ArticlePDF Available

Abstract and Figures

A systematic voltammetric study developed in this work allows the determination of the potential range at which the selective deposition of gold and silver is carried out in the presence of a high content of copper. As a first approach, laboratory solutions prepared with a high content of cyanide and copper and low values of gold and silver are used; later, the methodology is applied to leaching solutions of industrial origin.The chemical speciation and microelectrolysis studies showed that copper deposition occurs at more negative potentials than deposition of gold and silver. Also, the voltammetric study of a cyanide solution containing low concentrations of Au(I) and Ag(I), free of and with high concentration of Cu(I) was carried out. The study shows the potential range at which Au(I) and Ag(I) are reduced despite the high concentration of the Cu(I) ions. The deposition of gold and silver was not interfered with by the high concentration of Cu(I) ions when the leaching solution was electrolyzed in a laboratory electrochemical reactor FM01-LC with a reticulated vitreous carbon (RVC) cathode.
Content may be subject to copyright.
Electrochemical deposition of silver and gold from cyanide
leaching solutions
V. Reyes-Cruz, C. Ponce-de-Leo
´n, I. Gonza
´lez *, M.T. Oropeza
Departamento de Quı
´mica, Universidad Auto
´noma Metropolitana-Iztapalapa, Apdo. Postal 55-534, C.P. 09340 Me
´xico D.F., Mexico
Received 20 March 2001; received in revised form 14 November 2001; accepted 4 June 2002
Abstract
A systematic voltammetric study developed in this work allows the determination of the potential range at which the
selective deposition of gold and silver is carried out in the presence of a high content of copper. As a first approach, laboratory
solutions prepared with a high content of cyanide and copper and low values of gold and silver are used; later, the methodology
is applied to leaching solutions of industrial origin.
The chemical speciation and microelectrolysis studies showed that copper deposition occurs at more negative potentials than
deposition of gold and silver. Also, the voltammetric study of a cyanide solution containing low concentrations of Au(I) and
Ag(I), free of and with high concentration of Cu(I) was carried out. The study shows the potential range at which Au(I) and
Ag(I) are reduced despite the high concentration of the Cu(I) ions. The deposition of gold and silver was not interfered with by
the high concentration of Cu(I) ions when the leaching solution was electrolyzed in a laboratory electrochemical reactor FM01-
LC with a reticulated vitreous carbon (RVC) cathode.
D2002 Elsevier Science B.V. All rights reserved.
Keywords: Silver cyanide; Gold cyanide; Copper cyanide; Electrochemical recovery; Cyanide leaching; RVC electrode; Electrodeposition
1. Introduction
Cyanide leaching processes have been used by the
mining industry for over 100 years in the extraction of
noble metals (Kordosky et al., 1992; Fleming, 1992).
Minerals from which most of the noble metals are
obtained are increasingly poorer (gold and silver
concentrations in the order of 15 ppm), so the
leaching solutions from these processes do contain
Au(I), Ag(I) and Cu(I), with copper in concentrations
typically over a hundred times higher than the other
two metals. This high concentration of Cu(I) might
interfere during the selective recovery of gold and
silver (Jha, 1984), and the use of ion exchange resins
or activated carbon to remove the Cu(I) ion is often
necessary to obtain a concentrated solution of Au(I)
and Ag(I). The following stage after the removal of
interfering ions is the recovery of noble metals. Two
traditional methods have been used: cementation and
electrolysis (Fleming, 1992; Jha, 1984). The electrol-
ysis method has been used in concentrated solutions
in electrochemical reactors with plane electrodes (e.g.
electrodeposition of copper or zinc); however, with
dilute solutions, the efficiency is low (Jha, 1984;
Reyes, 1998). Works reported in the literature have
shown that the high surface area found in porous
0304-386X/02/$ - see front matter D2002 Elsevier Science B.V. All rights reserved.
PII: S0304-386X(02)00083-X
*
Corresponding author. Fax: +52-5804-4666.
E-mail address: igm@xanum.uam.mx (I. Gonza
´lez).
www.elsevier.com/locate/hydromet
Hydrometallurgy 65 (2002) 187 – 203
electrodes increases the efficiency when used with
diluted solutions (Bennion and Newman, 1972;
Coeuret, 1976; Coeuret et al., 1976; Trainham and
Newman, 1977; Olive and Lacoste, 1980; Coeuret and
Storck, 1981). Most gold plants actually use stainless
steel wool as cathode. The recovery of Au(I) and
Ag(I) at concentrations between 11 and 30 ppm has
been recently studied (Waterman et al., 1984; Reyes et
al., 2002; Stavart et al., 1999). However, the recovery
of Au(I) and Ag(I) from solutions containing high
concentration of Cu(I) in cyanide solutions has
received less attention.
Since the metal with the highest concentration
would be expected to be the first deposited, the
presence of large amounts of Cu(I) is likely to
influence the selective recovery of gold or silver.
Preliminary studies performed on stainless steel 304,
vitreous carbon and Ti showed that vitreous carbon is
the most adequate material for performing Ag(I)
deposition from a diluted silver solution (11 ppm)
with a high content of copper (Reyes, 1998).
The solution used in this preliminary study (0.1
M Cu(I), 0.5 M CN
and 10
4
M Ag(I)) differs
significantly from the solutions from industrial
leaching processes with cyanides; nevertheless, the
conditions of high copper and cyanide concentra-
tions allowed the realization of an electrochemical
study on a vitreous carbon electrode where the
recovery of silver was shown to be possible without
the deposition of copper, despite the fact that the
concentration of Cu(I) was 100 times higher than the
concentration of silver (Reyes et al., 2002). The
study showed that the Cu(I) deposited at potentials
more negative than Ag(I) and that the cyanide
species of Cu(I) modified the capacitive current
densities of the media (CN
), making favorable
the deposition of silver. On the other hand, in this
study, a systematic methodology is established to
determine the potential range at which the selective
silver deposition takes place. For that reason, it
confronts the problem of faradaic current density
response from the reduction process of a low silver
concentration (11 ppm) masked by the capacitive
current of cyanide. Thus, a part of information of a
previously performed study (Reyes et al., 2002) is
taken up again and the same methodology is applied
in order to study the model solutions containing (a)
Au(I) and (b) Au(I) with Ag(I) in the presence and
absence of Cu(I) (laboratory solutions). This allows
later analysis validation of the results obtained in the
study of an industrial leaching solution containing
low concentrations of copper and cyanide and much
lower concentrations of noble metals (of the order of
15 ppm).
Firstly, speciation and voltammetric studies of a
cyanide solution with a high concentration of Cu(I)
and low concentrations of Au(I) (laboratory solution)
were carried out. The purpose of this study was to find
out whether the high concentration of copper inter-
feres with the selective deposition of gold. After this
experiment, a voltammetric study of the cyanide
solution containing the three metallic ions (high
Cu(I) concentration and low concentrations of Au(I)
and Ag(I), laboratory solutions), was carried out in
order to determine if the interaction between the three
metal ions changes the potential range at which the
selective reduction of Au(I) and Ag(I) occurs. After-
wards, the same methodology was applied to the
industrial leaching solution.
Once the potential range of the Au(I) and Ag(I)
reduction was established, an electrolysis of the cya-
nide leaching solution containing the three metallic
ions was carried out in an electrochemical FM01-LC
laboratory reactor.
2. Experimental
A 100-ml Pyrex cell with a three-electrode system
and nitrogen inlet was used in the voltammetric study.
The working electrode was a vitreous carbon rod with
geometric area of 0.07 cm
2
. The electrode surface was
polished with 0.3-Am alumina powder/water and
rinsed with deionised water followed by ultrasonic
bath for 5 min to remove traces of alumina, grease and
a final rinse with deionised water. The reference and
counter electrodes were saturated calomel and graph-
ite, respectively. The solutions were:
Laboratory solutions for methodology validation
(a) Cyanide solution 0.5 M KCN
(b) Cyanide solution
of Cu(I)
0.1 M CuCN and
0.5 M KCN
(c) Cyanide solution
of Au(I)
10
4
M KAuCN
2
and
0.5 M KCN
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203188
All solutions except the industrial leaching solution
were prepared with deionised water 18 MV
1
cm
1
and analytical grade reagents. The pH was held
constant at 10 for laboratory solutions and the solu-
tions were deoxygenated with nitrogen for 10 min
prior to cyclic voltammetry experiments. A flux of
nitrogen previously saturated in a CN
solution was
held on the surface of the solution during the experi-
ments without disturbing the electrolyte.
