The role of electrochemistry in the extraction of gold

The role of electrochemistry in the extraction of gold

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j.-Eieccioo;;or;-Chern,;~~~ &Y+&~-~&~. ._.-

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.- Elsevier S&uoia SiA., Lai&nne Y Printed.in The NethMands

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THE.ROLE

OF ELECTROCHEMISTRv; IN THE EXTRACTION . . .

. R-L.

*

:

~..

OF-GOLD

PAUL

Council

for

#ineral

Technology,

Private

Bag X3015,

Randburg

2125

(South

Africa)

ABSTRACT The flow sheet for the recovery of gold from an ore consists of several unit opet-ati on5 , of which a high percentage are based upon electrochemical principles. The unit operations are discussed in this paper to illustrate the diverse role played by electrochemistry in the overall recovery process. The discussion is based,upon the results of recent research carried out at the Counci 1 for Mineral Technology (Xintek) _

INTROIIUCTICN

sheet for a ‘conventional ’ gold plant consists of crushing and of the ore, followed by cyanidation, filtration, and recovery of gold

The flow

milling

by cementation

onto

large cyanided _ To reduce many gold existing is

operating

producers unit

costs

while

of

gold can

increasing

the

of

occluded

, which

process

roasting

without

permits

the

In view of of

gold

interest are

that,

clearly

cementation, trochemical

(viz.

these from of

recent the eight

identifiable

as having

though

material

different

and electrowinning). basis,

this

unit

A fourth is

0022-0728/84/$03.00

the role

of

is

flow

operations

perceived,

techniques

electrochemistry

0 1984 Elsevier Sequoia S.A.

basis

for

in hematite of

has had

and slimes sheet

for 1.

depicted

flotation)

(viz.,

not generally

recovery

shown in Fig.

an electrochemical

, CIY) makes. use of- electrochemical

optimization. In this paper,

a ‘typical’

developments,

some pyritic,feed

the ore_

lost to

filtration,

such as calcines a major impact on the processing of pulps, which are not easily filtered_ treatment of dump material, tion

of

pyrite

the

for

need

gold,

flotation

content

the

~-to

is

of

(and thus

of

used

or replaced

The use of (FeS2)

the pyrite

(CIP)

pulp

steps

techniques. the pyritic

within

is

the pulp recovery

processing

by

leached

separation

before

the overall

additional

be liberated

The carbon-in-pulp from

gravity

by milling

by newly developed

processes)

gold

some plants,

liberated

common in recovery

particles

dissolved

In

have introduced

fairly

conventional

(Fe203).

dust_

of gold

operations

therefore

Microscopic

zinc

particles

recover

It

the

the extracis

in Fig.

(viz.,

from

of 1,

three

cyanidation.

also.

has an elec-

whereas. a fifth. process

in the extraction

control of

gold

i

and. is

dis-

...

148 cussed

in terms

of recent

of both

the

schematic

flow

sheet shown in Fig.

1 and .the

results

research conducted at the Council for Mineral Technology (Man&k).

Au Fig. 1.

A 'typiealt fiaw

sheet far the reesvery 6f gsld.

PhCifAflBN8F PYRITE The @arl;it%&deeumanixd prae@oo f6r the s@parat46n 6F minerals by s@l@et;tve appears t6 be a pat@nt fil@d by B@ssel and B@ssal fn i877 [I]. fn

flstatien

&hi5 preeasg, graphdta partlalas w@r@ flaafod fram the gangue matrix by the additI6n 6f 641 t6 tha gulp, which ws

then beiled. hater werk@rs appaared t6

cbneentrate 6~ imprevfng the methed fer g@n@rating gas withIn the pulp; t@eh= nlques roqu+rlng the add;i%fer, ef earbenatae and aelds, the applIeatt@n of rsdue@d pr@s~ur@~, and @WI

fh@ @f@e&~fy~~s @f wat@r, a11 m@t wjth varying

d@gr@@s 6f ~uee@f~. CIad@rnflotatjon ealla ut~l~x@ a aubm@rg@d lmpellar to guek air down chann@l~ ;Inthe shaft, Thfr air am@rgesas a flno eurtalnaf

bubblesfram staf@gIeally plae@d ordf;ie@eereund tha imp@ll@r, 1~ lat@r y@ars, Plotallon r@s@areh has eaneentratad 6~ th@ @r-genier@agents (@all@d 'eelleetors')that ar@ requtrad to Interaeg a@l@ef~v@ly with th@ sur= Pac@s of th@ partIel@e t@ ba #l@at@d, Thle interestlan r@nd@ra th@ ~urfae~ ef th@ d@slr@d partfef@s hydropheble, and this faeilltat@e bubble attachment and

fletatien, In 1%3,

%alaw and Nlxen [2] prapes@d that *ha ehamleal #areas

aetlng b@tw@@nth@ surfaea and the eel'taeterw@r@ @l@etr@eh@mleal In @rIgIn, a prepesal that app@ar% te hav@ w@n general aecepfanee f&5] by wsrkars In fhls fjold.

