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1.3 PREPLANNING TOTAL MINING OPERATION <br /> 1.3.1 Acid-Base Account <br /> In the humid areas of the United States, the toxicity associated with acid <br /> results largely from the oxidation of iron disulfides. This process takes <br /> Place when earth disturbance activities such as mining (Temple and Koehler, <br /> 1954; Hill, 1970) and highway construction (Miller et al. , 1976) expose iron <br /> disulfides to the atmosphere. Since the public in the United States has <br /> supported legislation that acid-toxic or potentially toxic materials <br /> (a source of pollution) will not be left exposed, the need for a basis to <br /> evaluate overburden materials arose. <br /> Acid-base accounting is a dependable criterion by which overburden materials <br /> can be evaluated. An acid-base account consists of two measurements: <br /> (1) total or pyritic sulfur and (2) neutralization potential. The <br /> accounting balances maximum potential acidity (from immediately titratable <br /> sources plus sulfuric acid equivalent calculated from total sulfur) against <br /> total neutralizers (from alkaline carbonates, exchangeable bases, weather- <br /> able silicates or other rock sources capable of neutralizing strong acids <br /> as measured by the neutralization potentials). <br /> The total or pyritic sulfur content (see 3.2.4) accurately quantifies <br />�. potential acidity of materials when all sulfur is present as a pyritic <br /> mineral. When gypsum is found in an overburden sample or the materials <br /> are weathered, sulfur occurs in the form of sulfates. Samples high in <br /> . organic carbon usually contain organic sulfur. When part of the sulfur . <br /> occurs in nonacid-producing forms, the maximum potential acidity as calcu- <br /> lated will be too high. It is for this reason that such calculations are <br /> referred to as maximums and that in doubtful cases appropriate acid and <br /> water leachings should be made to rule out those forms of sulfur which do <br /> not produce .acid (see 3.2.6). Then from the stoichiometric equation of <br /> pyrite oxidation, the maximum potential acidity can be calculated in terms <br /> of calcium carbonate equivalent. Overburden material containing O.1% <br /> sulfur (all as pyrite) yields an amount of sulfuric acid that requires <br /> 3.325 tons of calcium carbonate to neutralize one thousand tons of the <br /> material. The neutralization potential (see 3.2. 3) of overburden materials, <br /> the second component of a net acid-base account, measures the amount of <br /> neutralizers present in the overburden materials. This measurement is <br /> found by treating a sample with a known amount of standardized hydrochloric <br /> acid, heating to assure complete reaction, and titrating with a standardized <br /> base. The result is then expressed in calcium carbonate equivalents.. When <br /> balanced against acidity from the total sulfur measurement, a net acid-base <br /> account can be made. <br /> From the acid-base account, potentially toxic material is defined as any <br /> rock or earth material having a net potential deficiency of 5.0 tons of <br />_+ calcium carbonate equivalent or more per 1000 tons of material. The 1000 <br /> tons is based on the assumption that an acre plow-layer contains 2 million <br /> pounds of soil. Regardless of the acid-base account, materials which have <br /> a pH of less than 4.0 in a pulverized rock slurry in distilled water are <br /> i defined as being acid-toxic. <br /> 3 <br /> ti } <br />