The electrolysis of the selective reduction of Au(I)
and Ag(I) in the presence of high concentrations of
Cu(I) was carried out using an industrial leaching
solution on a filter press electrochemical reactor,
FM01-LC. A full description of this reactor has been
outlined in the literature (Brown and Plecher, 1992;
Brown and Plecher, 1993; Brown and Plecher, 1994).
A cationic NafionRmembrane NX550 divided the
anodic and cathodic reactor compartments. The cath-
ode used was a reticulated vitreous carbon (RVC)
electrode with 60 pores per inch (ppi), filling a
volume of 31 cm
3
(Electrosynthesis). Copper plates
glued by conductive carbon paste made the electrical
contact with the RVC electrode. The anode was an
A304 stainless steel plate.
The industrial solution was re-circulated through
the anolyte and catholyte compartments using two
centrifugal pumps obtained from Cole Palmer. A
potentiostat EG and G model PARC 273A with a
Booster KEPCO (0 20 A and 0 20 V) and the M270
software were used in the voltammetric and macro-
electrolysis experiments. The determination of total
Au(I), Ag(I) and Cu(I) concentrations was carried out
by atomic absorption spectroscopy (AAS) (Varian
model Spectr AA-20).
3. Results and discussion
3.1. Laboratory solutions
3.1.1. Chemical speciation study
A chemical speciation study was performed in order
to establish the nature of the electroactive species of
gold, silver and copper in cyanide solutions. A Pour-
baix type diagram (Fig. 1) was constructed using the
thermodynamic data for soluble and insoluble species
of gold, silver and copper reported in the literature
(Ringbom, 1963; Zhang et al., 1997; Caroli and
Sharma, 1978), taking into account the laboratory
solution conditions ( pCNV=log[CNV] = 0.222,
pAuV=log[AuV(I)] = 4, pAgV=log[AgV(I)]=4 and
pCuV(I)= log[CuV(I)] = 1) using the method proposed
by Rojas et al. (1991, 1993). The MV(I) corresponds to
the generalized chemical species of the metallic ion in
solution (Rojas et al., 1991, 1993).
The full lines in Fig. 1 represent the conditional
potential change of the system MV(I)/M(0) with pH.
The dotted lines represent the limit of the pH range
where a particular metal ion species predominates
(high molar fraction) with respect to the other
cyanide species of the same metallic ion (generalized
chemical species), or in the other case, the solubility
limit for CuCN
(s)
.Fig. 1 shows that under the
chemical conditions of leaching solutions, there are
four copper, two silver and one gold species of
cyanide.
Fig. 1 shows that, at any pH, the redox potential
of the couple CuV(I)/Cu(0) has more negative values
with respect to the potential of the couples AuV(I)/
Au(0) and AgV(I)/Ag(0). These results indicate that
under thermodynamic considerations, the copper
species should not interfere with the selective reduc-
tion of Au(I) and Ag(I) under experimental condi-
tions of laboratory solution used to validate the
methodology.
(d) Cyanide solution
of Au(I) and Cu(I)
0.1 M CuCN,
10
4
M KAuCN
2
and 0.5 M KCN
(e) Cyanide solution
of Au(I),
Ag(I) and Cu(I)
0.1 M CuCN,
10
4
M KAuCN
2
,
10
4
M AgNO
3
and 0.5 M KCN
Industrial leaching solution
(f) Industrial leaching
solution
0.025 M (400 ppm)
free CN
,
810
3
M
(500 ppm) Cu(I),
510
6
M
(1 ppm) Au(I),
310
5
M
(3 ppm) Ag(I),
0.015 M (615 ppm) Ca,
0.025 M (575 ppm) Na
and 3 10
4
M
(17 ppm) Zn at pH 11
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203 189
The calculated potentials associated with the elec-
trochemical reactions AuV(I)/Au(0), AgV(I)/Ag(0) and
CuV(I)/Cu(0) at pH = 10, pCNV= 0.22, pAuV=4,
pAgV= 4 and pCuV= 1 are:
AuðCNÞ
2þ1e!Au0þ2CN
Ej¼1060 mV vs:SCE ð1Þ
AgðCNÞ2
3þ1e!Ag0þ3CN
Ej¼1198 mV vs:SCE ð2Þ
CuðCNÞ3
4þ1e!Cu0þ4CN
Ej¼1546 mV vs:SCE ð3Þ
It is important to note that under experimental
conditions of the laboratory solution, the difference
in Ejfor gold and silver is very small; this would
indicate that the selective deposition of these two
metals is not easy.
3.1.2. Voltammetric study of gold
A voltammetric study of cyanide solutions with
and without metal ions was carried out on a plane
vitreous carbon electrode within the range of 100 to
1800 mV vs. SCE. In this study, the influence of
Cu(I) and cyanide on the electrochemical deposition
of gold was determined.
Fig. 2 shows a comparison of voltammetric behav-
iors of the following solutions: cyanide solution free
of metallic ions (curve a), cyanide solution with Au(I)
(curve b), cyanide solution with Cu(I) (curve c) and
cyanide solution with both Cu(I) and Au(I) (curve d).
In Fig. 2a, the cyanide solution free of metallic ions
has a high capacitive current density at potentials
lower than or equal to 1400 mV vs. SCE. The
current density is attributed to the adsorption of
cyanide on the surface of the vitreous carbon electrode
(Reyes et al., 2000, 2001; Vilchis-Carbajal et al.,
2000) (see inset in Fig. 2). Towards more negative
Fig. 1. Pourbaix type diagrams of soluble and insoluble chemical species involved in the redox couples: AuV(I)/Au(0) (-n-), AgV(I)/Ag(0) (-E-) and
CuV(I)/Cu(0) (-
y
-). The diagrams were constructed with thermodynamic data from the literature considering as non-variable the following
concentrations: 10
4
MAuV(I), 10
4
MAgV(I) and 0.1 M CuV(I) in 0.5 M CN
. The concentrations of these chemical species represents the
composition found in cyanide laboratory solutions.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203190
potentials, the reduction of the medium increases due
to the water reduction.
The presence of Au(I) ions in the cyanide solution
shifts the current density associated with the reduction
of water towards more negative potentials with respect
to the cyanide solution free of metallic ions (Fig. 2b
and a, respectively). Since the reduction of water does
not have an associated peak, the influence of the
electroactive species in this process was measured
by the potential at which the current density was 85
AAcm
2
. In each case, this potential (E
85 AAcm
2
)
was used as a parameter for comparison. In the metal-
Fig. 2. Typical cyclic voltammograms obtained from laboratory solutions containing 0.5 M CN
at pH 10, on a vitreous carbon electrode, at 25
mV s
1
. The curves show the influence of different ions: (a) free of metallic ions, (b) 10
4
M Au(CN)
2
, (c) 0.1 M Cu(CN)
4
3
and (d) 10
4
M
Au(CN)
2
and 0.1 M Cu(CN)
4
3
. The inset shows the voltammetric responses at low current densities. The current density E
85 AAcm
2
chosen for
analysis of water reduction is indicated.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203 191
free solution, E
85 AAcm
2
=1506 mV vs. SCE,
while in the solution containing Au(I), E
85 AAcm
2
=
1658 mV vs. SCE. The presence of gold reduces the
capacitive current density, which was attributed to the
complexes of gold with the adsorbed cyanide (Mac
Arthur, 1972; Kirk et al., 1980; Mughogho and
Crundwell, 1996; Chrzanowski et al., 1996; Bindra
et al., 1989). In the reverse potential scan for the
solution containing Au(I) and CN
, the current den-
sity was higher than in the forward scan. This is a
typical behavior of an interface modified by the
presence of a gold deposit. In the forward scan, the
gold and water were reduced on the vitreous carbon,
while in the reverse scan, they were reduced on the
gold. Due to the low concentration of Au(I) in the
cyanide solution, the cathodic current density associ-
ated with the reverse scan is directly attributed to the
reduction of water which notably increases the inter-
facial pH. In the inset of Fig. 2b, it can be seen that
during the reverse scan, the curve has an associated
constant current density in the potential range of
1050 to 400 mV vs. SCE. This observation
suggests the formation of a passive film does not allow
the gold dissolution to be seen as it has been reported
in the literature (Mac Arthur, 1972; Kirk et al., 1980;
Mughogho and Crundwell, 1996). The said passive
film was enhanced by the pH modification at the
interface. This fact does not allow the gold deposition
to be clearly evidenced; however, the above descrip-
tion of voltammetric behavior suggests the presence of
deposited gold.
