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~~ <br />Pega 11 <br />Employing the data and basic knowledge of the process, a continuous flow plot plant program was <br />designed to Investigate the recovery of cyanide using ehher complete mbc reactors In series or stripping <br />towers. <br />or obtain design Inforrnatlon. The results Indicated that WAD cyanide levels of 218 mg/I could be reduced <br />to less than 10.0 mg/I. The Increase In total cyanide was due to sdubllzatlon of Iron and formation of the <br />stable Iron cyanide complex. The change In chemistry noted Indicated the need to examine each <br />appllcatkx-ard each slurry IsldNldually to determine potential changes In the slurry chemistry. An overall <br />removal of cyanide of greater tharf 95 percent was achieved. The apparetus simulated a complete mbr <br />reactor: Alr flow rates of 80 and 100 L(mlrt'were employed along with 10 L slurry samples. <br />The plot plant program was undertaken to verify the laboratory results and to obtain the necessary deslgn <br />Information for the full-scale cyanide recovery system. The slurry used In the picot plant study Has obtained <br />from the Martha Hill Gdd Mlne located In the town of Waihl, New Zealand. The slurry exhlbrted chemical <br />~.`:• and physical characteristics slmlar to those anticipated at the Gdden Cross Mine and provided an excellent <br />continuous untreated teed for the pilot plant program. The form of the WAO cyanide was predominantly free <br />and a basic pH was selected for the volatilization process. <br />In the first phase of the study, the use of multiple complete mix reactors In series was Invest gated, along <br />with various aeration periods and air Flow rates. Course bubble flexcap diffusers were use'i to facilitate <br />recovery of free cyanide and to minimize buildup of total dissolved solids and precipitates <br />T.p <br />\:Y <br /> <br />The results of the aeration basin studies are summarized In Tables 7 and 8. At slurry feed rates ranging from <br />0.5-2.2 m'/hr, air flow rates ranging from 2.4$.0 m'/m= min, aeration periods ranging from 138312 minutes, <br />and a slurry depth of 7.3m, WAD cyanide was reduced from 150-230 mg/I to 157 mg/1. 1'he results In <br />Table 8 Indicated that In multiple baffled systems of 3-5 complete reactors, the bulk of the cyanide removal <br />occurred within the first hour of aeration regardless of air flow, pH, or influent cyanide coicentrations. <br />However, there was a marked difference 1n relative cyanide removal whhin the first hour depending on the ~ ~ <br />air flow rate. No mechanical problems were encountered with the equipment or diffusers although certain <br />deficiencies were noted In the actual battle construction. No buldup of chemical precip{tates were noted. <br />TABLE 7 <br />RESULTS OF THE CONT{NUOUS FLOW PILOT PLANT STUDY USING COMPLETE MIX REACTORS <br /> Shirty fsW Influent No. of Total Aenlion Effluent <br /> Rat <br />; Influent WAD CN Alr Flu= Slurry Depth Reactor Period WAD CN- <br />Tr1al Im <br />lhrl (oHl (mM) ma/m=emin (m) In Serlea lminl (mdn <br />1 1.7 B.6 200 1.5 1.3 1 r" ~ 178 67 <br />2 1.7 9.6 150 1.3 1.3 7 776 4] <br />] 2.2 B.6 226 I.fi t.3 1 106 67 <br />/ 2.2 B.7 226 ].9 1.] 1 106 67 <br />5 1.7 9.7 19B 1.1 1.] ] 1]B 60 <br />6 1.6 9.7 195 4.5 1.7 ] 170 52 <br />7 2.2 B.B it+8 2.1 1.3 7 106 BI <br />B 2.2 10.0 1 B2 /.3 1.7 S 92 67 <br />B 0.5 10.0 207 1.3 1.7 S 712 28 <br />10 0.5 100 1ST 2.B 1.3 5 712 28 <br />it 0.3 10.0 19B I.S 1.] 5 ]72 2] <br />72 0.5 10.0 170 1.5 1.] 5 012 22 <br />10 0.5 t0.0 203 1.3 1.] S 712 ~ <br />11 0.3 70.0 179 6.2 1.] S 072 16 <br />15 0.3 10.0 171 fi.B 1.0 ] 167 16 <br />t6 OS 9.B 164 4.5 1.] S ]12 19 <br />t 7 0.5 B.0 176 6.0 1.] 3 012 13 <br />