Proceedingsofihe 1SthSymposiumofMalaysian Chenical Elgineers SELECTIVE LEACHING OF SILVER FROM SELECTED SEMICONDUCTOR WASTE L. L Meng, A. N. Sadikitr",N. Othman,L S.N. KimarudiL H. B. Mat AdvancedProcessEngineeing ResearchGroup (AIEN), Faculiy of Chemical& Nat1]ial Engneering,UnivelsitiTeknologiMalaysia,81310Skudai,Johor,Malaysia. Resources 'Conesponding Fa{r +607-5581463, author.Phone:+607-5535526, Email: aziahrlniza@fkkksa.utm.my ABSTRACT Depleiion ofnatural resourcesis becominga seriousissuein rec€ntdecades.This siiuation gives an arlsing interest to r€cover recyclable rcsouces from indlrstrial waste Semiconduciorwaste thai containshigh concentrationofprecious m€ials may be treated as potenlial sources of precious metals if economic extraction is availableCharacterizaiionol the wast€ sampieir xhis sludy has shoqarlucrative silver contenl of of aluminium,copper,calciumandferum.Thepotentisl 5.35%by masswith co-presence of ihiosulfate solution in selective leaching of silver from this selected waste was invesxigat€d.Thiosulfat€ leaching of silver folows a combination of reaction paihs that include dircct l€aching, indircct leaching and catalytic lea,rhing. At selectedleaching condilions,nearly 90% of silv€r is leachedand high selectivitvis achieved.Silver Ieacljng efficiency is irfluence by concentrationofthiosulfate, Li S ratio, A: T ration and temperanrle.Varying initiai pH ofthe leachitrgagen!did not result in a markeddifferent in silver leaching efnciency. However, an alkaline medium is preferred to avoid or minimize decompositionof thiosulfate, loss of anmonia, formation of sulfide ions that enhanceFecipitation, and dissolulion of undesiredmetals Thiosulfate solution exhibited a high selectiviryof silver over othermetals. K€ytordsr Silver,Leaching,S€miconductor' 1 INTRODUCTION The grcwth of globai economics and human population has triggered the fear of exhaustionin nahrml resourcesincluding metals due to the increasiry consumptionand the deplethg sofices of natura] ore. Silver the m€tal of interest in this siudy has been usedas a monetaiymetal,jewelry and omamentsinceancienttime. In recentyeals,many technologiesthat utilized silver's propefiy ofhigh electrical andthemal conductance,and also the light sensitivebehavior of its compoundhave been developed. Nowadays,silver is conrnonly found in batteriesand cells, medical appamtus,catalvsts,electrical contacts, coatiry for elecfonic conducton, platirg of printed elech-ical circuit, phorographic productsandrecordablemediasuchas compacldisks. By the elld oflhe 19ih century, naiive or high-gade silver ores throughoutthe world had been largely depleted. Nowadays,most of the primary silver is exaactedas a byproduct in the processingof compiex copp€r, lead and zinc ofes (Masseyet dt, 1973)The de?letionof natural silver sourcesand its increasingconsumptionhas resultedin an arising interest to recover and recycle silver ftom photogaphic and industrial waste bLt conservalior' Recorer)ard reLlclmgot si.verfrom\ arlesaoronl) ersurerecource also at the sametime minimize the detrim€ntaleffectsof ore mining to ihe environment ln this study, potential of seleclive silver recovery from lhe sel€ctedsemiconductor waste is investigated using hydrometallugical process of solidliquid extaction, commonlyktrowr as leaching. Comparedto th€ conventionalhydrometallurgicalprocess thar rcquies complicaiedfumace operationand high consumplionof energyandtime, and also biological processwhich is complicated,sensitiveand canonly operateat a very low metal conc€ntration,hy&ometallurgical processcan be a simpler, less energy intensrve, more effective and economicmethodto