The influence of the Cu(I) ion in the cyanide
solution (Fig. 2c) can be seen in the voltammetric
response as a shift of the reduction potential of water
towards more negative potentials (E
85 AAcm
2
=
1664 mV vs. SCE), and a modification of the
capacitive current density. The latter effect can be
attributed to the fact that Cu(I) is adsorbed on the
vitreous carbon surface (Reyes et al., 2000, 2001)
and competes with the adsorbed cyanide species
(Reyes et al., 2000, 2001; Vilchis-Carbajal et al.,
2000). On the other hand, there are no peaks asso-
ciated with the reduction and oxidation of copper in
the range of the potential scan studied. In a previous
work, it was shown that the reduction of Cu(I) on a
vitreous carbon electrode from a cyanide solution
begins at a potential of 2200 mV vs. SCE (Reyes
et al., 2002).
From Fig. 2d, it can be seen that the presence of
Au(I) and Cu(I) in the cyanide solution causes a
more negative potential for the reduction of water
(E
85 AAcm
2
=1728 mV vs. SCE) with respect
to Fig. 2a, b and c. This indicates that Au(I) and Cu(I)
ions in the cyanide solution have an influence on the
capacitive current densities and the reduction of water
since both metals involve species adsorbed on the
vitreous carbon surface (Reyes et al., 2000, 2001; Mac
Arthur, 1972; Kirk et al., 1980; Mughogho and
Crundwell, 1996; Chrzanowski et al., 1996; Bindra
et al., 1989). The competition between different
adsorbates on the vitreous carbon causes a modifica-
tion of the voltammetric response. In this work, we
associated such behavior with the modification of the
capacitive current densities. A more detailed study
could consider the evaluation of these capacitive
currents, however, it is out of the scope of this work.
During the reverse scan in Fig. 2d, there are two
oxidation processes: process I at 900 mV vs. SCE,
and process II at 550 mV vs. SCE. These processes
can be attributed to the oxidation of gold as reported
in the literature (Mac Arthur, 1972; Kirk et al., 1980;
Mughogho and Crundwell, 1996) or to the dissolution
of the codeposit Cu/Au (as shown below). When
Cu(I) is in solution, it is possible to observe the
oxidation process of gold, which indicates that the
passive process seen in alkaline media has been
modified by the Cu(I), because the pH modification
in the interface is notably diminished. This effect is
similar to that reported for the presence of lead in the
gold oxidation process.
From the above study, it was considered necessary
to identify the potential range at which the selective
deposition of gold occurs in the presence of high
concentration of Cu(I). This was done by a voltam-
metric study, shifting the switching potential E
k
towards negative values.
3.1.3. Influence of the negative switching potential
(E
k
)
Fig. 3 shows the voltammograms obtained by
changing the switching potential E
k
during the
forward potential scan for cyanide solution with
Au(I) and Cu(I). It can be seen that at E
k
=1500
mV vs. SCE, there is a dissolution shoulder II (see
inset) whereas at E
k
V1700 mV vs. SCE, there is a
dissolution peak I. The current density associated with
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203192
these two processes increases as the switching poten-
tial E
k
is changed toward more negative potentials.
These two processes could be associated with the
oxidation of metallic gold deposited during the for-
ward scan, since in a previous work, it was demon-
strated that the reduction of Cu(I) in a cyanide solution
(Au(I) free) on a vitreous carbon electrode begins at
2200 mV vs. SCE (Reyes et al., 2002). However, the
potential of the peak I shifts towards negative potential
values as the E
k
turns more negative; at E
k
V
2000 mV vs. SCE, the current density peak in-
creases, indicating the formation of the codeposit Cu/
Au or the massive deposition of copper.
The dissolution of both the codeposit Cu/Au and
the metallic Au occurs at very similar potentials and
therefore, the identification of each dissolution proc-
ess is complex. It was not possible to identify the
exact potential range of gold deposition free of
copper, so it was decided to quantitatively analyze
the voltammetric curves. The associated charge of the
oxidation processes, Qa, was determined from the
area under the voltammetric curves of solutions con-
taining Au(I) and Cu(I), Fig. 3, and plotted as a
function of E
k
(Fig. 4a).
In Fig. 4a, the curve of the charge Qa as a function of
E
k
for the cyanide solution containing Au(I) and
Cu(I) ions shows a linear correlation in the switching
potential range of 1700 zE
k
,z1900 mV vs.
SCE. This linear behavior can be attributed to the gold
deposit on the vitreous carbon electrode. On the other
Fig. 3. Partial view of typical cyclic voltammograms obtained from a laboratory solution containing 10
4
M Au(CN)
2
and 0.1 M Cu(CN)
4
3
in 0.5 M CN
at pH 10, on a vitreous carbon electrode (0.07 cm
2
)at25mVs
1
. The voltammograms were obtained at different negative
switching potentials (E
k
). The inset shows the voltammetric responses at low current densities.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203 193
hand, it can be seen that at more negative switching
potentials, the linear correlation of the curve Qa vs.
E
k
has two different slopes; the first one at potentials
between 1900 and 2000 mV vs. SCE, due to the
Cu/Au codeposit, and the second at E
k
more negative
than 2000 mV vs. SCE, due to the massive deposi-
tion of copper.
Since the concentration of Au(I) is very low, the
faradaic current associated with its reduction process is
lower than or similar to the capacitive current, so it is
not possible to determine the potential range at which
the deposition of gold takes place; besides, it is not
possible to distinguish the gold deposit through its
process of electrochemical dissolution since when
there are some, the reduction of water becomes more
important modifying the interfacial pH. However, the
presence of Cu(I) in cyanide solution allows the obser-
vation of the dissolution peak of gold through the
analysis of the area under oxidation peaks at different
E
k
. Therefore, it was possible to determine at which
potential the codeposit of Cu/Au begins. Up to now, the
influence of Ag(I) on this system is not known and it is
necessary to study the interaction between Au(I) and
Ag(I) in the same solution with and without Cu(I).
3.1.4. Voltammetric study of silver and gold
Fig. 5 shows the voltammetric comparison of the
following solutions: cyanide free from metallic ions
(curve a), cyanide with Au(I) and Ag(I) (curve b), and
cyanide with Cu(I), Au(I) and Ag(I) (curve c).
The metallic ions Au(I) and Ag(I) shift the current
density associated with the reduction of water towards
less negative potentials (E
85 AAcm
2
=1402 mV
vs. SCE) with respect to cyanide solution free from
metallic ions (E
85 AAcm
2
=1506 mV vs. SCE),
Fig. 5b and a, respectively, catalyzing the reduction
of water. This indicates that although the current
density associated with the reduction of Au(I) and
Ag(I) is not evident, either these ions modify the
surface of the vitreous carbon electrode or the
deposit of silver gold increases the water reduct-
ion. The shift in the reduction potential of water is
more important when there is Au(I) with Ag(I) than
when there is only Au(I) (Figs. 5b and 2b, respec-
tively), showing that silver is responsible for such
behavior.
In the inset of Fig. 5, it can be seen that the
capacitive current density of cyanide solution free
from metallic ions is similar to the current of the
Fig. 4. Oxidation charge (Qa) associated with the dissolution peaks as a function of the negative switching potential (E
k
) from the
voltammograms obtained on a vitreous carbon electrode (0.07 cm
2
)at25mVs
1
from 0.5 M CN
laboratory solutions at pH 10 containing:
(a) 10
4
M Au(CN)
2
and 0.1 M Cu(CN)
4
3
, (b) 10
4
M Ag(CN)
3
2
and 0.1 M Cu(CN)
4
3
, (c) 10
4
M Au(CN)
2
with 10
4
M Ag(CN)
3
2
without Cu(CN)
4
3
and (d) 10
4
M Au(CN)
2
with 10
4
M Ag(CN)
3
2
in the presence of 0.1 M Cu(CN)
4
3
.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203194
solution containing the three metallic ions, Fig. 5a
and c. The presence of Cu(I) in the cyanide solution
with Au(I) and Ag(I), shifts the reduction of water
towards more negative potentials (E
85 AAcm
2
=
1494 mV vs. SCE). This indicates that the Cu(I)
ion has an important effect on the reduction of water
and on the process of cyanide and gold adsorption.