eell@etoremest ssnnnenly utiadin tha flotatfon of pyrlta in n@utrel te mltdly alkellnepulps [6] ar@ tha xanthates(typIeal'iy,!a@-prepyl and s@c= The

butyl xanthatas). A'lllsens8 aZ, [P] measurad tha open-elreult potentials of sevaralmetal sulphidas in th@ presort@@of potassdum @thy1 xanthate (6.2% x

:’

19%)

ata

pH value

and pyrrhotite the

.exhibited

which, all

to the reversible

dixanthogen 2EtOCS;

potential

in-the

in this of 0.13

te -(FeAsS) ; chal copyri to paper

range-of are

V calculated

0.14

quoted), for

(CuFeS2) -

to 0.22.V which

the ethyl

.(u,s

are xanthate-

:

+ Ze-

(1)

dixanthogen

(att potentials in this i.e.

potentials

potentials

couple (E' = -0.06-V);

+ (EtOCS2)2

xanthate

arsenopyri

of 7..Pyrite,‘

-(Fe+*)

HljE, against

anodic

.1&a

paper

have signs

Ox + ne- + R, irrespective

consistent

with

reduction

reactions,

of the manner with which the reactions are

displayed in-the text). Bornite (Cu5FeS4) and galena (PbS)

displayed

open-

circuit potentials of 0.06 V that are cathodic tc the xanthate-dixanthogen redex petent~al. Analysis

of

the chemical campounds present cn the mineral

surfaces revealed the presence of dIxanthagen on the first group of four sulphides, whereas metal xanthate was detected on the surface of the miinerals in the second group. formation of the metal vanthatas can cccur via the react$on

although reactions producing oxfdized sulphur apec'ies(such as S,&‘, S40t-, etc.) are also feasible, Evidence supparttng reactions s=Imitarto (2), in pr@faranee to the simple Ian=axchange displacement reactIon

of dlsselved oxygen [S], i.e., the cathodic current ex&Pn (4) 4s requ4~ad

te suste-inthe anedje

current ee ranetlan (1) or (2). Woods [8]

studded the eleetreehem~eal eharaefar~st~ea oQ galena and noble-metal ala+ Wades

!n tka presanea of ethyl xanthata, and eencludad that the ehamiserptisn

oP xentheta i,a,,

occurs en the gelene surface at the open-circuit potential. Zn aeidle pulps (#.g, those obtalned in the treatment of material from slimes,

160

dams or of leach residues from uranium plants), co77ectors such as diethyl dithiophoophate (3TP) or mecaptobenzothiozole (IIBTjare commonly used 161. and Finkelstein [3] identified the products of reaction between.a number of sulphide minerals and 3TP as well as MBT. The dithiolates (DTP)2 and (MDT)2 Cioold

were positively identified as being present on the surface of pyrite, although the ferric salt of MBT, Fe(MBT)3 , was also found to be present. In both instances, the open-circuit potentials of a pyrite electrode in the presence of thiols (100 mg 7-l) was 'anodic to the reversible potentials calculated for the reactions: Eco, += %/Et+ P Etd 'S-S' 'OEt

2e___,2 E?/

(OTW 2

IMBT)

EtO' 'SDTP-

EO-0.25 V

MBT-

2

Fuerstenau et al. [lOI agreed that (0TP)g is the major product formed on pyrite surfaces in the presence of DTP, whereas Yitrofanov and Kusnikova [ll] favoured the insoluble metal dithiophosphate. The weakness in the research described above is that there is no certainty that the identification of a product adsorbed onto the mineral surface proves that flotation is indu.ced by that particular chemical compound. A recent study at Mintek 1121 of the electrochemical

behaviour of platinum, gold, and pyrite

electrodes in the presence of OTP and MBT made significant progress in identification of the possible surface products involved in the flotation of pyrite, though, at this stage, the results cannot be regarded as conclusive. Cyclic voltammograms

illustrating the i-E

response of a platinum eleitrode

(electrolyte NaCIOq at 0.1 M and pH 5) in the presence of DTP (50 mg 1

, i.e.,

2.23 x ?o-4 M, added as the potassium salt, KDTP), and in its absence, are shown in

Fig. 2. From the evolution of hydrogen in an anodic direction, the presence

of DIP is seen to inhibit the small current peaks associated with the desorption of hydrogen. The heights of the well-defined peak at -0.15 V and the poorly defined shoulder at about 0.15 V in the presence of DTP are linearly related to the potential sweep rate, indicating the possible adsorption of DTP anions. -2 measured at 0.1 V in the Interfacial capacitance values of 38 and 60 PF cm presence of OTP. and in its absence, provide confirmatory evidence supporting the adsorption of DTP. Also shown in Fig. 2 are contact angles measured on a platinum electrode held at

various

potentials

in

the presence of DTP. Contact angles greater than 20’

---

Pt

Pt t OTP-

I

0.05 rnAcia-3

i /

E/V I

-0.8

V

0

-

*o

e 0

l

e

0

e

1 40

.*

l l

0

20

Fig. 2. Cyclic voltamnograms (10 mV s-l) and contact angle measurements for Pt electrod in NaC104 (0.1 M) at a pH va'lue of 5 in the presence of DTP (2.23 x 10Bz M) and in its absence.