recoverysilver ftom semiconductorwasle 5- 168 P.oceedilgs ofthe18thSymposjum ofMalaysjan Ctemical EryirceB ll1: \:: :: fii ln hydrometaliurgicalprocess,leaching is usually the first step in recovering metal from solid waste. Whendealingwith multimelal lvast€,which recoveryof only onemetal is desimbl€,it is importantthat the selecredleachingagentis selectivetowardsthe desired metal so that the resultant leach solution can be Durified wiih less effon DesDite seleflrrir).tne .elecleole,icr.ng ageil soord proridea good leaching petomance including fast kinetics and high efficiency. Besidethar, the leachingagentshouldhave a low toxicity. Otherwise,its operationandthe speniieachingsotution wjll posedangerio both humanand environment. Previously,Tang (1999) has repodedihe potenlialof using acid and chlondejn ieaching of silver fiom semiconductorwaste. The best leaching efficiency is achieved with a solution of hydrochloic acid and sodium chloride. Though only about 55% of silver l€achingjs rcportedandthe selectivity on silver is very low, suggesringthat a berier leachingagen! shall be used. Cyanideis currently the major leachingagent of precious metal in most ofthe mining industryrhroughoutthe world (Han e, at, 1994). Howeverirs exfeme toxicity eliminat€s-it $om consid€rationin this study. The leaching agent select€d is thiosulfaie(S,O3'J,whichis regardedby manyas theporentialsubsrilution of cyanid€ in the leaching of precious metal due io irs 1ow toxicity and effectivenessin leachingrefractoryorc (Berezowsky er dt, 1978;Kerley, 1981;Abbruzzese er dt, 1995; BrionesandLapidus,1998;Tlomase1al, 1998jBreuerandJefftey,2000;Jetrr€y,2001j Aylnore,200I; AybnoreandMuir, 200l). Tbiosulfate(SzOi) is an inexpensiveand non{oxic chemical.Reagenrsin ihe folrn of sodium thiosulfate and ammonium thiosulfate are commonly used in leaching, the removai of excesschlodne ill paperand textiie bleaching,ihe manufacturingofmatches, as a photographic fixing agent and the whitening of cotton fabric, bone and ivory. Medically, thiosulfateis kno*n asthe antidoleto cyanideandarsenicpoisoning(Aylmore and Muir, 2001). In addition. thiosulfate in the form of ammoniumthiosulfatehas been usedasa fertilizer for soil deficientin sulfur for decades. Theimportance ofthiosulfat€hpr€ciousmetalrecoverywasftst discovered in 1900s. This processis known as the Von Pateraprocess(Aylmore and Mui, 2001) and it bas b€enusedfor silver recoveryin SouthAmerica for many years. In this process,silver is exira.red by sodium rhiosulfate ieaching of dre product ftom a chlorodizing roasr of a silver-rich su1fideore (Flett s/ al, 1983). The chemisrry of rhe ammoniacalrhiosulfare l€achingsystemis complicated presence dueto the simultaneous of complexingligands such as ammonia and L\iosulfate, catal'tic cupdc'cuprous(Cu(II)-Cu(I)) redox couple, decompositionproductsof thiosulfateincluding tetrathionateand other sultur compound (Kerley andBemafd, 1981). Thiosulfateis a meta-stableanionthat tendsro decomposein aqueoussolurion,especial]yln acidic mediun. The factoa ihat influencethe stability of thiosuliat€areconcentration, pH, prcsence ofmetal ionsandsulfurmetabolizing bacteria (Aylnore andMuir, 2001). Th€ investigation of thiosulfate performance in the leaching of silv€r from semlconductorwaste,lvhich includesits ieachingeffici€ncy andparametersthar influence its leachingperformance,is the subjectof this study. 