On the other hand, the reduction of gold and
silver is masked by the capacitive current densities
(see inset of Fig. 5b and c). However, in the reverse
scan, there is only one oxidation peak at 600 mV
vs. SCE in both solutions (Fig. 5b and c). This
behavior could be attributed to the Ag/Au codeposit,
since this oxidation peak is present at more positive
potentials than the oxidation peak of silver deter-
mined in the previous paper (Reyes et al., 2002) and
at more negative potential than that corresponding to
the oxidation of gold (peak II). It is important to
note that the peak I, which appears when the gold
deposit takes place in the presence of copper (Fig.
2d), is not observed in this case; this is an additional
argument for the fact that a codeposit of Ag/Au is
taking place. The oxidation peak in 600 mV vs.
SCE is slightly higher when Cu(I) ion is in solution,
indicating that there is either more deposit of Ag/Au
or codeposit of copper on this new surface (see
below).
In order to establish the potential at which the
deposition of gold and silver without copper takes
place, a voltammetric study was carried out chang-
ing the switching potential E
k
towards negative
values.
Fig. 5. Typical cyclic voltammograms obtained from laboratory solutions containing 0.5 M CN
at pH 10, on a vitreous carbon electrode, at 25
mV s
1
. The curves show the influence of different ions: (a) free of metallic ions, (b) 10
4
M Au(CN)
2
,10
4
Ag(CN)
3
2
and (c) 10
4
M
Au(CN)
2
,10
4
Ag(CN)
3
2
and 0.1 M Cu(CN)
4
3
. The inset shows the voltammetric responses at low current densities and the current density
E
85 AAcm
2
chosen for the analysis of water reduction.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203 195
3.1.5. Influence of the negative switching potential
(E
k
)
Fig. 6 shows the voltammograms obtained when
the negative switching potential E
k
was changed
towards negative values for the following solutions:
cyanide solution with Ag(I) and Cu(I) (curve a), from
a previous work (Reyes et al., 2002), cyanide solution
with Au(I) and Ag(I) without Cu(I) (curve b) and with
Cu(I) (curve c).
In Fig. 6a, from E
k
=1400 mV vs. SCE, there
is an oxidation peak of Ag(0) to Ag(I) at 675 mV
vs. SCE; the current density associated with the
Fig. 6. Partial view of typical cyclic voltammograms obtained on a vitreous carbon electrode (0.07 cm
2
)at25mVs
1
from 0.5 M CN
laboratory solutions at pH 10 containing: (a) 10
4
M Ag(CN)
3
2
in the presence of 0.1 M Cu(CN)
4
3
, (b) 10
4
M Ag(CN)
3
2
and 10
4
M
Au(CN)
2
without Cu(CN)
4
3
and (c) 10
4
M Ag(CN)
3
2
and 10
4
M Au(CN)
2
in the presence of 0.1 M Cu(CN)
4
3
. Voltammograms were
obtained at different negative switching potentials (E
k
).
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203196
oxidation peak increases as the switching potential
E
k
turns more negative.
Fig. 6b shows that in the solutions with Au(I) and
Ag(I), there is an oxidation peak at 600 mV vs.
SCE from E
k
=1500 mV vs. SCE, with a current
density that increases as E
k
becomes more negative.
This peak shifts towards less negative values with
respect to the oxidation peak of silver (Fig. 6a),
indicating the normal codeposit of Ag/Au although
the gold dissolution at more negative potential is not
observed in this case.
The voltammogram of cyanide solution containing
the three metallic ions (Fig. 6c) also shows an oxida-
tion peak at 600 mV vs. SCE from E
k
=1500
mV vs. SCE. The current density increases, as the
E
k
turns more negative. This oxidation peak was
shifted towards less negative potentials within the
range of E
k
from 1500 to 1600 mV vs. SCE.
However, for E
k
V1700 mV vs. SCE, the poten-
tial peak now changed to negative values. This change
of the oxidation peak potential is associated with the
dissolution of different deposits (see below).
In order to identify the potential range at which the
gold and silver deposition is free of copper, a quanti-
tative study of the voltammetric curves was carried
out. The associated charge, Qa, of the solutions with
and without copper, was calculated and plotted as a
function of the switching potential E
k
.Fig. 4 shows
the curves Qa vs. E
k
of the following solutions:
cyanide with Ag(I) and Cu(I) (curve b) obtained from
a previous work (Reyes et al., 2002), cyanide with
Au(I) and Ag(I) (curve c) and cyanide solution with
Au(I), Ag(I) and Cu(I) (curve d).
In Fig. 4, cyanide solutions of Au(I) and Ag(I)
without and with Cu(I), Fig. 4c and d, show the same
slope during the first three switching potentials E
k
,
thus indicating the same reduction process in these
solutions, the codeposit of Ag/Au. At more negative
switching potentials, the slope of the curve Qa vs.
E
k
of these solutions was similar to the slope of the
solution containing Ag(I) and Cu(I) (Fig. 4c, d and b,
respectively), indicating the occurrence of the silver
deposition process. On the other hand, in the solution
containing the three metallic ions (Fig. 4d), there is a
Fig. 7. Pourbaix type diagrams of soluble and insoluble chemical species involved in the redox couples: AuV(I)/Au(0) (-n-), AgV(I)/Ag(0) (-E-)
and CuV(I)/Cu(0) (-
y
-). The diagrams were constructed with thermodynamic data from the literature considering as non-variable the following
concentrations: 5 10
6
MAuV(I), 3 10
5
MAgV(I) and 8 10
3
MCuV(I) in 0.025 M CN
. The concentrations of these chemical species
represent the composition found in the industrial leaching solution.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203 197
change in the slope and an increase of the density
charge after E
k
=1900 mV vs. SCE, which is
attributed to the codeposit Cu/Ag/Au and the massive
deposition of copper.
From the comparative study of cyanide solutions
containing Au(I) and Ag(I) ions with and without
Cu(I), it is possible to determine the potential of the
codeposit Ag/Au free of copper. However, the poten-
tial deposition of silver and gold cannot be found
independently.
The methodology developed till now allows us to
establish the systematic electrochemical study that is
to be carried out in order to identify the codeposit of
Ag/Au without copper deposition from diluted gold
and silver solutions with a high content of copper and
cyanide. This methodology is then applied to an
industrial leaching bath.
3.2. Industrial leaching solution
3.2.1. Study of chemical speciation
The chemical speciation study of electroactive
species of Au, Ag and Cu present in the industrial
leaching solution ( pCNV=log[CNV] = 1.6, pAuV=
log[AuV] = 5.3, pAgV=log[AgV] = 4.55, and
pCuV=log[CuV] = 2.1) is shown in Fig. 7.The
Pourbaix type diagram was constructed with the
same methodology used for the speciation study of
Fig. 1.
In Fig. 7, it can be observed that Cu presents four
cyanide species, whereas Ag presents two and Au
only one cyanide species. Under conditions of indus-
trial leaching (very dilute concentrations of gold,
silver and cyanide ions), it can be seen that the silver
cyanide species have a lower state of coordination
than that observed in the first study of speciation
carried out in this work (Fig. 1). On the other hand,
Fig. 7 shows that, again in all pH values, the potential
of the redox couple Cu(I)/Cu(0) appears at more
negative potentials with regard to the redox couples
Au(I)/Au(0) and Ag(I)/Ag(0), indicating that copper
does not interfere thermodynamically in the selective
deposition of gold and silver.
Potentials and thermodynamic reactions associated
with the Au(I)/Au(0), Ag(I)/Ag(0) and Cu(I)/Cu(0)
couples in an industrial leaching solution at pH = 11,
Fig. 8. Partial view of typical cyclic voltammograms obtained from an industrial leaching solution containing 510
6
M Au(CN)
2
,310
5
M Ag(CN)
2
and 8 10
3
M Cu(CN)
4
3
in 0.025 M CN
at pH 10, on a vitreous carbon electrode (0.07 cm
2
)at25mVs
1
. The
voltammograms were obtained at different negative switching potentials (E
k
).
