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The dissolution of magnetite in acidic oxalate solutions has been studied under various experimental condi-tions. The effects of temperature, pH, oxalate and ferrous ion concentration in solution were extensively examined. The dissolution of the magnetite is highly dependent on temperature and the pH of the solution, but is practically independent of the oxalate concentra-tion. The addition of ferrous ions in the solution has a positive effect on the dissolution rate, especially at lower temperatures and higher pH values. Magnetite, along with hematite, is a common impurity in var-ious industrial minerals and has to be partially removed to meet market specifications. Its removal can be effected by leaching in aqueous solutions of mineral or organic acids. The dissolution of iron oxides, such as magnetite and hematite, with organic acids comprises three steps:5 (1) acti-vation of the solid surface, which includes the generation of active centres and formation of surface complexes; (2) reduc-tive dissolution of active centres, which is characterized by a quite well-defined induction period-this step is accelerated by ferrous ions, which are transferred from the solid to the solution when bivalent iron occurs in the lattice; and (3) autocatalytic reductive dissolution of active centres. Of the various organic acids, oxalic acid has been found particu-larly effective and is widely used for dissolution ofiron.2 The aim of the work presented here was to study the effect of the most important operating parameters, such as tempera-ture, pH of the solution, initial ferrous ion concentration ih solution and oxalate concentration, on the dissolution of magnetite in acidic oxalate solutions so as to provide the basis for an industrial process suitable for the removal of iron from industrial minerals.
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Dissolution of magnetite in acidic oxalate solutions
M.Taxiarchou, D.Panias, I.Douni, I.Paspaliaris and A. Kontopoulos
Synopsis
The dissolution of magnetite in acidic oxalate solutions
has been studied under various experimental condi-
tions. The effects of temperature, pH, oxalate and
ferrous ion concentration in solution were extensively
examined. The dissolution of the magnetite is highly
dependent on temperature and the pH of the solution,
but is practically independent of the oxalate concentra-
tion. The addition of ferrous ions in the solution has a
positive effect on the dissolution rate, especially at
lower temperatures and higher pH values.
Magnetite, along with hematite, is a common impurity in var-
ious industrial minerals and has to be partially removed to
meet market specifications. Its removal can be effected by
leaching in aqueous solutions of mineral or organic acids.
The dissolution of iron oxides, such as magnetite and
hematite, with organic acids comprises three steps:5 (1) acti-
vation of the solid surface, which includes the generation of
active centres and formation of surface complexes; (2) reduc-
tive dissolution of active centres, which is characterized by a
quite well-defined induction period-this step is accelerated
by ferrous ions, which are transferred from the solid to
the solution when bivalent iron occurs in the lattice; and
(3) autocatalytic reductive dissolution of active centres. Of
the various organic acids, oxalic acid has been found particu-
larly effective and is widely used for dissolution ofiron.2
The aim of the work presented here was to study the effect
of the most important operating parameters, such as tempera-
ture, pH of the solution, initial ferrous ion concentration ih
solution and oxalate concentration, on the dissolution of
magnetite in acidic oxalate solutions so as to provide the basis
for an industrial process suitable for the removal of iron from
industrial minerals.
Experimental apparatus
All experiments were carried out in a 500-ml glass reactor
that was equipped with a thermostatically controlled heating
mantle connected to a mercury contact thermometer and a
mechanical stirrer incorporating a speed controller and fitted
with a glass impeller. A pH-meter with combined electrode
and a glass condenser were fitted to the glass reactor.
Since magnetite dissolution is a photochemical process,6-8
the experiments had to be performed under controlled light
conditions. Therefore, an isolated box was constructed to
contain two 15-W white-light sources. The experimental
apparatus was placed in the box and all the experiments were
conducted under similar visible-light conditions.
Manuscript first received by the Institution of Mining and
Metallurgy on 9 October, 1996; revised manuscript received on 29
January, 1998. Paper published in Trans. Instn Min. Metall. (Sect. C:
Mineral Process. Extr. Metall.), 107, January-April 1998. ~ The
Institution of Mining and Metallurgy 1998.
Experimental procedure
Initially, 400 ml of buffer H2C204-K2C204 solution with a
constant total oxalate concentration and preadjusted pH
value was heated in the glass reactor at a preselected tempera-
ture. The solution was agitated at a speed of 600 rev/min.
During the heating period the buffer solution was purged
with argon to avoid the oxidation of ferrous ions by the
dissolved oxygen. Ferrous ions were added to the solution in
the form of pure ammonium iron(n)-sulphate-6-hydrate
(Merck, 99%). A preweighed amount of dry, chemically pure
(Heraeus, 99.5%) magnetite powder was then added to the
solution to create a suspension with pulp density of 0.022%
(wtlvol).