2 trXPERIMENTAI2.I MATERIALS Sampl€swere collected from the filter cake dryer of a wastewatertreatmentplan! of a semiconductorindustry. The sampieis grayish and is in the folnl of damp solid. Ior the initial pH adjustneni of leachingagenis,sodium hydroxide and sulturic acid were used. Leachingagentswere preparedjlom analyticalgade sodiumthiosulfai€penrahydrateand distilled water. Agitator used in the leaching exp€riment is mechanical shaker manufacturedby Labline (Mode14626). For leachingexperimentwith varied temperature,the mecharical shakeris r€placedby a temperature-controlled shaker(New Brunswick Scientific Irmova 4080).pH is measuredby EcometP25pH meter.Afier leachingis conpleted,laboratory c€ntituge (Hettich Zeniritugen EBA12R) is used to separatesolid and supematant.The concentation of silver and other select€dmetalsin the supematantis anallzed by aiomic absorylion spectrophotometer, AAS (GBCAvanta2000) 5- 169 Prcceedlngs of theI sdrSynrposiunol Mataysian ChemicatEngineeB 2.2 SAMPLE CHARACTERJZATTON Physrcaiard chernicai €haracle zations of sample were perfomed ro obi.tD pilysicat properties and ch€flical composition of ahesample. Physicai characierizatiois rn rhis siud, irclude waier and orgrnic content, apparent densiry, particle size with screen aid purosry wrh gdsadsorprior. 14h,lerbrcnemicat charrcrelTdrion. Lrera\ -cl].i! -D,spe|li\e X-ra)analysisrl D{XrandX-ra)Did.ac,ion anat}<srXRn/ \\ereJpptied 2.3METHODS 20 ml oi ieachingagentwasdispensedwith bufetteinto a I 00 ml Erlenmeyerflask. Theq solid sa1r}pleaccording 1o the specified liquid: solid miio was caretully weighted and addedto the le6chingagent. The mixrurewas broughtinro conracib/ nechanical shaking at 200 qrm for a period oi 3 hours- Throughout the coune oi shaknrg,ihe flask was cavered by aluminium foil ro flinimize evaporaiion of leach soludor and lojs of arlrmonia.The leachingp€riodof 3 houls x'as selecredfrom preliminary srudy.which was rdEquatefor the systemto reach equilibrilun. Aiier 3 hours of sh.rijtg. sample ot lhe rnixh.fe wastaken andcentrituged(2000rpm lor 3 min res). In theinvesligaiion ofthe eflectofl€achingagents'pHon leachingequiiibrium,initiat pH of leaching ag€ntswere first adjustedby concedr.ared(2.0 M) sodirnit hyiiroxid€ of sulfuricac d. Uhen lnesolllrorpH wasclose'oLhedesignfled \alue.adllLswenr wa! follow€d by th€ samereagentswilh more diluted concentation (0.2 M). In the investigaiionof the effect of temperatureon leaching equilibrium, exp€rimenrs were canied out in temperature-contolledshaker ll,irh a similar rotational speed and leachingtim€ wirh oiher expedments. Leaching agentsin the flasks were heaxedto the desigmtedtenperatu€ beforesolid sampteswere added. Experimentalprocedur€for selectiviry of leaching agent on sihc. qus similar to the study of leaching €quilibridn but ar the end of the experiment,th€ ieach solurior was analyzedfor concm1mtionof Ag, Cu, Al, Fe and Ca by AAS. Two seis of experiments rnd Letuperurure wc e cafriedoL ro ;\esrigare "ith dillerenr!h.o:u farecon.enndr.oo whether differencesin these parameterswill inlll,rence selectivify oi siiver. Leaching conditionsfor thesetesrswere: (i) I NI sodiumthicsuifate,A:T=1, L:S=200.50"C. leachingtime of3 hours,and (ii) 0.1 M sodiun thiosulfate,AiT=i. L:S=200.30.C. leachingtime of 3 hours. 3 RESULTSANI} DISCUSSION 3.1 SAMPLE CIIARACTERIZATION The semiconductolwaste sampleobtainedfrom dried filter cake consisrsof solids wirh varying sizes. The vaiue ofmass meandiametercalcuiatedis 490.0 !lm, which is taken as the averagediamet€ror padcle sie ofthe sample. Apparenrdensityafsanple was found to be 2.270g/cm' by muliipycnometer. Resultsfrom EnergyDispersiveX-ray Spectropholometer (EDAX) reveatedthat silver content in fie sampleis 5-35%by dry mass. Other metals thai co-pleseri h rhe sample mciudealuminium, copper,calciumand ferun 3.2 LEACHING EQUILIBRIUM 1.2.