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203198
pCNV= 1.6, pAuV= 5.3, pAgV= 4.55 and pCuV= 2.1
are:
AuðCNÞ
2þ1e!Au0þ2CN
Ej¼973 mV vs:SCE ð4Þ
AgðCNÞ
2þ1e!Ag0þ2CN
Ej¼1037 mV vs:SCE ð5Þ
CuðCNÞ3
4þ1e!Cu0þ4CN
EW¼1280 mV vs:SCE ð6Þ
It is important to stress that, in principle, the above-
predicted potentials should be more negative than
those previously obtained in Eqs. (1) (3) because of
having much lower concentrations of gold, silver and
copper in relation to the laboratory solution used.
However, the potentials are less negative, which is
attributed to the lower concentration of cyanide in the
industrial leaching solution.
In this case, the potential difference Ejbetween Au
and Ag is even smaller with regard to that seen in the
laboratory solution; this predicts that the separation of
these two metals is more difficult.
3.2.2. Influence of the switching potential scan (E
k
)
Fig. 8 shows the voltammograms obtained by
modifying the switching potential in direct potential
scan (E
k
) for the industrial leaching solution. This
figure shows that from E
k
1200 mV vs. SCE,
there is an oxidation peak at 425 mV vs. SCE and
that the current density associated with this peak
increases as the switching potential is shifted towards
more negative values. The oxidation peak appears
at less negative potentials within the range of E
k
from 1200 to 1400 mV vs. SCE whereas at
E
k
V1500 mV vs. SCE, the oxidation peak ap-
pears at more negative potentials, indicating the dis-
solution of different codeposits of gold, silver and
copper on the VC surface. The oxidation peak dis-
placement observed at less negative potentials in
relation to the oxidation peak of the laboratory sol-
ution study is due to the difference in concentration of
Fig. 9. Oxidation charge (Qa) associated with dissolution peaks as a function of the negative switching potential (E
k
) from the
voltammograms obtained on a vitreous carbon electrode (0.07 cm
2
)at25mVs
1
at pH 10, from (a) industrial leaching solution containing:
510
6
MAu(CN)
2
,310
5
MAg(CN)
2
,810
3
MCu(CN)
4
3
and0.025 MCN
and(b) laboratorysolutioncontaining: 10
4
MAu(CN)
2
Au(CN)
2
with 10
4
M Ag(CN)
3
2
in the presence of 0.1 M Cu(CN)
4
3
and 0.5 M CN
.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203 199
metallic ions of Au(I), Ag(I) and Cu(I) and a lower
concentration of cyanide in the solution.
On the other hand, in Fig. 8, it is observed that the
oxidation peaks of industrial leaching solution are
wider with regard to laboratory solution and they
change their shape rapidly with increase in the switch-
ing potential. This indicates how complicated it would
be to develop the methodology to identify where the
Ag/Au codeposition takes place without the deposi-
tion of copper from the industrial leaching solution.
The statement above justifies the need to use higher
copper and cyanide concentrations to develop the
methodology used in this study.
With the purpose of determining the potential
range at which the deposition of Au(I) and Ag(I) free
of copper from the industrial leaching solution takes
place, the quantitative study of the voltammetric
curves was carried out through the charge associated
with E
k
-dependent oxidation peaks (Qa). Fig. 9
compares the Qa vs. E
k
curves of an industrial
leaching solution (curve a) in relation to that of the
previously obtained and discussed more concentrated
cyanide solution of Au(I), Ag(I), Cu(I) and CN
(curve b).
In Fig. 9, the behaviors of the slopes of the Qa vs.
E
k
curves of the cyanide solution, for the laboratory
solution prepared in the prior section, and the indus-
trial leaching solution are observed to be quite similar.
On the other hand, it can be seen that for the industrial
leaching solution, there is a potential displacement
towards less negative values with regard to more
concentrated cyanide solution of Au(I), Ag(I), Cu(I)
and CN
, which agrees with the speciation studies of
both solutions.
Fig. 9a shows that for the industrial leaching
solution, the codeposition attributed to Ag/Au takes
place within the potential range of 1200 1400 mV
vs. SCE (slope m=0.13). Linear correlation in this
range does not show the same slope (m=0.90) as
that obtained for more concentrated cyanide solution
of Au(I), Ag(I), Cu(I) and CN
, because of the
nucleation processes of these metals on the vitreous
carbon electrode and the fact that, at lower over-
potentials, less gold and silver is deposited. However,
at E
k
V1400 mV vs. SCE, the changes in the
slopes of the Qa vs. E
k
curves of the industrial
leaching solution are similar to the slope changes of
the more concentrated cyanide solution of Au(I),
Fig. 10. Change in the normalized concentration of cyanide metallic species in the catholyte compartment with time during the electrolysis of an
industrial leaching solution. Concentration profile of (a) Au(I), (b) Ag(I) and (c) Cu(I) at electrolysis potential of 1400 mV vs. SCE. The
electrolysis was carried out in an FM01-LC electrochemical laboratory reactor using an RVC of 60 ppi at a linear flow rate of 19 cm s
1
.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203200
Ag(I), Cu(I) and CN
(Fig. 9a and b, respectively),
thus indicating the presence of: (i) the massive dep-
osition of Ag (slope m=0.67), (ii) the codeposition
of Cu/Ag (slope m=1.27) and (iii) the massive
deposition of Cu (slope m=5.46) as the switching
potential turns more negative.
From the comparative study of the charges (Qa) of
industrial leaching solution in relation to the more
concentrated cyanide solution of Au(I) ions with
Ag(I), Cu(I) and CN
, it is possible to determine
the potential at which the codeposition of Ag/Au takes
place without the deposition of copper. However, just
like in the study of the more concentrated cyanide
solution of Au(I), Ag(I), Cu(I) and CN
, it is not
possible to determine the potential at which the gold
and silver deposit independently. In order to confirm
the results from the previous experiments, an electrol-
ysis study of an industrial leaching solution was
carried out.
3.2.3. Electrolysis study
The potential at which Cu(I) does not interfere
with the electrochemical deposition of gold and
silver has been established from the experiments
above. Taking this into account, an electrochemical
deposition of the species Au(I) and Ag(I) in a batch
re-circulation reactor using the industrial leaching
solution (solution f) was carried out.
The electrolysis was at constant potential on a
reticulated vitreous carbon electrode (RVC) for 25
min at a linear flow velocity of 19 cm s
1
. The
concentration change of Au(I), Ag(I) and Cu(I) in
the catholyte compartment during the electrolysis
was analyzed by atomic absorption spectroscopy.
Fig. 10 shows the depletion of Au(I) (curve a),
Ag(I) (curve b) and Cu(I) (curve c) as C
t
/C
0
vs.
time, at a constant potential of 1400 mV vs. SCE,
where C
t
and C
0
are, respectively, the concentrations
of the metal ion at time tand at the beginning of the
electrolysis.
Fig. 10 shows the evolution in the concentration of
the three metal ions with time when the electrolysis
was carried out at 1400 mV vs. SCE. Depletions in
the concentration of Au(I) and Ag(I) were up to 48%
and 71%, respectively, from their original concentra-
tions (Fig. 10a and b). The concentration of Cu(I) was
Fig. 11. Scanning electron microscopy (SEM) image of 60 ppi of the RVC electrode after 25 min of the electrolysis of the industrial leaching
solution containing: 5 10
6
M Au(CN)
2
,3
10
5
M Ag(CN)
2
,8
10
3
M Cu(CN)
43
and 0.025 M CN
at pH 10 for an
electrolysis potential of 1400 mV vs. SCE.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203 201
constant during the first 10 min of electrolysis, how-
ever, in the following 25 min, the concentration of
Cu(I) fell 12% (Fig. 10c). This indicates that metallic
copper would be on the surface of the reticulated
vitreous carbon (RVC).
In order to analyze the morphology and composi-
tion of gold, silver and copper deposits on the RVC,
scanning electron microscopy (SEM) and X-ray dif-
fraction studies on the electrode surface were carried
out. Fig. 11 shows the SEM image of the RVC
electrode after the electrolysis at constant potential
of 1400 mV vs. SCE. In this figure, the metallic
nuclei on the RVC surface could be attributed to gold,
silver and copper deposits. Fig. 12 shows the X-ray
diffractogram obtained for the electrode surface after
the electrolysis at 1400 mV vs. SCE; this diffracto-
gram shows signals that correspond to gold, silver and
copper. The copper signal agrees with the depletion of
this ion observed after 25 min of electrolysis (Fig. 11).