In each test the total and bivalent iron concentrations in
solution were measured as a function of time. Total iron
chemical analysis was carried out by flame atomic absorption
spectroscopy with the use of a Perkin Elmer 2100 atomic
absorption spectrophotometer and bivalent iron chemical
analysis was carried out using a Hitachi UIIOO spectro-
photometer with 1,10-phenanthroline as a complexing
agent.9
Experimental results
Effect of temperature
Tests were conducted at 30, 50, 60, 70 and 80°C at a con-
stant pH of 3 and a total oxalate concentration of 0.3 M. The
iron dissolution is plotted as a function of time for these
temperatures in Fig. 1; for purposes of comparison iron dis-
solution from hematite I0 at 80°C has also been included. The
rate of dissolution is seen to be highly dependent on tempera-
ture. At 80°C dissolution is complete in less than 2 h,
whereas at 30°C only 57% of the iron has been dissolved after
5 h. At 30°C, in contrast to its form for the higher tempera-
tures, the dissolution curve is slightly concave, indicating that
the reaction rate increases with time. This is typical behaviour
of an autocatalytic reaction.
Plots of ferrous ion concentration in solution versus time at
different temperatures are presented in Fig. 2, along with the
results for hematite dissolution. The curves of ferrous ion
50
100 150 200
Time, min
2SO
300
Fig. I Total iron dissolution as function of time for different tem-
peratures (pH 3; oxalate concentration, 0.3 M)
C37
100
90
80
.30'C
..
70
c50.C
.3
"
80 .60.C
50
.70.C
:;
Jt
40
A80.C
30
.80.C, hematite
20
10
250 3IJO
50
100 150 200
Time. min
Fig,2 Ferrous ion concentration in solution as function of time for
different temperatures (pH 3; oxalate concentration, 0.3 M)
generation as a function of time are similar to those of iron
dissolution, indicating the dependence of the dissolution rate
on the rate of ferrous ion generation in solution. At 30°C the
ferrous ion dissolution rate is quite low, whereas at tempera-
tures between 50 and 80°C it is high. This correlation
between the ferrous ion concentration in solution and the
magnetite dissolution rate reveals the catalytic effect of fer-
rous ions on the magnetite dissolution process.
The same correlation between ferrous ion concentration in
solution and dissolution rate has been observed in the case of
hematite dissolution in acidic oxalate solutions under similar
conditions (80°C; pH 3; oxalate concentration, 0.3 M; pulp
density, 0.022%).10 The hematite dissolution curve in Fig. 1
has a typical sigmoidal form and is characterized by an induc-
tion period of approximately 3 h, during which ferrous ions
are slowly generated in the solution.
In the case of magnetite the sigmoidal shape of the dissolu-
tion curves is absent, but at 30°C the dissolution curve is
slighdy concave. Magnetite is a spinel that contains ferrous
and ferric ions in its lattice. These ferrous ions are easily
transferred from the lattice to the solution, as recorded in Fig.
2, to eliminate the induction period and the sigmoidal shape
of the dissolution curve.
Effect of pH
To evaluate the effect of pH a series of tests was carried out at
60°C, a total oxalate concentration of 0.3 Mand at pH values
between 1 and 5 (Fig. 3). The dissolution rate of magnetite
was affected significandy by pH. It was highest at pH 3 and
decreased in solutions with higher or lower acidity. The iron
dissolution curves at the other pH values have the same form
with the exception of pH 5. At pH 5 the dissolution curve is
characterized by an induction period. This indicates that the
acidity of the solution plays an important role in the dissolu-
350
50
100 150 200
Time, min
3IJO250
Fig.3 Total iron dissolution as function of time for different values
of pH (60°C; oxalate concentration, 0.3 M)
C38
c:: =
3IJO
350
50 100
150 200
Time, min
250
Fig. 4 Ferrous ion concentration in solution as function of time for
different values of pH (60°C; oxalate concentration, 0.3 M)
tion process and reduction of the hydrogen ion concentration
in solution drastically inhibits this process.
The level of bivalent iron in solution in the same tests is
plotted against time in Fig. 4. At pH 2 and 3 the rate of fer-
rous ion generation is approximately the same. In less acidic
solutions (pH >4) the ferrous ion concentration is signifi-
candy lower and it decreases as the pH increases. At these
DO
:1
I
60
- I
.30'C
50
t.3IJ
1
a 50-<:
1
A
A60'C
.pHI
If
.70'C
e 3IJ
.pH 2
20
t..
x80'C
If
ApH 3
loti/A'
a 80'C, hematite
20
ApH4
I
apH5
10
1:1
A
A
.
g :\
.pH I
.. 60
.pH2
"0
1:i 50
ApH3
:;;
" 40
ApH4
""
3IJ
apH5
20
10
t
Fe2+
'"
60
"
'(j
tft.