| | eaching Equilibrium: A Funcrion of fime Th€ time dependencyof leaching equilibrium of silver with thiosulfaaesolution is illwtrated in Figwe 1. It shows that the incremenrof silver leaching levels off after 5 minutes(300s),suggestingthat leachingequilibrium is achievedas early as5 minures. The resultsindicatethat ieachingtime needto be minimized oncel€achingequilib.ium is achieved. This is necessaryto avoid the deirimental effect of prolong leachingto the leaching efficiency as the equilibrium is shift€d toward reprecipirationof silver in rhe leach soiution. Leaching time of more than l0 houn should be avoided since ir was reportedthat silver app€aredlo be unsrablethereafler(Aytmor€, 2001). 5 ,170 Procccdilgso ne l3iir Symposium oli,IaiaysEnCtehiclt Engdr.eL: FICURE 1. percenl3geof silve. leachedtor rhe firsr I 0 rrirutes (experimenral colrditions: 0.1M sodiumthiosujfare, 30.C,L: 5=200,Ar T=1) 3.2-2Effectof Thiosuuate Concentration Fig re 2 shows that increasingthe rhiosulfate concmtrarion &om 0.01 M to 0.05 M drasr,cdllyincfease rhe percerlage or sil\er teacb,og from o2oolo S1",. q l0_f"lj Increase or rhroruttdreconcLrnalionfrom0.tM,ot.0Moolyinprove(abou,t00"offie 'eachiogeffcieDcy. Tbr. sligbr increa,edra) due ro rhe t""*.i"" ot **"r Jf,t*..i s l\er-trrosullhle comple\er. $hichrs,avored b] ncrea.ing corceDralon of!hio.utfare. FIGURE 2. Efect of thiosulfar€concenhationon silver leaching (experimental condirionsr 30"C,L:5=200,A:T=1,Leachingtime=3hours) 3.2.3EffectofL: S Ratio F;gurcI :llusraLe.rhal a.hary ircrea(ein .rtver leachingefficienc' $as ob.erued bv S_m:o t0 ro 200 rigue I a,soi usiaresttrari"".r* i" r*.tri l.:re.asine,rhe !: lom ettrcrency levelsotf afterL:S rafioof200. l i i i l I ) 5-t7l Proceedingsoftle 181hSymposiumofMalaysian ChemicalEngineers FIGURE 3. Effect ofI-rs ratio on silver leaching(experimentalconditions: 0.1M sodiumthiosulfate, 30"C,A:T-1, Leachingtime=3houn) 3.2.4Effec!ofA: T Ratio The effect of A:T ratio on silver leaching €quilibrium for solutions wilh thiosulfate concentation fixed ai 0.I M arepreseftedin Figure 4 Thereappearsro be a sharpincrease in leachingefficiencywhenthe A:T ratio is increased ftom 0.1 io 1.0. Maximumsilver leachingis achievedat A: T ratio of 1.0 and turther incr€asein A: T raxioslightly lowels the leachingeffici€ncy. 560 : bo IIGURE 4. Effect of A:T ratio on silver leaching(experimedalconditions: 0.1 M sodiumthiosulfare,30.C, L:S=200, Leachingtim€=3 hoxrs) 3.2.5EfIectOfpH Figur€ 5 ilustrates the €ffect of pH.q to leachingequilibriun of silver. It show€dclearly that varying pH"qdid not fesult in a marked diff€(ence in leaching efiiciency. Leaching efiiciencyfor pH"qrangeof8.02 to 10.82waswithin 80% to 83%while at pH.qof 12.9, lbeleach.ng effcrenc)decrease sligbrly.o "70.. 5- 172 Proceedilgs ofthe 18thSymposilmofMataysianChenicatErgircers r-!- FIGURE5. EffectofpHeqon silverleaching(ereerimental condiiionsr 0-1M sodiumrhiosulfate, 30"C,A:T=1,Lr5=200,LeachingtimF3 hours) It is concludedihat the idtial pH shouldbe mainlainedin th€ alkaline rangesincethe resultrngleach solurionswere more stable. Fomation ofprecipitate was noricid to occur faster with leach solution thar iniiial pH was adjustedto acidjc range. This was not a suryrising observationsince decomposirionof thiosulfate, formation of sulfide ions and loss of anrmoniawere all accele€tedby tower pH. 3.2.6Effectof Temperatue Th€ effect of remperatur€on silver leaching equilibrium with thiosulfate solution is presentedin Figure 6. The leachingefficiency increasesfrom rhe temperarueof3ooc ro 50"C but falls asthe temperatur€reached60"C. The decreaseofteaching efficiency at the temperatureof60'C