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Regional ground water flow from the west is along the coal seams, discharging into Maitland Arroyo. <br />' Thus, the underground workings act as drainage conduits, directing ground water into and out of the arroyo <br />alluvium. During the wetter months, water Oows increase in the Maitland alluvium, and the watertable rises. <br />When the hydraulic head is higher in the alluvium than in the workings, the reverse would occur, whereby <br />surface water would recharge the coal seams and into the underground workings. Thus, the underground <br />' workings would also act as large storage reservoirs. <br />The rate of discharge into or out o[ the arroyo alluvium is controlled primarily by coal permeability and <br />' hydraulic gradients. At the time that piezometers were installed, water levels in the underground workings <br />were higher than in the bedrock near the arroyo as indicted by the water levels at Site W82-10 (6237 feet). <br />Water levels in the workings of the Champion and Maitland No. 2 Mines were at 6241.8 feet (W82-12L) <br />' and 6240.8 feet (W82-9R), respectively. <br />Sector II <br />' Sector II is bounded by Maitland Arroyo to the south and by a fault to the northwest. The sector is <br />partially dissected by a dike which intersects the fault in the west central portion of the permit area. <br />' Water levels in Sector II indicate a relationship between bedrock ground water and Maitland Arroyo <br />similar to that in Sector I. However, only limited mining has taken place in the Lower Robinson Seam of <br />Sector [I. Variations in static water levels for the various wells indicate the increased length of time these <br />' units require to reach equilibrium with the water level in the alluvium beneath Maitland Arroyo. The water <br />level in the Lower Robinson seam underground workings, however, is the same throughout Sector II as <br />Sector f due to mining through the dike (see wells W82-6R and W82-lOR). <br />' Sector III <br />' In Sector III, a similar relationship exists between the major strata and the Gordon Arroyo alluvium. <br />Piczometric levels at Sites W82-2, W82-3 and W82-15 are largely hydrostatic. Ground water Oow proceeds <br />up dip from the west, moving through the strata and ultimately discharging to the alluvium of Gordon <br />' Arroyo. The point at which these strata subcrop beneath the alluvium is where discharge takes place. <br />Geochemical data confirms this Oow system. The electrical conductivity (EC) of the Alluvial WeII in <br />Gordon Arroyo, located up gradient of the Cameron and Lennox seam subcrop is 900 umhos/cm. In <br />' contrast, alluvial piczometers down gradient from the subcrop limit have higher EC values. This increase <br />in EC is indicative of mine waters discharging to the alluvium. The Gordon Mine workings intersect the <br />Gordon Arroyo alluvium just upstream from W82-21A. The intersection controls the interaction of the <br />' alluvial ground water discharge with the workings and bedrock ground water discharge. <br />Gronnd Water uali <br />t Limited chemistry sampling of "natural" ground waters in the region has been conducted as most ground <br />waters in the area have been affected by historic mining activities. The major chemistry of "natural" ground <br />' water in the mine plan region is dominated by sodium and bicarbonate species. Concentrations generally <br />range from 70 to 200 mg/I Cor sodium, and from 150 to 300 mg/I for bicarbonate. Calcium and sulfate arc <br />also present in significant quantities. Calcium values range between approximately 50 and 100 mg/I while <br />' sulfate ranges between 200 and 350 mg/I, rivaling bicarbonate as the dominant ion. Total dissolved solids <br />(TDS) values vary between 800 and 1300 mg/l, and average approximately 1000 mg/I. pH values are neutral <br />to alkaline, varying from 6.5 to 8.2. All water quality collected from 1984 through 1988 is presented in <br />Appendix 2 and summarized in Tnble 2. <br />