Characterization of the acid or toxic potential of overburden material is generally accomplished by either a technique known as acid/base accounting (Smith and others, 1982; Sobek and others, 1978) or leaching tests (Caruccio and others, 1977, 1981, 1982; Caruccio, 1984; Geidel, 1979).
Acid/base accounting is utilized nationwide to assess acid or toxic potential and consists of the following three fundamental measurements:
Paste Ph is a measure of the sample's immediate acidity or alkalinity and reflects current geochemical conditions. Samples with a paste Ph of 4.0 or less are classed as acid/toxic regardless of the pyrite and neutralizer balance (Smith and Sencendiver, 1982; Sobek and others, 1978).
Solubility and mobility of many trace elements and metals in water are strongly dependent on Ph. For example, at a Ph 4.0 or lower, elements such as aluminum, copper, manganese, zinc, lead, and chromium can be released into ground or surface waters.
Maximum potential acidity is calculated from the pyrite content of the sample and the four-step chemical reaction of pyrite to acid formation (Sobek and others, 1978). This calculated value represents the maximum or worst case condition of acid production. The actual acid production rate and completeness of reaction cannot be estimated using the acid/base technique.
Neutralization potential measures the sum total of carbonates, alkaline earths, and bases available to neutralize acidity and represents the most favorable condition. Calculations of maximum potential acidity and neutralization potential are structured to equate the two measurements to a common basis for comparison. The resulting values, expressed as calcium carbonate equivalent, are compared to compute a net acid-producing or neutralizing potential. Materials exhibiting a net acid production potential of 5 tons/1,000 tons of overburden material or more as calcium carbonate equivalent are classed as toxic or potentially toxic (Smith and Sencindiver, 1982; Sobek and others, 1978; Sturm and others, 1984).
The primary advantages of the acid/base accounting method are:
The principal disadvantages of acid/base accounting are:
Application of this acid/base accounting method to overburden handling and placement plans throughout the country has generally been moderately effective in eliminating or reducing adverse water quality impacts. Acid/base accounting is typically considered state-of-the-art for overburden analysis.
Leaching or simulated weathering tests have been advocated by Caruccio and others (1977, 1981, 1982), Caruccio (1984), and Geidel (1979) as an alternative overburden analysis method. The procedure is designed to mimic the conditions expected to occur in regraded spoil. Samples are subjected to alternating water leaching and exposure to moist air. Leachate is collected periodically and analyzed for pH, acidity, sulfate, and any other constituents of interest. Supplemental information may also be obtained by petrographic study of pyrite morphology. Caruccio has indicated that fine-grained pyrite with a large surface area is much more reactive and likely to produce acidity than coarse-grained pyritic material (Caruccio, 1969, 1984; Caruccio and others, 1982).
Results of leachate analyses are plotted as a function of time resulting in data on rate of reaction and the quantity of acidity or alkalinity produced. Leaching simulations have been applied to eastern and midwestern minesites and are reasonably good predictors of short-term (2 or 3 years) drainage quality.
Caruccio (1984) suggested that acid/base accounting be used as an initial screening test for overburden samples. Materials containing a large net neutralization potential do not require further analyses. If total pyrite exceeds about 1 percent or if the neutralization potential is small, Caruccio recommends leaching tests to more accurately predict drainage quality.
The main advantages of leaching tests are summarized as follows:
The primary disadvantages associated with leaching tests are:
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