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<br />State Reg. <br />l underburden sample was less than 5 tons calcium carbonate per <br />1,000 tons of material. <br />Significantly different pH and neutralization potentials exist <br />between the Wolf Creek and Wadge overburden areas. The pH is <br />6.5 in Wolf Creek overburden and 7.9 in the Wadge overburden <br />area. The mean acid-base potential is +1.3 in the Wolf Creek <br />and +6.2 in the 4ladge areas. <br />Overburden mixing will effectively mitigate many of the extreme <br />(suspect) pH levels in individual cores. Reclamation success <br />will be determined by treating the Wolf Creek and Wadge <br />overburden areas independently. Since the greatest <br />availability for the most nutrients is at a slightly acidic pH <br />(6.5) and since trace metal availability increases <br />exponentially at pH levels less that 5.5, spoils showing very <br />strong acidity (pH < 5 and ABP < -5) will be limed or will <br />receive a two to three foot suitable spoil topdressing. <br />Nickel. Values for nickel range from < 0.3 to 9.8 ppm and have <br />mean values of < 2.3 and < 2.5 ppm for overburden and <br />underburden materials. Nine samples, or 7.6 percent of the <br />total number of samples analyzed, were above 5.0 ppm suspect <br />level. Of these, eight occurred in the overburden and one in <br />the underburden. These strata occur in the overburden cores <br />and comprise 9.4 to 40.0 percent of the individual core volwne <br />(Table 6-6). Weighted mean core concentrations are less than <br />3.3 ppm. <br />In most cases, high nickel concentration strata will blend with <br />other material of lower concentration during the course of <br />mining, and the effect will be to dilute the inimical zones. <br />Like most other trace elements, nickel is fairly insoluble over <br />a pH level of 6.b (Donahue, et al., 1972 and 14aclean, 1978). <br />Wolf Creek overburden may represent a potential problem area. <br />Liming, where necessary, (mean pH < 5 and ABP <-5) and <br />6-30 Revised 10/1/86 <br />