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~~ <br />The NEt.P is a relatively simple test which could be conducted quickly in the field <br />(Coasteeh Research Inc., 1989; Miller et al., 1990), a distinct acl~~antage; over thz three <br />previously mentioned tests. However, both Coa:tech Research Inc. (1989) and Miller et al. <br />(1990) indicated that the NAP underestimated the capacity to produce acid. One possible <br />explanation for this flaw is that the hydrogen peroxide "digestion" does not completely oxidize <br />the iron sulphides present in the mine waste samp:.es. Consequently, the acid generatedi in the <br />test is less than the actual acid production potential. <br />The use of hydrogen peroxide to accelentte the oxidation of sulphide minerals was <br />previously applied to determine the acid potential of soils (Sobek et al. 1978). Mirza et al. <br />(1992) tested this method and reported incomplete ~~xidation of coal, coal pyrite, and ore pyrite. <br />Finkelman and Griffin (1986) proposed another method, referred to a<; the Hydrogen Peroxide <br />Test, for deternrining the pyrite content of coal related wastes. Coastex:h Research Inc. (1989) <br />applied this technique to hard rock mine samples and concluded the method was "too inaccurate <br />and erratic to be of real use." <br />O'Shay et al. (1990) subsequently modified the method of Finkt;lman and Griffin (1986) <br />and achieved pyrite recoveries on pyrite standards of 97 to 102%, as compared to 61 to 171% <br />for the original method. Thus, the modified technique was highly accurate in determining the <br />pyrite content of the standards, which suggests that similar modific;rttion may improve the <br />accuracy of the NAP Test. This paper presents results from such a madificadon, and compares <br />these results to those of other static tests and the Net NP determined by mineralogical analyses. <br />Based on the results, field application of the test is discussed. <br />Materials <br />METHODS <br />Four waste rock samples, identified as RK1 to RK4, and six tailing samples, identified <br />as TLl to TL6, were collected for testing. The mine waste sample were split into different <br />subsamples for subsequent chemical and mineralogical analysis and static testing. The splitting <br />procedure was tested by analyzing the sulphur and cazbon dioxide content of three sample splits, <br />to ensure uniformity of the samples generated. <br />Sulphur was analyzed by LECO induction f~.rrnace and sulphate was analyzed following <br />a sodium carbonate leach. Carbon dioxide was analyzed using a Coolermetrics carbon dioxide <br />analyzer. Silica and major metal components were extracted using bor<<te fusion and analyzed <br />using DC Plasma. X-ray diffraction (XRD), in ccmjunction with the chemical analyses, was <br />used for mineral identification as well as for determination of the approximate modal <br />composition. <br />Static Test Procedures <br />Standard Acid-Base Accounting, Modified Acrid-Base Accounting, and the B. C. Research <br />initial Tests were conducted using the methods of Sobek et al. (1978), Iawrence (1990), and <br />147 <br />