a

(indicating that the platinum surface is becoming hydrophobic) are obtained at potentials anodic to about 0.1 V. Because this'potential is cathodic to the equilibrium potential of the (DTP)2-DTP- reaction (0.47 V for DTP at 2.23 x 10W4 M), the results demonstrate

that species other than (DTP)2 can induce hydro-

phobicity on a platinum surface. Xn view of the results presented above, it is suggested that adsorbed OTP anions are responsible for the increased contact angle at these low potentials. The contact angle increases rapidly with increasing potential, reaching a maximum value of 57' at 0.83 V. If the potential is held at this value for some hours, the surface becomes covered with an oily film, thought to be the dithiolate (DTP)2. Chandler and Fuerstenau salt, platinum-DTP,

1131 suggested that the ins@luble platinum

is formed in this potential region. If the potential is-

increased beyond 0.83 V, a steady decrease in the contact angle is observed. In _

the region of oxygen evolution, the surface of the electrode is once again

hydrophilic. This decrease in the contact angle is cdnsidered to be due to oxidation of the dithiolate to.form further oxidation products, because

a

platinum electrode held for extended periods at potentials above 1.0 V does not

appear to generate the oily film of (OTP)3 that is observed at lower potentials. Attempts to study.the electrochemical

behaviour of DTP on pyrite electrodes

were frustrated by the high background-current& of-this mineral (due to oxidation and reduction of the pyrite) in relation to the low currents associated with the collector. Several microflotation

studies were therefore carried out so

_.

.-

:

152.

:

that the data generated actual

flotation

with several

electrodes

correlation.

by the use of platinum.electrodes

practice_

A Partridge

(platinum

of the efficiency

could-be

and Smith microflotition

of flotation

with some. electrochemical of each float

or oxygen as the carrier

air

various

(such as Na2S, KCN, or Na2S03) to alter were ontained

gas,

could

use of nitrogen, reagents

to

vtas .fitted

as tie11 as pyrite electrodes were.used) for

of the flotation system. The conditions

the pulp. Samples of pyrite

related

cell

be altered

or by the addition

property by the of

the redox- Potential

of

from Custer in South Dakota via Gfard’s

Natural Science

Establishment , Inc. , and from the Durban Roodepoort Beep (DRD) Gold Mine in South Africa. The samples were screened to a particle size between 106 and 36 Pm, and were tested for total floatability with amyl xanthate. Values of 94 and 90 % were obtained for the Custer and DRD pyrite, respectively. All flotation tests were conducted on 2 g of sample in DTP (2.23

The extent tial

of flotation

of the pyrite

electrode

appears

to correlate

reasonably

made from Custer pyrite

x 10v4 14) at ptl 5.

well

(Fig.

3).

with the potenBoth pyrite

samples exhibit increasing flotation recoveries with increasing potential, though the Custer pyrite is inherently more floatable than the JRD material. Although the potentials at which flotation occurs are cathodic to the reversible potential

of the (DTP)2-DTP- couple

enough for

formation

(0.47

of the dithiolate

V),

the difference

to be discounted.

is not large

Furthermore,

when

several large and seemingly homogeneous samples of Custer pyrite were crushed to a particle size of about 1 mm, the individual particle potentials (measured with

a small

platinum

values as large

probe

with

a pointed

tip)

were found

to

have a spread

of

as 150 mV. The average potential for 30 such particles in an

oxygen-purged electrolyte was 0.53 V. and only two particles failed to attain potentials higher than 0 -47 V. If it is assumed that a17 particles exhibiting potentials anodic to the (DTP)2-DTP- equilibrium potential will float, a flotation

recovery

of 93 % can be predicted.

This predicted

value is to be expected

from the results in Fig. 3, if it is borne in mind that the total floatability of the Custer pyrite (as measured with amyl xanthate) was 94 %. This experiment was repeated

in a nitrogen-purged

of 0.42 V and a predicted flotation the range 80 to 90 % were obtained

electrolyte-,

and yielded

an average

potential

recovery of only 7 %. However, values experimentally (Fig. 3).

in

The conclusion to be derived from these results is that good floats can be obtained even when the potentials of the individual particles in the pulp are

cathodic

to the equilibrium

potential

of the (DTP)2-DTP- couple.

This floata-

bility is attributed to the presence of adsorbed DTP anions, which apljear to be capable of inducing contact angles of 20’ to 30’ (Fig. 2). The positive identification of (DTP)2 on the surface of floated pyrite reported~by Goold and Finkelstein

191 could

arise

from the fraction

of all

pyrite

particles

that had

-.

-:.

153. '. _ioo_ : -. m

:

l

Extent of flotation of surface potential

potentials

sufficiently

problem can provide the more classical

0.44

Custer and Durban ?oodepoort Deep pyrites (collector 2.23 x 10-4 M DTP).

of

anodic for the oxidation

flotation of the bulk of the material DTP anions. Although there field of flotation,

0.42

0.40 0.38 Potential/V.

0.36

0.34

Fig. 3. function

:-

Custer Pyrite Durban Oeep Pyrite

of DTP to occur.

is attributed

as a

However,

to the presence

of adsorbed

is clearly much mdre fundamental research required in the it is apparent that anelectrochemical approach to the an insight

into

the phenomenon of flotation

that complements

approach.

