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interact by the chosen method of mining. <br />Thus, the prediction of acid mine drainage <br />cannot be based exelus ive ly upon overburden <br />analysis, although to a large extent, the <br />character of the factors mentioned above <br />is controlled by the rock chemistry. At <br />best, overburden analyses provide a first <br />approximation of the expected mine drainage <br />quality and it is only when the strata of <br />various chemistries are allowed to interact <br />in a backf filled mine, which itself is con- <br />stantly readjusting in terms of its hydro- <br />logy, geochemistry, pore space gases and <br />surface re vegetation, that the quality of <br />mine drainage emanating from the backf filled <br />mine can begin to be assessed. Usually <br />these adjustments take place over many <br />years and the true nature of the drainage <br />quality may not be i~mnediately discerned. <br />The assessments of a stratwo's capa- <br />bility to produce alkaline or acid drainage <br />are to be used as guides for the placement <br />of spoil material in order to minimize the <br />environmental impact of the mine of the <br />adjacent streams. lbxic (acid producing) <br />material should be isolated from the near <br />surface environment, whereas alkaline mate- <br />rial should be utilized to enhance revege- <br />tation. '!b extend overburden analyses to <br />the prediction of mine drainage quality <br />without considering the kinetics of acid <br />or alkaline release, the ground water geo- <br />chemistry, the chemistry of recipient <br />streams, the quality of the rain, the <br />arrangement of the spoil material in the <br />backfilled mine (blending versus segrega- <br />tion), the hydrology of the mine, the evo- <br />lution of pore space gases and the chemical <br />loads (as opposed to concentrations) of the <br />acid and alkaline leachates, ignores the <br />multivariant nature of the acid mine drain- <br />age problem and will lead to erroneous con- <br />clusions. <br />The initial objective of this study <br />was to ascertain, through laboratory experi- <br />ments, what effect various leaching solu- <br />tions had upon the leachates of several dazk <br />gray shales. Because each sample was ex- <br />pected to have a different chemical compo- <br />sition the experimental design vas extended <br />to include ancillary study that would test <br />the various rock parameters to determine <br />which parameter best predicts the quality <br />of leachate that would be expected from <br />each sample. <br />Experimental Design <br />Eleven samples of dark gray to black <br />shales were collected Erom newly cut cores <br />taken from several strip mines in Wharton <br />Township in southwestern Pennsylvania. <br />Four samples were collected from above the <br />Brush Creek coal seam, four from above the <br />Mahoning coal seam, and three from above <br />the Lower Kittanning seam. The 11 shale <br />samples were crushed to pass a four milli- <br />meter sieve and subsequently riffled into <br />three representative portions of roughly <br />equal size, giving a total of 3) samples. <br />Earn of these was then further riffled to <br />produce two representative but unequal <br />portions. The larger portion vas used in <br />Table 1. Chemistry of Synthesized Acid <br />Aain (R) and Synthesized Acid <br />Mine Drainage (A). <br />Synthesized Acid Hain (R) <br />Concentration <br />Component _ (mg/1) <br />+ <br />H ++ 0.21 <br />Ca++ 1.08 <br />Mg+ 0.15 <br />Na 4.75 <br />K+ 2.25 <br />so4 s.4s <br />C1- 9.39 <br />NO-5 6 .50 <br />Synthetic Acid Mine Drainaaipe (A) <br />concentration <br />Component (mq/1) <br />Fe ~+ 210.0 <br />Al+++ 15.0 <br />Mg++ 51.0 <br />Mn++ 19.0 <br />Ca++ 100.0 <br />Na 2.0 <br />H+ 3.0 <br />SOq 1100.0 <br />Cl- 110.0 <br />the simulated weathering tests, and the <br />smaller portions were used for whole rock <br />analysis. <br />Simulated Weathering Tests. Each of the 11 <br />shale samples vas ri fled into three repre- <br />sentative portions - in essence generating <br />three groups. The 33 samples were placed <br />into individual plastic chambers through <br />which humidified air was constantly passed. <br />At weekly intervals the chambers were opened <br />and one group vas covered with ~deionized <br />water (wl, a second group was covered with <br />synthesized acid rain (r), and the third <br />group was covered with synthet in, acid mine <br />drainage (a). The composition of these <br />solutions is shown in Table 1. <br />The leachate volume was measured and <br />analyzed for pH, specific conduuaance, <br />acidity (hot mineral), alkalinity (cold <br />titratable) and sulfate concentrations. By <br />noting the weight of the rock sample used <br />in the weathering test and the ieacha to <br />volume and quality, all results can be con- <br />verted to milligrams of acidity, alkalinity <br />or sulfate produced for each leaching per <br />100 grams of sample. These values are <br />plotted versus time to graphically depict <br />acid or alkaline production trends with time. <br />The sulfate ion is produced by pyrite <br />oxidation and is useful in in [e x~pre [inq [he <br />degree of oxidation that has taken place. <br />The specific conductance is a measure <br />of the amount of ions in solution and is <br />useful in interpreting the degree of chemical <br />reactivity. <br />440 <br />