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1 <br />1 <br /> GROUND WATER MONITORING <br /> <br /> BEDROCK <br />' <br /> Sandstone Aquifers <br /> Four sandstone aquifers are monitored at the site. They are, in ascending <br />' order: Trout Creek Sandstone (2 wells), Middle Sandstone (6 wells), <br /> Twentymile Sandstone (3 wells), and the lowermost sandstone bench of the <br /> White Sandstones (3 wells). The No. 5 Mine is between the Trout Creek <br />' Sandstone and the Middle Sandstone. The No. 9 Mine is between the <br /> Twentymile Sandstone and the White Sandstone. <br /> <br /> Water Levels <br />' Plots of the water levels in wells in the upper three aquifers are <br />presented in Figure 3 to Figure 14. The water level measured in the <br />Twentymile Sandstone has continued to remain fairly constant. A <br />' piezometric contour map of the Twentymile sandstone is presented on Figure <br />16. The indicated gradient is 525 feet per mile to the northwest. The <br />high indicated gradient is probably a result of one of the wells, Well <br />259, being in a discharge area of the aquifer. <br />' The plots indicate that the water levels in the Middle Sandstone stopped <br />declining in most areas of the aquifer in 1983 to 1984. Since that time, <br />' the water levels have been rising in all the wells except 83-03. The <br />changes are probably due to movement in the center of dewatering activity <br />and due to the above normal recharge during 1983 and 1984. Based upon the <br />1985 piezometric map (Figure 15), the ground water gradient in the Middle <br />' Sandstone ranges from 150 feet per mile to the southwest to 400 feet per <br />mile to the west. <br />'i ' The 1983 piezometric levels in the White Sandstone indicate that the No. 9 <br />Pline may not be effecting the 4lhite Sandstone. The rise in water levels <br />in the White Sandstone wells is also probably due to the high recharge in <br />1983 and 1984. As there was no significant decrease in the discharge from <br />' the No. 9 Mine until 1985, the water level change in the wells probably <br />can not be attributed to the effects of mining. Based upon the 1985 <br />piezometric map (Figure 17), the ground water gradient in the White <br />' Sandstone has not changed significantly and is approximately 100 feet per <br />year to the northwest. <br />' Water Quality <br /> The water quality data for the sandstone aquifers are presented on Table 5 <br /> to Table 12. The data indicates that the wa±er quality of all four <br /> sandstone aquifers is fairly constant over the whole period of <br /> measurement. The tables include either all data collected through 1985. <br /> Also, carbonate data is included when it is greater than zero (this <br />' applies for all the water quality data). <br /> -2- <br /> <br /> <br />