CYANIDATION OF GOLD The leaching

of gold by oxygen in the presence

of cyanide proceeds

via the

reacti on 4Au -i- o2 + SCN- + 2H20 +

4Au(CN); + 40H-

(6:

although it is still uncertain whether the reduction of oxygen stops at hydrogen peroxide [14]. Because of

efficiencies South Africa

cal cined

the difficulty involved in the achievement of high is leached from pyrite (a problem that Was recognized -in over 80 years ago [15]), it is comnon practice ~for the pyrite to be

when gold (producing

hematite ; Fe20B , which is subsequently-subjected

or for the pyrite to be milled to a very fine particle tion), dation; The poor leaching characteristics of gold from pyrite attributed to one or more of the following factors:

(ij

.-the presence ‘trapped milling

of very fine

within

the.larger

to liberate

size

to cyanidabefore

parti cl es of gold, -which are occluded Pyrite

the gold;

particl&.necessitating 1

cyani-

are generally

fine

or

_

164_. ... (ii)

:

..

.’

reduction.

present

(iv)

sulphide

aeration

is interesting,

of free

which- -ii u&ally

cyanide

due to the~formation

of

and.

of sulphide

ions (a particularly effective poison in into the pulp, above are trivial, since they can be eliminated-merely

and the addition because

of sufficient

the practical

addition

of lead

(usual ly in the form of

leaching

vessels

[17].

cementation

pyrrhotite~,

1

and ferri-cyanides;

the liberation

(iv)

(particularly

in the concentration

cyanidation [I6]) Points (ii) and (iii) by adequate

minerals

with pyrite);

reduction ferro-

.

in .the ckmcentrtition .oi -oxygen. in the -pulp due to ~&idat>on

-of- the iron (iii)

.-_

This effect

of gold onto zinc

cyanide

solution

Point

to the problem involves

lead nitrate

is discussed

to the pulp.

or li tharge,

later

in relation

the.

PbO) to the

to the

dust.

By far

the most interesting problem is that of the occlusion of gold within necessitating either fine milling or calcination. The the pyrite particles) question arises as to whether the problem is totally physical in nature (as it involvement_ Evidence appears to be), or whether there is some electrochemical that strongly supports the role of electrochemistry was recently presented by Filmer [181. In Fig. 4, the i-E curve

(as measured in this

laboratory)

is shown for

oxida-

tion lyte

of a gold rotating-disc (500 rpm) electrode in a nitrogen-purged electroof 0.01, 0 -02. and 2 x containing NaOH, NaCN, and Pbzt at concentrations Also shown are the curves for the reduction of oxygen on IO-5 M, respectively_ the same gold electrode and on a pyrite rotating-disc electrode (air-saturated electrolyte gold will

containing corrode

0.01 M NaOH). It is clear

spontaneously

in an aerated

from these

5-L” curves

al kal ine cyanide

solution

that at a

mixed potential of approximately -0.41 V and at a rate (limited by the mass transport of oxygen to the electrode surface) of about 30 PA (approximately 0.4 mA cmm2). Although for

the reduction

measured currents

the current

density

(which is

of oxygen on the pyrite

electrode

are considerably

because

higher

limited is also

this

by mass tpnsport) 0.4 mA cm

, the

electrode

has a much cm2). Since the

larger surface area (0.58 cm2) than the gold electrode (0.071 peak current (at -0.28 V) for the oxidation of gold (0.23 mA) is lower than that for the reduction of oxygen on pyrite (-0.25 mA at -0.28 V), short-circuiting

of the INO electrodes

should

result

in immediate passivation

of the

gold electrode. When the experiment was carried out, the open-circuit potential of the paired electrode increased to a value of 0.01 V in a matter of seconds. At this potential , the corrosion rate of the gold electrode is only 4 PA (approximately 0.06 mA cmq2). The practical implication-of any gold particle embedded in the surface of a much larger

this result is that pyrite particle, .but

of gold and Current-potential curves (1 mV S-l) for the oxidation Fig. 4. (Gold surface area 0 -071 cm2 ; reduction of oxygen on gold and pyrite electrodes. FeS2 surface area 0.58 cm*_) nevertheless exposed retarded rate.

to oxygen and cyanide,

wi 11 be leached

at a -greatly

Experimental results supporting the above electrochemical interpretation were reported by Filmer [18] . In a 24-h leach, the extraction of gold from milled pyrite (with a BET surface area of 0.3 m2 g-l) was 17 %, compared with 82 % from the calcine (with a surface area of 3.0 m2 g-l) produced by roasting of the pyrite. Extension of the leaching period to 21 days increased the recovery of gold from the pyrite (28 %) , but had no effect upon the calcine-. However, partial reduction (by hydrogen at 7OO’C) of’ the calcine to yield some magnetite reduced the -extractibn of gold (in (FegD4), which is an electronic conductor, a 24-h.leach) from 82 to 60 %, though no change in the surface area was observed. These results indicate the beneficial effects of roasting of the pyrite to liberate occluded.gold, as well as the retarding effects of large surface areas for

the reduction

of oxygen on the rate .at which gold

CARBON-IN-PULPPROCESSFOR GOLDRECOVERY In a conventional gold plant, a significant

is leached.

percentage

and 1 %) of the go1.d dissolved during the cyanidation the filtration stage that yields a clarified solution

(varying

6etween 0.2

process is ‘lost’ during for the -cementation step.

