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Ir <br />I <br />f <br />~' <br />Page 10 - <br />of WAD and total cyanide to levels In the range of 5-20 tng/I. By lowering the level Of metals and cyankle <br />requiring downstream treatment, lower effluent levels can be reached. <br />The Impoundment Into which the tailings are dlscftarged should be designed to enhance cyanide <br />degradatkxf, thereby minimizing downstream. treatment requirements. If downsVeam treatment of decant <br />water Is required prior to discharge to a surface water, conventional chemical or bidogical treatment should <br />be 'employed as These processes are'best -suRed for this purpose. The use of chemical or bidogical <br />treatment for slurries Is unwarranted or Impractical In most cases from both an environmental and economic <br />standpoint. The next section details the approach taken by Cyprus Gdd to develop the 9rst full-scale <br />cyanide recovery process for the tailings slurry at the proposed Gdden Cross Mine. <br />Bench and Pilot Plant State Investigations <br />A series of bench scale laboratory tests were first utilized In the study of cyanide recovery trop slurries. A <br />schematic d the laboratory apparatus is presented on Figure 4. The slurry utilized was obtained from <br />associated metallurgical tests. The chemistry of the tailings scurry and the experimental results are presented <br />In Table fi. The pH d the slurry was lowered Into the proper range with sulfurk acki, utilizing a 2.0-hour ~ <br />stripping period, and reneutrailzatlon with lime to a pH of about 9.5 - 10.0. <br />TABIF 8 <br />CHEMISTRY OF TAILINGS SLURRY BEFORE AND AFTER CYANIDE RECOVEIaY <br />~:> . -. <br /> Before After C vanide Recover~_ <br />Parameter t't Cvanide Recovery Trial 1 Trial 2 <br />pH (in pH units) 10.4 9.7 1(1.2 <br />Total Alkalinity (as CaCO~ . 575 . _ - - . 170 -. _ 16.4 _ <br />.+ <br />Total CN- 218 - _ <br />.. 29.4. 2a.6 <br />-r. - . <br />WAD CN- 213 7.4 E..B <br />Total Hardness (as CaCO,) 307 2170 2030 <br />Sulfate 360 2525 2350 <br />SCN 34 37 3E• <br />As 0.8 0.8 C .7 <br />Ca 123 869 Bta <br />Cd <0.01. <0.01 <C.Ot -, -. ., <br />' .. <br />Cr ..... -: 0.02 .... ._ . .. <0.02 <[.02 <br />Co 0.16 - - 0.33 C.30 <br />Cu 4.7 - 6.0 E.1 . _ <br />Fe 1.3 8.7 ; : E.7 - <br />Pb <0.1 <0.1 <0.1 <br />Mn 0.01 0.02 0.02 <br />Hg 0.0155 0.0004 0.0001 <br />Ag 0.15 0.04 0.04 <br />Zn 0.64 0.01 0.06 <br />Alr Flow (L/min) ---- 80 100 <br />t'1 Ali values In mg/I, unless otherwise stated. <br />These experiments completed at the Department of Science and Industrial Research (DSIR) in Wellington, <br />New Zealand, were conducted to verify the effectiveness of the process, but not to optimize the nical usage <br />or obtain design Information. The results Indicated that WAD cyanide levels of 218 mg/I could be reduced <br />