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2016-12-01_PERMIT FILE - C1980007A
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2016-12-01_PERMIT FILE - C1980007A
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Last modified
2/1/2017 10:43:12 AM
Creation date
2/1/2017 10:22:48 AM
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Template:
DRMS Permit Index
Permit No
C1980007A
IBM Index Class Name
Permit File
Doc Date
12/1/2016
Doc Name
delete
Section_Exhibit Name
Exhibit 71
Media Type
D
Archive
Yes
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HYDROLOGIC CHARACTERIZATION AND MONITORING PLAN 12 <br />4.0 COMPREHENSIVE HYDROLOGIC MONITORING PLAN <br />The MCC hydrologic monitoring program is designed to collect the monitoring data needed to <br />assess mining -related impacts on hydrologic resources. CDRMS approved a revised hydrologic <br />monitoring plan for MCC in October 2016 (CDRMS, 2016). A description of the revised <br />monitoring plan, effective WY 2017, is presented in the following sections. The hydrologic <br />monitoring plan for the permit area includes monitoring surface water resources, springs and <br />seeps, groundwater resources, the coal refuse pile underdrains, and pertinent mine water sites. <br />Routine monitoring, i.e. monitoring done subsequent to the baseline monitoring period, includes <br />collecting field water quality data (pH, electrical conductivity [EC], and temperature) and <br />collecting a sample for independent laboratory analysis annually. Flow or water level <br />measurements are collected three times per year corresponding with the rising limb period, <br />between April 3rd and May 13th; the peak flow period, between April 21" and June 26th; and the <br />low flow period, between July 10th and October 8th, as shown on Table 5. <br />The hydrologic monitoring plan for MCC incorporates a separate baseline monitoring schedule <br />for potential new monitoring sites for approximately one year prior to the time when mine <br />development operations expand into new possibly affected areas. The baseline monitoring <br />schedule protocols specify collecting monthly field water quality data, flow or water level <br />measurements, and collecting samples for laboratory analysis for the year prior to initiation of <br />mining and potential impacts (Table 5). Site-specific baseline schedules are dependent on site <br />accessibility and mine development timing. In general, baseline monitoring is conducted for at <br />least six consecutive months, usually from April through September, in order to provide <br />adequate data to show seasonal variations in water quality and quantity. Winter access to most <br />sites within the MCC permit area is impractical and not feasible, so baseline monthly monitoring <br />is generally not performed from October through March. A summary of the approved baseline <br />and routine monitoring program frequencies is presented in Table 5. <br />The chemical analyte suite for the first five years of sampling for both groundwater and surface <br />water samples, including one year of baseline sampling, is presented in Table 6. After <br />monitoring sites have been monitored for five years (including approximately one year of <br />baseline monitoring), the analytical parameter suite list is reduced and samples are submitted for <br />laboratory analysis of total suspended solids (TSS), total dissolved solids (TDS), electrical <br />conductivity (EC), pH, dissolved iron, and total iron. Field parameters (pH, EC, temperature, <br />and flow or water level) are also recorded. <br />The Upper and Lower North Fork and Middle Sylvester Gulch monitoring sites have expanded <br />analytical parameter suite lists, in order to provide data for the on-going characterization of the <br />North Fork. The North Fork and Middle Sylvester Gulch lab parameters include those listed in <br />Table 6, plus chromium, nickel, silver (total), cyanide (total), iron (total recoverable), alkalinity <br />(total CaCOA bicarbonate, carbonate, hydroxide, nitrogen (ammonia), ortho-phosphorus <br />(dissolved), and sodium adsorption ratio (SAR). <br />Revised 09/07- PR12; 08/16- TR139 MydroGeo, Inc <br />
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