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REP43993
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REP43993
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Entry Properties
Last modified
8/25/2016 12:46:20 AM
Creation date
11/27/2007 10:06:39 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1988112
IBM Index Class Name
Report
Doc Date
4/16/1992
Doc Name
FAX COVER
From
BATTLE MOUNTAIN GOLD CO
To
MLRD
Media Type
D
Archive
No
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e <br />.~f' <br /> <br /> <br /> <br />/"~ <br />B4i 16'52 17:14 a' 17196723363 <br />C;R7TLE n7,~,0LD <br />J. J. BYERLEY ET AL <br />An-X-2). The An-X-1 column is sized [u cnllcct virtually all <br />the residual meta! cyano complexes (Cu, Fe, NI, Co, etc.} as <br />well as a small perrcntatge of SCN' and unknown amounts of <br />sulfate and thiosulfate (Snopck, ]986). The Aa-X-2 column <br />wllects 8D-85% of the SCN' and again unknown amounts of <br />sulfate and [hiosulfate (Trang,1985), After step four, the main <br />wastes[rcamwill contain csscntiallyno Cu, Fe, Ni, Co, possibly <br />a few mg/1 Zn, about 15%a o[ the original SCt~r concentration <br />and all original ryanide less the amount associated with the <br />metals removed in Lbc previous steps. Step five shows the <br />waste stream being recycled after the pH has been raised and <br />fresh makeup cyanide has bees added For total recycle there <br />will be a build-up of impurities in the circuit not removed or <br />controlled by the preceeding steps, thus a bleed of between 2 <br />and 5°l0 of the recycle stream is rcgtfued Step six is an <br />oxidation step to destroy the SCN- and CN' in the bleed <br />stream. To accomodate the water balance in the circuit it may <br />be necessary to upgrade the cyanide recycle stream by a factor <br />of at least 10 using an anion exchanger- The entire pror^cc u <br />not wmplete until exhausted columns have been eluted and <br />re;~enetated. Of particular iatere;t i; thq yluant from the <br />second anion exchange (An-X-2). This column contains SCN' <br />with some sulfate and thiosulfatc. The alkaline eluan[ stream <br />may be oxidized electrochemically to regenerate <br />approximately60% of the Gl~moietyFrom SCIT and recycled <br />to the cy'.widation circuit (13yerley and E.nns,1984; lJS Patent <br />4519880; U5 Patent452666Z). <br />PRECIPITATION STUDIES. <br />Copper Cyanide Precipitation <br />The metal complexspeaes formed when copper interacts with <br />cyanide in basic solution (pH 1Q-12) have been identified as <br />Gtit(CN)z-, Glt(CN)3~ and Cu(CN)a3 [Copper and PIat,1966; <br />Penaeman and Jones,1956; Noblitt (7973)]. 7n the case oFzinq <br />the cyano com2plexcs aze reported to be Zn(CN)z, Zn(CN)~ <br />and Zn(CN)q ~ (Iza[t et al, 7965). Besides these aqueous <br />complexes i[ u Found the[ at low pH, solid CuCN i5 formed <br />No evidence of asimilaz solid zinc cyanide or ZnCN+ has been <br />reported or found experimentally in this work. The stability <br />constant data for these and other c}^alt0 complexes of interest <br />in this Communication arc cpmpilcd in many volumes (Sillen, <br />1964; SIDety 1971], <br />Tn view of the above an aqueous solution containing cyanide, <br />copper and zinc is a complicated system which may be <br />adequately represented as a solution containing the copper <br />and zinc cyanide complexes noted above as well as HZQ, H+, <br />CN", HCN, Cu+, and Zak+. Using this aqueous solution <br />model two sets of equations can be written to represent the <br />chemical equilibria before and after the precipitation of <br />CuCN. This equih~brium model can be used to determine <br />et7aceatrations of all species at different pH values of the <br />cyatude solution thereby predicting the precipitation of CuCN <br />P. 07 <br />i <br />and the decomposition of zin~ cyanide complexes upon <br />aGddipti00. <br />FIGURE 2 <br />DISTRIBUTION OF DIAGRAM FOR COPPER <br />CYANIDE GOMPLEXES <br />to <br />0.8 <br />m <br />~u O.fi <br />c <br />N <br />C <br />a <br />~ O.d <br />0 <br />0 <br />b 0.2 <br />v, <br />'•~~ u(Ct•Q4 <br />.` <br />.~ <br />z- <br />Cu(CN)3 <br />1 <br />1 <br />1 <br />1 <br />Cu(CN)2 1 <br />L <br />1 ____ a_t <br />) <br />1 A-2 <br />1 <br />1 <br />t <br />CuCN <br />0 ,`~ <br />p 4 6 8 t0 <br />pH <br />I"igute 2 shows the copper cyanide distribution diagrams <br />calculated using the equilibrium model for two solutions, one <br />a copper-cyanide solution (A-1) and the other a <br />capper-zinc-cyanide solution (A-2), (refer Co Table 2 for <br />solution composition). These diagrams provide an overall <br />picture of the equilibria of the systtms. A vertical 1'me drawn <br />at a selected pH divides the distribution curves into segments <br />which are proportional to molar ratio of the concentration of <br />a copper containing cyano complex and the total <br />concentration of copper in solution. For example at pH 3 the <br />fraction of capper present as CuCM is 0.70 and of Cu(CN)a--' <br />is D.30. The fractions of Cu(CN)3a-and Cu(CN)a'3 arc quite <br />small at this pH. As the pH increases the di, tri and tetra cyano <br />complexes become more predominant as competition o(thc <br />proton for cyanide ion weakens. 1t is interesting to note that <br />there is no range of pH where more than two <br />copper-containing cyano species are present in appreciable <br />quantity. The distribution diagram also indicates the[ the <br />distribution of copper cyano complexes is affected only <br />marginallyby the addition of Zn(II) to [he solution. A similar <br />distribution diagram can be calculated for the zinc-cyanide <br />- 333 - <br />RANDOL GOLD FORUM 88 <br />
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