This loss arises .because of the large tonnage treated (a typical plant processes 200 OODt of ore per month) and a constraint on the amount of water that can be used to wash t.he ioluble gold from the filter cake. This problem is exacerbated by the difficulty the retreatment of their

with which. certain materials (such ascalcines and. slimes from of old dumps) are f i 1tered and washed, owing ‘to the small size

particles.

.:&+:

--2.

., -. -, ..-. ..~:

-;-

y,‘:.

._. In .the. CI?_process

;19,20]

.r ._:;::.:- __._ -:,:.. ;;;.::.._. . .. .: -.. .:_ :.

i the entirefiltration

,tep

js

:

.,-

ei<.mfnat&~.by:

the-..

’ -___ ._ : is .added to the l&t_ tank (usually -referred to as a. ‘stage’) in a-‘series of .. ‘~. absorption stages (typically four to six stages are-used). .The pulp, containing.

addition.

of granules

dissolved all

gold;

the

of activated.carbontol’the

is pumped into at a ‘flow

stages

in each stage.

Screens

the first

rate designed

on the

peripheries

cyanidation:pulp’.

stage , and flows

The carbon

under gravity

through.

to permit a residence. time of about i-h of the tanks restrain the.carbon.

granules within each tank while permitting .the pulp to flow to the next stage. At regular intervals, a percentage of the pulp and the carbon in the nth stage is

pumped back to the

A certain

(n-1)th

stage,

thus maintaining

a carbon

flow that is

each stage

is adsorbed

to the overall flow of the pulp.

counter-current

percentage

of the soluble

gold entering

onto the carbon. If six stages are used, and 70 % of the dissolved aurocyanide ions are adsorbed onto the carbon in each stage, an overall recovery higher than

99.9

eluted ratures

The loaded carbon emerging from the first

% fs attained.

stage

is

[Zl] by treatment with a solution of NaOHand NaCNat elevated tempe, and the gold is finally recovered by electrowinning [ZZ]. The eluted

carbon is reactivated for 2 to 3 min, after

by being heated to about 700 ‘C in the presence of steam which it is returned to the last stage of the absorption

circuit. To optimize operation developed a mathematical various

operational

of the adsorption circuit, Fleming et aZ. (231 model for the process, which relates the effects

parameters

(such as the flow rates

of

of the Pulp and the

carbon, and the mass of carbon in each stage) to the efficiency of adsorption. One of the interesting conclusions to emerge from this study was that each stage should contain

equal. masses of carbon.

However,

for

various

reasons

(such

as

surges

in the flow rate of the pulp, blocked screens, etc.), large fluctuations in the carbon concentrations in each stage are frequent. A typical variation in

the carbon concentration in the last stage of a South African CIP plant is shown in Fig. 5. The data points were obtained by weighing of the carbon obtained in a IO-litre

‘grab sample’

of pulp from the adsorption

tank.

Also shown in Fig. 5 is a continuous curve of the carbon concentration as determined by an electronic ‘carbon meter’ [24]. This instrument, which is still under development to-date

at Mintek,

measurements

provides

the

of the concentration

plant

operatorwith

of carbon

into

and generally

the pulp,

and carbon particles

have surface

die to the potential the open-circuit to 5 mV in height.

potentials

of the probe)

potential

that

strike

of the electrode,

earthed. The probe

(which are electrically are

and up-

in each stage. The measuring

probe consists of two metal electrodes, one of which is

inserted

accurate

several

the indicator producing

hundred

millivolts

electrode. small

is conducting

voltage

catho;

This affects pulses

1

The pulses are amplified and counted if they are above the

5. Comparison between the measurements obtained manually and by the Mintek carbon meter of the carbon concentration in a CIP absorption tank.

Fig.

random, backgrcund

noise

level . The recorder curve shown in Fig. 5 is the output from an electronic ratemeter, i .e., a voltage that is proportional to the rate at which pulses are detected. This, in turn, is proportional to the concentration of carbon in the pulp. Perhaps even more important than maintenance of the correct concentration of carbon in each stage is the activity of the carbon that is returned to the adsorption circuit. If the eluated carbon has not been sufficiently reactivated thermally, the capacity and the kinetics of the adsorption process are affected_ The activity of the carbon can be determined in the laboratory as follows. A known mass of carbon is added to a-stirred beaker containing gold (as potassium aurocyanide) at a concentration of 100 mg 1-l , and the decrease. in the concentration of gold with time as it-is adsorbed by the carbon is monitored. However, this

technique

is labour-intensive

using an_ atomic-absorption gold

in alkaline

cyanide

and requires

spectrophotometer. electrolytes

is readily

capable

the analysis

accomplished

of

of

by anodic-strip-

is well

ping vol tammetry ) and this

technique

processor-based

is currently

instrument

a skilled.dperator In contrast.

suited to.automation. A microbeing tested at :?intek. Once activated,

the instrument continuously measures the.gold concentration during its adsorption onto the~carbon, each data point (i.e., concentration US time of. measurement) being automatically plotted on an X-Y recorder. Apart from the-addition of the test solution to .the stirred beak~er?, no further .attention- is required from the operator, and a complete the end of the. test. :

carbon-adsorption .: -’ ._ . .

profile

is available

at -.