It is important to stress that when the concentra-
tions of Au(I) and Ag(I) diminish in the solution, the
deposition of Cu(I) becomes energetically favorable.
Under these conditions, the electrolysis should be
stopped before the deposition of copper begins if a
quantitative separation of gold and silver is wanted.
The above analysis allows us to propose the recovery
of gold and silver at an applied potential of 1400
mV for the first 10 min of electrolysis in the electro-
chemical batch reactor with an RVC electrode.
The reduction of gold and silver in the electro-
chemical reactor FM01-LC is a preliminary study that
proves that gold and silver can be selectively
removed. However, further studies, such as current
efficiency, mass transport and space– time yield are
necessary to design an efficient electrochemical reac-
tor for the recovery of gold and silver from leaching
process solutions.
4. Conclusions
The deposition of the three metallic ions follows
the sequence: Au, Ag and Cu, this agrees with the
results found in the speciation study.
There is a potential range at which only Au(I) was
reduced even at high concentrations of Cu(I).
The Cu(I) ion contributes to modify the capacitive
current densities of the cyanide media and helps to
enhance the oxidation process of gold since the
water reduction diminishes considerably.
This work shows the influence of different
gold, silver and copper cyanide species on the
simultaneous process of water reduction occur-
ring during the deposition of these metals.
While the silver ions seem to favor this pro-
cess, the copper ions seem to diminish it con-
siderably.
The voltammetric study shows that the simulta-
neous reduction of Au(I) and Ag(I) in a medium
with a high concentration of Cu(I) ions occurs
within the potential range of 1500 to 1900
mV vs. SCE without Cu(I) deposition for labo-
Fig. 12. XRD spectrum obtained from the metallic deposit on the RVC electrode surface shown in Fig. 11. The dark lines correspond to the
sample and the pale lines to the standards of gold, silver and copper.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203202
ratory solution and 1200 to 1500 mV vs. SCE
for industrial leaching solution.
The recovery of gold and silver was proposed at an
applied potential of 1400 mV vs. SCE for the
first 10 min of the electrolysis in a batch reactor
with re-circulation on a RVC electrode.
The reduction of gold and silver in the electro-
chemical reactor FM01-LC confirms the selective
deposition of both metals. However, these are
preliminary studies and further work is necessary
in order to optimize the reactor performance.
Acknowledgements
The authors express their acknowledgment to
Conacyt (project number 32539-T) and Servicios
Industriales Pen
˜oles (Monterrey, Me
´xico) for funding
this work. V. Reyes Cruz thanks Conacyt and
Servicios Industriales Pen
˜oles (Monterrey Me
´xico)
for his PhD scholarship.
References
Bennion, D., Newman, J., 1972. J. Appl. Electrochem. 2, 113.
Bindra, P., Light, D., Freudenthal, P., Smith, D., 1989. J. Electro-
chem. Soc. 136, 3616.
Brown, C.J., Plecher, D., 1992. J. Appl. Electrochem. 22, 613.
Brown, C.J., Plecher, D., 1993. J. Appl. Electrochem. 23, 38.
Brown, C.J., Plecher, D., 1994. J. Appl. Electrochem. 24, 95.
Caroli, S., Sharma, V.K., 1978. Tables of Standard Electrode Poten-
tials. Wiley, New York.
Chrzanowski, W., Li, Y.G., Lasia, A., 1996. J. Appl. Electrochem.
26, 385.
Coeuret, F., 1976. Electrochim. Acta 21, 203.
Coeuret, F., Storck, A., 1981. Inf. Chim. 210, 121.
Coeuret, F., Hutin, D., Gaunand, A., 1976. J. Appl. Electrochem. 6,
417.
Fleming, C.A., 1992. Hydrometallurgy 30, 127.
Jha, M.C., 1984. Proceedings of the First International Symposium
on Precious Metals Recovery, p. XXI– 1, Reno, NV. The Metal-
lurgical Society of AIME, New York, USA.
Kirk, D.W., Foulkes, F.R., Graydon, W.F., 1980. J. Electrochem.
Soc. 127, 672.
Kordosky, G.A., Sierakosky, J.M., Virnig, M.J., Mattison, P.L.,
1992. Hydrometallurgy 30, 291.
Mac Arthur, D.M., 1972. J. Electrochem. Soc. 119, 672.
Mughogho, D.T., Crundwell, F.K., 1996. In: Woods, R., Richard-
son, P.E. (Eds.), Electrochemistry in Mineral and Metal Process-
ing IV, PV 96-6. Electrochem. Soc. Pennington, USA, p. 275.
Olive, H., Lacoste, G., 1980. Electrochim. Acta 25, 1303.
Reyes, V. MSc Thesis, Universidad Auto
´noma Metropolitana-Izta-
palapa, Me
´xico D.F. (1998).
Reyes, V.E., Oropeza, M.T., Gonza
´lez, I., Ponce de Leo
´n, C., 2002.
J. Appl. Chem., in press.
Reyes, V., Oropeza, M.T., Gonza
´lez, I., Ponce de Leo
´n, C., 2000.
In: Oropeza, M.T., Gonza
´lez, I. (Eds.), Proceedings of XIV
Meeting of Sibae. Electroquı
´mica, Oaxaca, Me
´xico, p. 18.
Reyes, V.E., Oropeza, M.T., Gonza
´lez, I., Ponce de Leo
´n, C., 2001.
Hydrometallurgy. Submitted for publication.
Ringbom, A., 1963. Complexation in Analytical Chemistry, Wiley-
Interscience, New York.
Rojas, A., Ramı
´rez, M.T., Iba
´n
˜ez, J.G., Gonza
´lez, I., 1991. J. Elec-
trochem. Soc. 138, 1921.
Rojas, A., Trejo, G., Ramı
´rez, M.T., 1993. Diagramas de Zonas de
Predominio Aplicados al Ana
´lisis Quı
´mico. Universidad Auto
´n-
oma Metropolitana-Iztapalapa, Me
´xico D.F.
Stavart, A., Leroy, C., Van Lierde, A., 1999. Miner. Eng. 12, 545.
Trainham, J., Newman, J., 1977. J. Electrochem. Soc. 124, 1528.
Vilchis-Carbajal, S., Gonza
´lez, I., Lapidus, G.T., 2000. J. Appl.
Electrochem. 30, 217.
Waterman, B., Olson, F.A., Andersen, T.N., 1984. In: Srinivasan,
S., Woods, R., Richardson, P.E. (Eds.), Electrochemistry in
Mineral and Metal Processing I, PV 84-10. Electrochem. Soc.
Pennington, USA, p. 611.
Zhang, Y., Fang, Z., Muhammed, M., 1997. Hydrometallurgy 46,
251.
V. Reyes-Cruz et al. / Hydrometallurgy 65 (2002) 187–203 203
... The presence of copper in large quantities at the silver and gold cyanidation is harmful, especially if it is the largest in amount because therefore it will be the most precipitated [12], all cyanide experiments must be carried out in alkaline media (greater than 7 in pH) to avoid the formation of the toxic hydrogen cyanide gas [13]. ...
Article
Full-text available
The main objectives of this article were to firstly decrease the amount of sulfide in the (Volcanic Massive Sulfide –VMS) in the eastern Sudan (Ariab) area through a roasting pretreatment, secondly determine the best and optimum (thiosulfate concentration – ammonia concentration – copper sulfate concentration - leaching time – pH) for extracting silver sulfide metal (Ag2S) also known as argentite from the same ore, thirdly using sodium cyanide concentration equal to the optimum thiosulfate concentration obtained from the experiments to determine which solvent is better at the same concentrations thiosulfate or cyanide.The leaching process took place at different concentrations, times, following a roasting pre-treatment at (300–400-500–600-700 °C), The Analytics of (ICP) and (XRF) showed that silver concentration is (10.91 PPM), iron is (15.76 PPM) and copper is (119.16 PPM), and the (SEM) analysis showed that Sulfur is present in the proportion of (26 %) in the ore, and from the study of fractions it became clear that the highest presence of silver was at the size (-106 + 75) micron.It was found that the best roasting temperature was (700 °C), and the best extraction using sodium thiosulfate was (61.06 %) at thiosulfate concentration (0.2 M) and ammonia concentration (0.2 M), time (6) hours, copper sulfate concentration (0.05 M), pH (10) and pulp density (25 %) at room temperature. As for sodium cyanide at the same concentration (0.2 M), it was found that the extraction was (49.47 %) at time (6) hours, pH (10), and pulp density (25 %). At room temperature, it was clear that cyanide was less efficient at (0.2 M) concentration than thiosulfate in dissolving silver.