is probably dueto loss of ammoniafiom the leachsolution. i;4 r4'd!c f c) FIGURE 6- Effect oftemperatur€on silver leaching(experimedratconditions: 0.1M sodiumrhiosulfate, ArT=1,L:S=200,Leachirytime=3hours) 3.3 SELECTIVITY OF LEACHING AGENT ON SILVER Figure 7 pr€sentsmetal conc€ntrationin the leach soluiion for two setsof experiment. In both cases,silver showed the highest conceni.ation, followed by aluminium, coppef calcium and ferum. The concentaiion of calcium and ferum in the leachsolution are-1ow, which are either und€rectedor less rhan 0.3 mg,{. Silver concentrationfor both sers of experimmtsis quite close. 5- t73 Proceedirysof the I8th Synposiur olMalaysian ChemicalEnginee6 FIGURE7.liletal conc€nlration in theieachsoiution(Eaperimental condirions: Set 1- I M sodiumthiosulfare, 50"C,A:T=1,L:3=200.3 hour!leaching; Ser2- 0.I M sodirmlthiosufare,30.C,A:T:1, LiS-200,3 houlr leaching) 1 CONCLUSION Semiconahrctor wastein this studyis a nrultimetalwastethat conrains5.35%of silverby mass.Co"existed netalsin lhe wasteinchrdeallnnnriun(16.94),copper(12.67),calcilrm (i.977")andfemn (1.30%). Severalteachingpanmetershave been idenLifiedtu influence silver leaching efficiency with thiosulfate.Theseparamete$are concentrationof thiosr late, L:S ratio, A:T ratio and iemperaflre. ln o.der to achievea significant amount of sitver dissolution with batchleaching,it is impotantthatconcertradon ofthiosulfareis 0.05M of more,L:S mtio is 50 or more, A:T ratio around I and temperaturenot higher rhan 50oC.For rhe cuaent semiconductorwaste sample,leachingtime of 5 lrlin tes io 5. |ours is adequate. Varying initial pH of the leacling agent did not rcsult in a rnl]lk€d different in silver leachingefiiciercy. However,an aikalinemediurnis prefenedio avoid or minimize decompositionof thiosulfate, loss of ammonia,fomation of sullate ions that eniance precipitation, anddissolutionof undesired metals. Finally, in terns of seleciivity. thiosulfare the leaching agent investigaredin rhis siudy have showeda geat potentialin selectivilyrecoveryof silver from selected semicondrctor waste-At the selected leachingconditions, almostcompietedissolution of silveris achievedwifi a selecrivityof 368.5overothermerals.This a grcatimprovemeni over the acid and chiorideleacLingmediumFevious investigaredby Tang( I 999). ACKNOWLEDGEMENTS A graieful acknov/iedgemenito the MinisLj, of Science,Technology & Environment of Malaysia for providing financial suppot through the IRPA gmnr and rhe Universiti Teknologi Malaysia for the ResearchFellowshipawardedro Mr. L. K. Meng. REFERENCES Abbnrzzese, C., Fomari,P.,Massidda, R., Veglo,F. andUbaldini,S. (i995). "Thiosllfate Leachingfor GoldHydromeiallurgy." Hydrometallugy,39 . 265-276. Aylmore, M. G. (2001)- "Treatment of a refraciory Cold-copperSulfid€ Concenrrareby CopperAmmoniacalThiosulfate Leaching."MineralsEngineering, 146(6),645-637. Aylmorc,M. 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(20C1)."Kinetic Aspectsof cold and Sitver and Silver teaching in Ammo a-Thiosulfa.e Soluiion. " Hydrometailurgy, 60.7-16. Kerley,JI., BemardJ. (1983)."RecoveryofpreciousMetalsfrom DiftuculrOres..'(U.S. P^refi 4, 269, 622). Massey.A. G., Jobnson. B. F- c., Thompson, N. R. analdavis,R_(i9?3). ..rhe Ch€misrry ofcopper,Silverandcold." 1'red.C. Britain,Pergamon hess.,79-119. Tang, B. S. (1999)."SelectiveSilver Removalfrom SelecredS€miconductor Waste." UniversitiTeloologiMalaysia:MasierThesis. ..cold Recovery Thomas,K. C., Fleming,C.,X{archbank, A.R. andDreisinecr,D. (1998)_ liom rcftactory Ca$onaceousOresby PressureOxidadon.Thiosulfareteachingandr€sinin-pulpAdsorprion."(U. S.Patenr5,785,?36). 5-t75