-_

l$s

ELE&JwINNINGOF &jLD.

:

‘~

-The ele&rowinning-of

,,: ..

-

_’

gold

-_

:

has become ‘a- familiar

unjf

-’

-.

._

--. ::-

operation

-.

._..

:’

in~,South :~:.‘.‘_

African gold mink, the technique being -used in the treatment of GIP eluates and of .leach liquors resulting from intensive -cyanidati’oh [25] _’ These two-. ‘1 -.. -1 .types of electrolytes contain gold 1;: the concentrationrange 100. to .lOOO’mg after el ectrowinning _ An interesting. before electrolysis, and 5 to 10 mg new development

[26]

is the elution,

and simultaneous-

recovery

by eleitrowin-

resins that have. been used .in the ning, of gold from poisoned anion-exchange extraction of uranium. In this process, the eluate (acidic thiourea or.neutral ammonium thiocyanate) is circulated from a tank containing-the resin through the electrowinning cell and back to the tank. As the eluted gold is recovered during the elution procedure, the concentration of gold entering t&cell -1 rarely rises above 10 mg 1 . Even at these low concentrations. use of the Mintek packed-bed electrowinning cell [22] results in recoveries of 50 to 70 % of the gold in the eluate per pass through the celll?t -1 O-4 m min (i.e., a volume flow rate of 200 1 min ). CEMENTATION OF GOLD .The recovery of metallic

gold

by cementation

a linear

onto zinc

flow

rate

of

dust is an electro-.

chemical process [27] involving the oxidation of zinc and the reduction of aurocyanide ions. The overall stoichiometry of the process is as follows: Zn f 2Au(CN)i

+

Zn(CN)i

-e

(7)

~Au

Pregnant solution from the filter plant (typically containing 5 to 10 mg of dissolved gold per litre) is usually stored in a surge tank before being pumped via a Crowe tower (for de-aeration) into an emulsifier tank, where lead nitrate and zinc

dust

(of

particle

size

between 110 and 70 pm) are added.

After

a

mixture is pumped residence time no longer than 1 or 2 min, the solid-liquid into a Stellar or a Merrill filter unit. The zinc dust forms a continuous bed of reducing

agent

on the

filter

medium through

which

the

pregnant.

solution

must

flow. Owing to the cathodic potential of the zinc (typically -1-l V , which causes the rate of go?d deposition to be 1 imited by the mass transfer of aurocyanide

ions to the surface

namic conditions’within

the

very high, barren solutions usually being obtained. Poor cementation following (i)

of the zinc bed,

particles)

the efficiency

of the cementation

with a gold content

efficiencies

can usually

and the excellent

hydrodyprocess -1

is

lower than 0.01 mg 1

be attributed

to one of the

effects: inefficient

de-aeration;;

to the reduction

resulting

of oxygen;

in excessive

corrosion

of zinc

due

1 ._. ~-___;: :.~I;

,,

:

-._ ._I .; ,i;;,_.. -, (iii)

-._

y..’

.- -:.

_

1:.

_

-.

._ :..

__.._ ,_..-.,:

;

‘.

-_I_

-

~.

:

_.

. .

._

__,i.

.

-.

..

:

:..

..-. ... _

_ -ticin .hydrbxide; Ghiih . . . .of.iinc .;.. passivates . . the-anodit.dissolution-of ~_ _‘::zinc’, and__, .’ -.. ‘1. .I. _ :‘;I 2: ._‘ _-:_.:‘-:‘ .:. 1..the: p&.&e

of::poisons-;-

-.‘.whi&i are reported’&

.-

::

..

159 ,. .. ._ .- _: _._ : .:~ ,_ :. ; .-. ;:‘-:-::.-:._:: ..; -;- ::-. ‘--.f_;.._ _- ,-; .’ -: :_:. :__. ” pregnant-solution; resulting---in the forma-. ~.. ‘.;I- insufficient..-cyanide:*:!.n-;:the ‘_ _,:

.. -. cy at concentrations .During.recent pilot-plant

such as sulphide

h&e .a deleterious

ions-, in _the pregnant solution, -effect-

on cementation

-as 1ow as. 0.03 mg 1-I [14]. testwork at Mintek on the cyanidation

efficien-

and .subse-

quent cementation of gold from the clarified. leach liquor, the control experiment (which duplicated the procedure used on the gold plant from which the milled ore was obtained) yielded extremely poor cementation results (barren solutions .of ._0.5 mg 1-1 from a head-value of 5 mg 1-l). However, additional cementation tests performed several tailings of less .than 0.002 mg 1-l.

days later

on the same leach liquor

yielded

Close inspection of the gold‘plant revealed that the clarified leach liquor from the filter plant is stored in a 1200 m3 surge tank before being pumped to the Merrill tion

filters

in this

for

cementation.

