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<br /> <br />documented in poorly-drained soils and extremely acid soils with pH levels below 5.0. Liming the soil <br />causes a lowering in the solubility of manganese and presumably brings the iron and manganese into <br />better balance in relation to plant requirements. Documented cases of iron toxicity are rare and <br />appear to be limited to flooded soils (Barth et al., 1981). Extremely high levels of iron often are not <br />toxic but cause imbalances or interfere with the uptake of other essential nutrients. <br />Total Sulfur. NP. and ABP. The sulfur content of overburden and interburden is determined to <br />predict the acid -producing potential of this material. In conjunction with potential acidity, the <br />neutralization potential from alkaline carbonates, exchangeable bases, and weatherable silicates is <br />measured. Sulfur fractionation (i.e., pyritic, sulfate, and organic) analyses are generally performed <br />when potential acidity exceeds the neutralization potential and/or when the total sulfur content is <br />greater than 0.5 percent. Amore accurate determination of potential acidity is obtained when only <br />pyritic sufur values are utilized (Sobek et al., 1987) After the potential acidity and the neutralization <br />potential are determined, an acid base balance is determined by subtracting the potential acidity from <br />the neutralization potential. An acid-base potential (ABP) balance indicates whether acid or base <br />producing elements are in the sample and to what degree (Smith et al., 1974). This balance reveals <br />whether the material will become acidic or basic after being blasted, spoiled, and weathered. A <br />positive ABP indicates the spoiled material will have an increase in pH when basic elements <br />(carbonates) become soluble during the induced weathering process. A negative ABP indicates the <br />spoiled material will have a decrease in pH when acid producing components (pyrites and carbonic <br />acid) become soluble during the induced weathering process. <br />Coouer. Copper is important in root metabolism, ammonium and protein utilization, <br />oxidation-reduction reactions, and enzyme activation (USDA, 1957). Copper deficiencies are <br />generally not a problem (Traynor, 1980). Naturally occurring excesses of extractable copper have <br />not been reported in the soil literature (Munshower, 1983). <br />'ckel. This is a nonessential (to plant and animal life) heavy metal that could induce plant toxicity <br />symptoms if present in excess quantities. Nickel toxicity problems are restricted to poorly drained, <br />very acid soils, soils derived from serpentine parent materials or soils that have been contaminated <br />near smelters (Traynor, 1980; Munshower, 1983; and Barth et al., 1981). Normal plant available <br />nickel concentrations in soil are slightly less than 2 ppm (Barth et al., 1981). <br />I ~ Revised 9/99 2.04.6-17 <br />