - related activities have been determined to have stabilized and are within acceptable <br /> limits, as determined from water quality criteria, and until approved to be reduced or terminated by the CDMG. <br /> The monitoring program conforms with all applicable State and Federal laws and will provide a continuing <br /> means of detecting and measuring any changes in the area hydrologic environment. Hydrologic monitoring <br /> activities will address the quality and quantity of both surface and ground water systems. Hydrologic <br /> monitoring sites will be accessed from dedicated lught -use roads or pre- existing County or ranch roads. <br /> Ground Water Monitoring <br /> Ground water monitoring in the permit and adjacent areas will involve measurement of ground water levels on <br /> both a semi - annual and quarterly basis and collection of ground water physical data and the sampling and <br /> analysis of ground water chemical constituents on both a semi - annual and quarterly basis. Ground water <br /> monitoring activities will encompass bedrock ground water and shallow alluvial ground water. The monitoring <br /> well locations are shown on the Hydrologic Monitoring Plan Map (Map 13A). <br /> Semi - annual ground water sampling of bedrock wells and quarterly sampling of alluvial wells will involve <br /> measurement of ground water temperature, pH, and electrical conductivity, and collection of the necessary <br /> samples for chemical analysis. Standard EPA calibration and measurement methods will be used for all ground <br /> 411, water measurements in the field. Acceptable techniques will be used to ensure the collection of representative <br /> ground water samples from wells. Water samples will be analyzed by a qualified laboratory using standard <br /> ASTM or EPA approved test procedures. Ground water analysis will involve measurement of the selected <br /> parameters and chemical constituents listed in Exhibit 14, Hydrologic Monitoring Plan. <br /> A 1995 water monitoring well was drilled to replace FCM #2, which has failed. The well, 95M005, will monitor <br /> the Trout Creek sandstone. After completion of the well, the site was reclaimed, the topsoil replaced, and the <br /> site reseeded with the appropriate seed mixture. <br /> Surface Water Monitoring <br /> Surface water monitoring will address the quality and quantity of area streamflows. Collection of the necessary <br /> monitoring information will involve the following activities: <br /> Sampling and collection of flow and field parameters; 12 per year during the period of March through <br /> September. Collection of 4 samples per year for full -suite analysis. Typically, flow measurements will extend <br /> from March into September. This period corresponds with the beginning of the major runoff period and <br /> continues into the low -flow period. The measurement frequency is given in Exhibit 14, Hydrologic Monitoring <br /> Plan. <br /> Continuous measurements of streamflow and water stage data for Foidel and Middle Creeks will be available <br /> from surface water gauging stations maintained by USGS -WRD. Stream sampling activities during periods of <br /> active flow will involve measurement of stream temperature, pH, specific conductance, and collection of the <br /> necessary samples for chemical analysis. <br /> • It is anticipated that water percolating through the upgradient spoil, together with a small amount of runoff from <br /> the adjacent area, will enter into the Area 2 Pit and the combined amount will be sufficient to cause overflow <br /> from the pit to Pond D. In order to measure the overflow, a cutthroat flume has been installed in the channel <br /> which connects the pit and Pond D. The point between the pit and Pond D has been designated as Site 7 and is <br /> PR09 -08 2.05 -168 04/29/09 <br />