tank is approximately

The average

residence

1 h. A concentrated

time

solution

for

the

solu-

of lead nitrate

-is continuously pumped into the surge tank to give a concentration lead of about 5 mg 1-I.- Additional lead nitrate is added directly -1 2+ .. emulsifiers to raise the Pb valueto8mgl

of dissolved to the

During leaching of a further 400 kg of pulp at Mintek, a sample of the pregnant solution was subjected to cementation immediately after the addition of Pb2+ at- a concentration of 8 mg 1 -1 _ Lead nitrate was added to a second sample of 5 mg 1-l) which was of the pregnant solution (to give a Pb2+ concentration aerated resulting

for

2 h. Further Pb2+ at a concentration

solution

cementation

yielded

Although the results sulphide

ions,

of 3 mg 1-l was added, and the

was pumped through the cementation barren solutions

cell _ The two tests

of 0.2 and 0.002 mg .1-I,

appeared to point

to the presence

in the pregnant electrolyte

on

respectively.

of a poison,

,- which is subsequently

such as oxidized

on

contact with atmospheric oxygen, confirmatory evidence was not easily obtained owing to the difficulty involved in‘the analysis of sulphide ions in solutions containing cyanide ions. Nevertheless, this investigation led to a study of the rate of oxidation of sulphide ions in an air-sparged electrolyte containing NaOH(0 .OI M) and S2- (50 mg 1-l). (A sulphide ion-selective electrode was used since

no cyanide

ions were present.)

The rate of oxidation-of

sulphide

ions was

found to be very slow in the absence of dissolved lead, no measurable drop in the concentration of-sulphide being observed over a 3-h period. However, the -1 -addition of Pb2? at a concentration of 4 mg 1 considerably enhanced the rate of oxidation;

the concentration

over the 3-h period. 1-I is theoretically

of sulphide

ions declined

(It should be noted that Pb? capable

of precipitating

from 50 to 2 mg l-1.

at a.concentration of 4-mg only 0.6 mg -1-l iof 52- as PbS.)

..:-... ‘160. ~: :

_

_:

_.

Similar

effects

were -noted with Cupric,

The .insoluble. electronic solids

metal sulphides

Conductors.

on the rate

1 g of coppe;

It

powder (BF-surface

and ..ferrous

_.

ions-.. --:.

of all, the .metal ions discu&ed

was therefore

of sulphide

ferric

. .

oxidation

.decided

thatthe

should-be

above. are good

effects-

area 0;19 m2 g-l)

to 1 1itre

.. 1

of various

measured...The

addition

of

of 0.01~ M NaOH

to below 0.1 mg containing S - (58 mg 1 ) reduced the sulphide concentration 1-I in approximately.15 min, whereas-l g of natural galena and pyrite (surface required approximately 50 min to areas of 9.67 and 0.54.1s~ g-l. respectively) effect a similar reduction. Chalcopyrite (surface.area. 0.58 m* g-l)- decreased -1 the rulphide concentration from 50 to 20 mg 1 in 3 h. In Fig. 6, the current-potential .curves (10 mV s-I) are shown for the oxidation of S2- (50 mg 1-l) in nitrogen-purged 0.01 M NaOHirith rotating-disc electrodes (500 rpm) fabricated from the minerals potentials recorded for the copper electrodes 2cu + s*-

mentioned above. The very negative are due to the reaction

-+ Cu2S f 2e-

(3)

2which has an equiliirium potential of -0.83 V in an electrolyte with an S content of 50 mg l-I_ The overpotentials for the oxidation of sulphide ion (the equilibrium potential for the S-S*- couple is -0.43 V) increase in the order

PbS c FeS2 c

CuFeS2.

Also shotin in Fig.

of oxygen (as well

6 are the corresponding

as reduction

cathodic

of the mineral

curves

for

in some instances)

sparged electrolyte of O.OL M NaOH. The overpotentials FeS2 c Cu -Z PbS -= CuFeS2. Xand [28] also found pyrite

the reduction from an air-

increase in the order to possess the greatest

activity for the-reduction of oxygen, though he reported chalcopyrite to be more active than galena. Combination of the various anodic and cathodic processes give the electroihemical cm

-2

rates

for the reaction of sulphide as 0.66, 0.11, 0.070 and 0.014 mA

for the Cu, FeS2, PbS and CuFeS2 eTectrodes, respectively. These rates

follow the same order as that observed for the experiments in which 1 g samples of the powdered minerals were used. The implication of these results is that the homogeneous rate of sulphide oxidation by oxygen is very slow, and that the heterogeneous rate at the surface of an electronic conductor is considerably faster. The addition of lead nitrate in gold

plants where there is a sulphide problem results in the of lead sulphide, which acts as a site for the reduction of oxygen and the,oxidation of sulphide ions. Furthermore, the presence of a precipitation

surge tank for storage of the pregnant solution from the filter plant provides sufficient residence time for oxidation of the residual su_lphide ions. The common practice

of 1i tharge or lead nitrate.

addition

to the leaching

vessels

Anodic and cathodic i-E curves for the oxidation of sulphide ions and the reduction of. oxygen in -0 .Ol :J NaOHwith copoer , galena , pyrite , and chalcopyrite rotating electrodes (500 rpm, 10 mV s-1).

