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cores, calcite is almost ubiquitous. Calcite serves two functions. First, it buffers <br />the pH of the water, which tends to slow the oxidation of pyrite, reducing the <br />production of acid. Second, it will neutralize the acid that is produced. The core <br />samples that exhibited low paste pH's are surrounded by non-acid producing, <br />calcite-bearing rocks. The water that contacts the low-paste pH materials will <br />have first reacted with calcite, and therefore developed a pH-buffer capacity of <br />its own. The groundwater monitoring data indicate that mixed overburden and <br />interburden waters have near neutral pH's. Sample pH's less than 6 are associated <br />only with the lower Dakota coal. Where the coal's permeability is high enough <br />to produce about Sgpm during sampling, the acid-producing reactions do not <br />appear to be fast enough to maintain the pH of the water less than 5. Oxidation <br />rates may increase due to [he mining process, however, other conditions which <br />inhibit acid production include the quantity of calcite present, and the reactivity <br />of the pyrite. In conclusion, the paste-pH test, conducted under oxidizing <br />conditions, indicates that only a small proportion of the overburden is likely to <br />produce acid. Acid that is produced will quickly be neutralized. During the <br />mining process, WFC tests the overburden. If and when acidic layers aze <br />encountered, they will be mixed with non-acidic layer to neutralize any acid <br />forming effects. <br />Potential impacts of replaced spoil on groundwater quality: The analysis of <br />geochemica] controls on groundwater quality suggests that the water chemistry <br />and concentrations of most elements of concern are controlled by mineralogic <br />reactions that will resist changes in water chemistry. Production of acid may <br />occur in very local settings and is probably most prevalent in the coal which will <br />be mined. Calculations indicate that neutralization of the acid will occur rapidly <br />with mixing of water, or with movement of acidic water into calcite-bearing <br />rocks. Also, the analysis conducted indicates that chemical changes aze not likely <br />to occur. <br />Effects of mining on the local geomorphology: Impacts from mining on the local <br />geomorphology will be long term, but appeaz to be of minimal significance. The <br />reestablished reach of the drainage which will be mined will result in a shorter, <br />slightly stepper stream channel. The potential for increased sediment loads in the <br />drainage (once pond 007 is removed) should be offset by the stable banksides and <br />the relatively small change in overall gradient. The increased runoff and <br />consequent erosion potential on disturbed basins in the mining area due to the <br />temporary loss of topsoil stricture should be of minimal significance. Contour <br />ripping, mulching and revegetation have been demonstrated to minimize soil <br />erosion and will be used to mitigate the increased runoff potential until the <br />topsoil structure is developed. <br />Effects of sediment ponds on channel characteristics and downstream users: <br />Potential impacts of sediment pond 007 on downstream users will involve <br />22 <br />