... The E eq,H2 equals to -0.709 V vs. SHE. The experimental potential of HER is influenced by the electrode material and the presence of Ag + metallic ions [75] , which consequently shift the HER potential. At more negative WE potentials (-0.8 --1.2 V vs. SHE), Ag deposition occurs simultaneously with water decomposition and the measured current density is a sum of current densities related to both the hydrogen evolution and silver electrodeposition. ...
Article
Herein, we report, for the first time, application of Ag nanowire array electrodes for electrocatalytic reduction of chloroform in an aqueous solution of 0.05 M KClO 4. The activity of this electrode was compared with a bulk Ag electrode, and the peak potential shifted up to 280 mV to less negative values, suggesting improved catalytic properties toward the reduction of chloroform. The template-assisted po-tentiostatic electrodeposition of Ag nanowires from a cyanide-based solution was optimized. Particularly, the influence of working electrode potential and duration of electrodeposition on the length of nanowires, passed electric charge, pore-filling rate, and current efficiency was studied. A highly reproducible and fast fabrication of anodic alumina templates was achieved by optimizing operating parameters of the voltage pulse detachment and duration of wet chemical etching.
... In the industrial solutions used in these hydrometallurgical processes, depending on the plant operation, trace amounts of noble elements such as silver (in the ppm range) are accompanied by a considerably higher concentration of less noble metals (in the g/L range), such as copper, iron, nickel [1]. Currently utilized silver recovery processes from such dilute solutions include several different methods such as cementation [2][3][4][5], chemical methods [6], precipitation [7], adsorption [8], membrane filtration [9] and electrowinning [10][11][12]. The typical issues when recovering silver from dilute industrial effluents by any method are in the solution complexity, high cost, high consumption of chemicals or high energy consumption of the process [13]. ...
Article
Full-text available
The electrodeposition-redox replacement (EDRR) process was studied to control the creation of copper and silver containing particles on the surface of a carbon nanotube film. Synthetic solutions simulating typical hydrometallurgical copper electrolysis process solutions (40 g/L Cu, 120 g/L H2SO4) with different dilute concentrations of silver (1–10 ppm) were utilized as the source for particle deposition and recovery. Such process solutions are currently underutilized for use as a potential source for the deposition of noble particles. The effect of deposition voltage, deposition time, stirring, and redox replacement time between deposition pulses were investigated as the parameters affecting the morphology and composition of the deposited particles as well as deposition kinetics. The results showed that pure copper particles can be deposited when the redox replacement time between deposition pulses is very short (t = 2 s). By increasing the redox replacement time (t = 50 s and more) the original copper particle composition transforms into a core-shell structure with an outer layer predominately consisting of silver or a bimetallic mix of copper and silver, depending on the deposition conditions. The bimetallic Cu/Ag particle size could be controlled from 200 to 840 nm by the applied deposition voltage. At high redox replacement times (t = 150 s and more) the resulting particles were shown to be pure silver with a small diameter from 100 to 250 nm.
Article
Efficient methods were proposed to improve the gold recovery from printed circuit boards (PCBs) in mobile phones. Gold was selectively extracted in the form of Au(S2O3)23− using Na2S2O3-CuSO4-NH3-O2/N2 system. Under optimal conditions (temperature: 25 °C; stirring: 200 rpm; O2/N2: 3.0/0.5 L/min; time: 3 h; Na2S2O3: 160 mmol/L; CuSO4: 120 mmol/L; NH3: 0.7 mol/L (pH 9.9); solid/liquid: 4 g/L), 98% of gold was extracted. The extracted gold was adsorbed by corncob-based activated carbon (CACw), which was prepared using pyrolyzed wood vinegar. The modification of CACw with mercaptobenzothiazole (MBT), forming MBT-CACw, which displayed maximum adsorption efficiency of 49.9 mg/g. The optimal pH for adsorption was found to be 7.5 at 40 °C with 0.2 mol/L (NH4)2S2O3. The adsorption was described by the pseudo-second-order model and the Freundlich isotherm, owing to the high affinity of MBT-CACw for the sulfur donor. Copper was eluted from the loaded MBT-CACw using 0.7 mol/L (NH4)2S2O3 followed by the gold elution with 40% v/v CH3OH. The two-step elution recovered 98.7% of copper and 97.6% of gold. These findings suggest that the oxygen-assisted extraction, combined with the adsorption conducted using low-cost, agriculture-based adsorbent and selective elution, is an eco-friendly approach to efficiently recovering gold from e-waste.
Article
In this paper, we proposed a combined leaching-electrowinning approach to recover Cu from AVR sediment. Firstly, speciation diagrams of the metal-cyanide (Cu, Zn and Fe) system were constructed using thermodynamic calculations. Afterward, leaching-electrowinning experiments were systematically conducted. The speciation calculations showed that CuSCN was converted into Cu-CN compounds when the CNT/Cu mole ratio exceeded 1.71. The cyanide ions complexed with Zn²⁺ were completely captured by Cu⁺ when the Cu/Zn mole ratio reached 5.0, yielding the formation of zinc hexacyanoferrate composite or Zn(OH)2 precipitation. Corresponding leaching results indicated that the selective Cu leaching from AVR sediment was realized with the leaching efficiency of 99%, forming Na2Zn3[Fe(CN)6]2 as the main ingredient of the residue at the optimal leaching conditions. Cyclic voltammetry tests suggested that cuprocyanide complexes were dominantly presented as [Cu(CN)2]⁻ complexes in the leachate (5680 mg/L, CNT/Cu mole ratio of 2.18), exhibiting much higher current density than that of [Cu(CN)3]²⁻ in the cyanide effluent. However, during the electrowinning process, [Cu(CN)2]⁻ were gradually converted into higher-order complexes, and the cathodic current efficiency decreased correspondingly. Ultimately, the Cu recovery of 92% was achieved with a current efficiency of 57% and energy consumption of 1.91 kW·h/kg Cu.
Article
The application of laboratory-generated biochar and activated carbon adsorbents in gold iodized solution for the recycling of waste mobile phone printed circuit boards (WMPCBs) is investigated. This research aims to solve problems associated with the existing gold recovery technologies of WMPCBs. Currently, the disposal of WMPCBs is expensive, involves complex processes, and contributes to secondary pollution. In this study, laboratory-generated biochar is produced from corn straw, wheat straw, and wood chips by pyrolysis. The effects of factors on the adsorption efficiency are investigated, and the optimal operating conditions for biochar and activated carbon adsorption are determined. The following optimal parameters were found for activated carbon: temperature = 25 °C, particle size = 40–60 mesh, dosage = 0.05 g/10 mL, pH = 7, reaction time = 2 h, and oscillation frequency = 200 r/min. The adsorption efficiency reached 98.6%. For biochar, optimization involved: raw material from corn straw at a pyrolysis temperature = 700 °C, reaction time = 5 h, oscillation frequency = 200 r/min, pH = 3, dosage = 0.15 g/10 mL, and temperature = 50 °C. An adsorption efficiency of 98% was achieved. The two adsorbents were compared, and results demonstrated that the adsorption properties of the laboratory-generated biochar were slightly inferior to those of the activated carbon; however, they were similar. Biochar adsorption can reuse waste, which may not only solve the current problems related to WMPCB recycling, but can help to achieve a “win-win” situation of increased environmental protection and sustainable utilization of resources.
Article
Iodine–iodide leaching is an effective and environmentally friendly gold extraction method that is expected to replace cyanidation. However, as the price of iodine is relatively high, for the industrial application of iodine–iodide leaching, decreasing the required amount of iodine is important to reduce production costs. In this study, persulfate was used to replace iodine as the oxidant for the extraction of gold from refractory gold ore. Using single-factor tests, the optimal leaching conditions were determined as a solid–liquid ratio of 1:3, a stirring speed of 350 rpm, 0.02 mol/L ammonium persulfate, and 0.1 mol/L potassium iodide. At pH 5, the gold extraction rate reached 83.69% after stirring for 1.5 h at room temperature. Even under neutral conditions, a gold extraction rate of more than 80% could be achieved. Using the activated carbon adsorption method to recover the gold from the leaching solution, a high gold recovery rate was obtained without solid–liquid separation. Compared with cyanidation, the S2O8²⁻ – I⁻ – H2O system has the advantages of nontoxicity, eco-friendly, a fast leaching speed, and a high gold extraction rate. Thus, this system was a promising alternative method for gold extraction from refractory ore.