Fig. 6.

when sulphidic i.e.,

ores

acceleration

are

being

of the

rate

treated

undoubtedly

at-which

sulphide

serves is

the

same purpose,

oxidized.

CONCLUSIONS

There is little doubt that the evidence clearly justifies the statement that the recovery of gold is predominantly an eiectrochemical process. In addition to -and cementation, electrochemisits obvious role in iryanidation. electrowinning, try plays a far more subtle part in other.operakions

CIP process. Although metallurgy

is ersentia7ly

an applied

such as flotation

practice,

and the

the application

of

theoretical -electrochemical principles to the subject has facilitated the optimization of many of the process stages. Further developments and improvements can be expected in this field as a better of the -various operations is developed.

understanding

of the electrochemistry

ACKNWLEOGEMENT

This paper is published

by permission

of the Council

for Yineral Technology.

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4 5

Institution of Mining and Metallurgy,, London, 1953, pp_ 503-516. S.X. Ahmed, in N.Li. Norman (Ed-), Recent Developments in Separation Science. Vol. .V, CRC Press, Cleveland, 1972, pp. 95-133. R. Woods, in M.C. Fuerstenau (Ed.). Flotation, A.M. Gaudin Memorial Volume,_-Vol. 1, AIME, New York, 1976; pp. 298-333.

G-W. Poling._in

M.C.

Fuerstenau

(Ed.),

Flotation,

A.M. Gaydin Memorial

162

_.

,.

Volume, Vol. 1,. AIME New. York 1976. pp. 334-363.. -, Vacation School , Johannesburg, P.-J. Lloyd, in Principles of &a .Flo&ition, 1978, University of the Witwatersrand, Johannesburg, 1978, pp. 57-107. 1-A. Goold, N.J. Nicol, and A..Granville, Metall. Trans., 7 S.A. Allison, 3 (1972) 2613-2618. 354-362.’ 8 R_ Woods, J. Phys. Chem., 75 (1971) Report 1439, National Institute for 9 L.A_ Goold and N-.P.Finkelstein, Metal 1urgy , Johannesburg, (1972). J .L. Huiatt, and M.C. Kuhn, Trans. Metal1 . Sot. AIME, 10 M.C. Fuerstenau, 250 (1971) 227~231. Mitrofanov and V.G. Kusnikova, in Svenska Gruvfareningen and 11 S.I. Jernkontoret (Eds.), Progress in :4ineral Dressing, Transactions; 4th 1957, Almqvist and International :4i neral Processing Congress i Stockholm, Wiksel l , Stockholm, 1958, pp. 461-473. at MINTEK 50, Sandton, 1984. i2 D. Groot, Paper presented J. Electroanal . Chem., 56 (1974) 217-247. 13 S. Chandler and D.W. Fuerstenau, Gold Metallurqv in South Africa, 14 N.P. Finkelstein. in R.J. Adamson (Ed.). Cape and Transvaa? Printers Ltd, Cape Town, 1972, pp. %4-351_ in R. Stokes (Ed.), A Text-book of Rand :4etallurgical 15 W.A. Caldecott, Practice, Charles Griffin and Co., London, 1912, pp. 380-398. 16 C.G. Fink and G.L. Putnam, Trans. Tiletall. Sot. AIHE, 187 (1950) 952-955. Dressing Notes no. 23, American Cyanamid 17 N. Hedley and H. Tabachnick , Mineral Co. 1968. p. 36_ 18 A-0. Filmer, J.S. Afr. Inst. Min. !4etall., 82 (1982) 90-94. F.:4. Howell, Northern !4iner., 20th April (1970). Holtum-and R. Rubin, in H.W. Glen (Ed.), :z P .A_ Laxen, C.A. F7eming;D.A. Proc. Twelfth Congress of the Council for Ilining and Metallurgical Institutions, The South African Institute of Mining and Metal turgy, Johannesburg, 1982, Vol. 2, pp. 551~5:1, inst. 14in.frletall-, 77 (1977) 21 R-3. Davidson and D. Duncanson, J-S. Afr.

6

254-261. in K. Osseo-Asare and J.D. lililler 22 R.L. Paul, A-0. Filmer and M.J. Nicol. Development and Plant Practice, Proc. 3rd (Eds.), Hydrometallurgy-Research, International Symposium on Hydrometal lurgy , Atlanta, 1983, pp. 689-704. M.J. Nicol and D.I. Nicol, Symposium: Ion Exchange and Solvent 23 C.A. Fleming, Extraction in Mineral Processing, National Institute for Metallurgy, Randburg, 1980. Paper presented at MINTEK and M-J. Ohlson de Fine, 24 N.D. Hulse, B. Fitzgerald 50, Sandton, 1984. G.A. Brown, C.G. Schmidt, N-W. Hanf, 3. Duncanson *and 25 R.J. Davidson, 5.3. Tavlor, J. S. Afr. Inst. Min. Hetall., 78 (1978) 146-165. C.A. Fleming, Council for Mineral Technology, Private Communication. :67 :4-J. Nicol, E. Schalch and P. Balestra, J. S. Afr. Inst. Min. Metal1 ., 79 (1979). 191-197. Chem., 83 (1977) 19132. 28 3-A-J. Rand, J. Electroanal.