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Figure 3 graphically displays this hydrograph for 1987. Average daily <br /> discharge ranged from 31, 014 gallons per day (gpd) during mid January <br /> to 262 , 000 gpd during December. Extremes in average daily discharge <br /> are usually explained by pump efficiency since flow measurements are <br /> based on pump hours . As indicated, a major flow increase was observed <br /> in December. This was a result of increased flow encountered during <br /> mine development activities during that period. <br /> When relating calculated discharge to the inflow results, <br /> correlation of inflow to discharge is relatively close. An inflow of <br /> 4 5. 4 gpm relates to 6 5, 376 gpd. Pump records are near this inflow for <br /> most of the months during 1987 (Table 3) . <br /> New Elk Mine <br /> At the New Elk Mine, thirteen sources identified in the 1983 <br /> mine inflow survey were examined. No additional sources were found <br /> other than those thirteen, of which three were dry. Table 4 presents <br /> the location, probable water source and estimated gallons per minute <br /> (gpm) for each of these sources. Major sources were measured <br /> volumetrically while seepage and weeping faces were estimated. A total <br /> of 123 gpm inflow was estimated. Of that amount, approximately 109 gpm <br /> is being generated from mined out areas totaling approximately 2, 800 <br /> acres (sources III, IV, V, VIII, IX, X, XI, XII and XIII ) . <br /> Representative water quality of the inflow was measured . <br /> Table 5 presents the temperature, conductivity and pH of each source. <br /> Quality of those sources seeping from gob or abandoned mine areas was <br /> higher in temperature and conductivity than those areas of current <br /> workings . Quality ranged from 1, 830 to 3, 540 umhos conductivity, 15.6 <br /> to 18 . 30C temperature and 6. 7 to 8. 0 S .U. pH. Quality of active areas <br /> ranged from 762 to 1045 umhos conductivity, 9.9 to 15. 30C temperature <br /> and 6.9 to 8. 0 S .U. pH. <br />