Article
The recovery of metals from wastewater is a recurrent problem due to numerous productive activities that produce wastewaters rich in toxic metals. Within this context, this research presents the study and optimization of copper recovery of real wastewater using pulsed electrodeposition. The studied parameters - method, current, temperature, and rotation- influence both the removal of Cu and the composition of the formed deposit, noting that the variation of these parameters enables the removal of copper with formation from crystalline oxides to crystalline copper in its metallic form. The process was optimized, and a 33.59% copper removal from a real wastewater with a deposition efficiency of 84.36% in 30 min was deemed optimal, using fast galvanic pulse, ton = 1 ms, 190 mA, 70 rpm, and 37 °C. For coating in the optimum point, a metallic and crystalline copper with 100% purity was obtained.
Article
Attention deficit hyperactivity disorder (ADHD) is a heterogeneous disorder of unknown aetiology. It usually affects school-aged children with an estimated prevalence of 3 to 6%. ADHD is characterised by a core of symptoms that include short attention span, easy distractibility and social impulsivity. Stimulants continue to be the most efficacious and least toxic agents used to treat the disorder in the majority of children, and are the drugs of choice in children in whom cardiovascular status is questioned. Tricyclic antidepressants are also effective and are especially beneficial in individuals who are resistant to stimulants or in whom ADHD is accompanied by comorbid depression, anxiety, enuresis, tic disorders, substance abuse or sleep disturbance. Other antidepressants such as clorgiline (clorgyline), nortriptyline, fluoxetine and monoamine oxidase inhibitors have also been shown to reduce ADHD symptomatology. These agents may provide therapeutic options in the future. Adverse effects associated with stimulants include decreased appetite, insomnia, gastrointestinal upset, headache and potential growth suppression. Tricyclic antidepressants may cause drowsiness, anticholinergic effects and cardiovascular changes. Tolerance does not development with stimulants but may occur with tricyclic antidepressants.
Article
The use of carbon felt as a three-dimensional electrode appears to be very promising for the recovery of heavy metals, and toxic compounds removal from dilute solutions, considering its favourable physico-chemical properties: high specific surface area, good fluid permeability and compressibility, chemical inertness and good electrical conductivity.This work presents the contribution of the carbon felt electrode in two different steps of the gold cyanidation recovery process •- firstly as a cathode for the electrowinning of gold solution obtained after the elution of loaded carbon;•- secondly as an anode for the electro-oxidation of cyanide ions present at low concentration (200–300mg/l) in waste streams.In the first case, more than 10 kg of gold per m2 of felt (2000 kg of gold per m3 of felt) can be loaded at 400 A/m2 from dilute gold solutions (30 mg/l Au) with classic Faradic yields (6–12 %) and high overall extraction efficiency (>90 %). The felt homogeneously loaded with adhesive gold deposit can be smelted in an electric furnace without addition of fluxes since the carbon felt decomposes in gaseous products without formation of ashes.In the second case, the cyanide ion concentration can be lowered to as low as 10 mg/l by electro-oxidation to cyanate form (CNO−) at 400 A/m2 in the anodic compartment of a divided cell. The presence of copper ion significantly improves the current efficiency of this electro-oxidation and sharply reduces the oxidation of the carbon felt. Copper ions accelerate the oxidation rate of free cyanide ions through the formation of easily oxidizable complexes owing to a mechanism in which the Cull Cull redox couple acts as an electron transfer mediator.
Article
The guanidine ion pairing functionality, which exists in its protonated form at pH < 10.5, is introduced Reagents having this functionality are shown to be strong, and somewhat selective extractants for gold typical low-grade cyanide leach liquors. The gold is readily strip and concentrated at pH > 13.5. Continuous solvent extraction circuits, run in the laboratory and in the field, suggest that leach-SX-EW technology, so successfully applied in the copper industry, is technically feasible for gold.
Article
A one-dimensional model for flow-through porous electrodes operating above and below the limiting current of a metal deposition reaction has been developed. The model assumes that there is one primary reactant species in an excess of supporting electrolyte, and that a simultaneous side reaction may occur. The model predicts nonuniform reaction rates due to ohmic, mass-transfer, and heterogeneous kinetic limitations; the effects of axial diffusion and dispersion are included. Results are compared with the experimental data observed by various authors for the deposition of copper from sulfate solutions with the simultaneous generation of dissolved hydrogen. Satisfactory agreement between model predictions and experimental data on over-all reactor performance and deposit distributions has been accomplished. For an upstream counterelectrode, distributions of reaction rate (for both single and multiple reactions), concentration, and potential describe the detailed system behavior.
Article
The potential drop occurring in the bed of the flow-through porous electrode (fpe) changes the local metal-solution potential difference (lpd). Thus it may destroy the considered electrochemical reaction specificity or limit the electrolytic cell efficiency.So, it's necessary to compute the fpe geometry (bed height, particles diameter) which satisfies the lpd for a chosen pair flow-yield.This study, realized in the case of a fixed bed built with very conductive particles, proposes a generalized equations system which permits the fpe design. It's possible to do the same for an undistinguished electrochemical reaction by introducing a characteristic number of this system. From these equations a design diagram is established.A discussion about the axial field electrode limits as performing reactor follows.
Article
An analytical expression is given for the local metal—solution potential difference in a Percolating Porous Electrode working under limiting current conditions. The solution is obtained for the case where the general electrolyte flow direction is parallel to the current lines, for a given location of the current feeder and for an equipotential dispersed phase.This solution can be useful in using a PPE for determining mass transfer coefficients between a liquid and the particles of a fixed bed, as well as for the recuperation of metals from dilute solutions in potential conditions close to those of the diffusional regime.Metal-solution potential distributions have been determined experimentally as a function of the height in a percolating porous electrode made of high conducting grains which are fixed or fluidized. The results are discussed with respect to their variation with electrolyte flow rate.When the grains are fixed and for limiting current conditions in the whole bed, the experimental distributions are in excellent agreement with the calculated distributions.It is shown that a fluidized electrode should have a very low efficiency and that the problem of electrical conductivity in two-phase system is important in the application of solid—liquid fluidized beds in electrochemistry.
Article
A FMO1-LC parallel plate, laboratory electrochemical reactor has been modified by the incorporation of stationary, flow-by, three-dimensional electrodes which fill an electrolyte compartment. The performance of several electrode configurations including stacked nets, stacked expanded metal grids and a metal foam (all nickel) is compared by (i) determining the limiting currents for a mass transport controlled reaction, the reduction of ferricyanide in 1 m KOH and (ii) measuring the limiting currents for a kinetically controlled reaction, the oxidation of alcohols in aqueous base. It is shown that the combination of the data may be used to estimate the mass transfer coefficient, κL, and the specific electrode area, A e, separately. It is also confirmed that the use of three dimensional electrodes leads to an increase in cell current by a factor up to one hundred. Finally, it is also shown that the FM01-LC reactor fitted with a nickel foam anode allows a convenient laboratory conversion of alcohols to carboxylic acids; these reactions are of synthetic interest but their application has previously been restricted by the low rate of conversion at planar nickel anodes.
Article
It has long been known that gold deposits obtained from Co and Ni‐containing electrolytes are generally hard, while Pb and Tl‐containing electrolytes tend to give soft gold deposits. Yet the mechanism by which these additives affect the grain size is not fully known. This study was undertaken to investigate the effect of base metal inclusions on the deposition characteristics and the microstructure of electrodeposited gold films. The kinetic and mechanistic aspects of the gold deposition reaction were investigated using linear sweep voltammetry on a rotating disk electrode. A combination of electron microscopy and electron diffraction techniques was used to characterize the microstructure.
Article
The electrochemical behavior of gold in alkaline cyanide, citrate, and phosphate buffered solutions has been studied using cyclic voltammetry and galvanostatic transients. Two reaction paths were observed. At low overvoltage the reaction goes through an adsorbed intermediate. (rate determining) At larger overvoltages a direct transfer between the gold complex in solution and the metal atom was found on reduction. The reduction reaction was the same in all the solutions but in the phosphate and citrate baths the gold did not oxidize to a soluble species.