40
20
0
0
1 2
3
pH
4 5 6
7
(a)
003;
003
002;
'"
"
002
'(j
"
""
'"
005
tft.
001
0005
0
0 1
2 3 4
5 6 7
(b)
pH
00003;
00003
00002;
'"
"
00002
1
00005
tft.
00001
000005
or'
I
'--,
4
(c)
pH
Fig. 5 Speciation of ferrous ions in oxalatesolution as function of
pH (25°C; oxalateconcentration, 0.1 M)ll
high pH values the ferrous ion generation curves register an
induction period, which lengthens as the pH increases.
The behaviour of magnetite dissolution at different pH
values is typical of tWo pH-dependent and competing
phenomena that occur simultaneously during the dissolution
process.
The pH of the solution is a determining parameter for the
speciation of ferrous ions in an oxalate solution, as seen in
Fig. 5. In the ferrous ions-oxalic acid system the species
Fez+, Fe(CZ04)~- and Fe(CZ04)j are present. In strongly
acidic solutions the ferrous ions remain uncomplex. As the
pH increases the concentration of the Fe(CZ04)~- complex
ion also increases and at pH >2.5 all ferrous ions are in the
form ofFe(CZ04)~-. The presence of Fe(CZ04)j and all the
hydroxo complexes of bivalent iron can be ignored in view of
their very low concentration at all pH values. II Of the prin-
cipal ions present, only Fe(CZ04)~- can be adsorbed on the
solid surface.
The tWo competing phenomena are the adsorption of
hydrogen ions and that of complex Fe(CZ04)~- ions on the
surface of magnetite particles. The first creates surface active
centres and the second accelerates dissolution through these
active centres. These tWo phenomena are intensified under
extreme experimental conditions.
In strongly acidic solutions the concentration of the
Fe(CZ04)~- ions in the solution is very low and the amount of
the complex adsorbed is very small. As the pH increases the
number of surface active centres decreases, since the number
depends on the hydrogen ion concentration in the leaching
solution, and most of the Fe(CZ04)~- ions are adsorbed on
non-activated magnetite sites. As a result, the dissolution of
magnetite is inhibited.IZ Dissolution is optimized when the
solution is a compromise betWeen those favourable for the
competing phenomena; this has been established experimen-
tally at around pH 3.
Effect ofFe2+ addition in solution
The foregoing tests have shown that iron dissolution follows
the rate of ferrous ion generation in solution. To study the
behaviour of magnetite dissolution when ferrous ions are ini-
tially added in the oxalate solution one test was performed
with the addition of 10 mgll Fez+ at 70°C, constant pH 3 and
a total oxalate concentration of 0.3 M. The results were com-
pared with those of a similar test without the addition of
ferrous ions. Iron dissolution as a function of time for the tWo
50
100
Time, min
150
200
Fig. 7 Ferrous ion concentration in solution as function of time with
and without addition of bivalent iron in solution (70°C; oxalate
concentration, 0.3 M): diamonds, without Fe2+; blank squares, with
10 ppm Fe2+
tests is shown in Fig. 6. At the temperature studied the addi-
tion of ferrous ions increases the dissolution rate only in the
initial stages of the process. As the reaction proceeds the dis-
solution rate with and without the addition of ferrous ions
becomes the same. Similar behaviour is observed for the gen-
eration offerrous ions in the tWo tests (Fig. 7). Generation of
ferrous ions in the solution takes place in the first stage of the
reaction, so the existence of ferrous ions in the initial solution
eliminates this stage and accelerates the dissolution process.
As a result the time required for the complete dissolution of
magnetite is decreased from approximately 3 to 2 h.
As seen in Figs. 1 and 2, at low temperatures the genera-
tion of ferrous ions and, consequently, the magnetite
dissolution are characterized by a prolonged induction
period. When all these data are compared it can be deduced
that the effect of ferrous ion addition in solution is probably
more significant at lower temperatures, at which the dissolu-
tion of the ferrous ions in the magnetite lattice is more
difficult.
Effect of total oxalate concentration
The effect oftotal oxalate concentration on the dissolution of
magnetite was studied through a series of tests carried out at
60°C, constant pH 3 and total oxalate concentrations
betWeen 0.1 and 0.3 M. In the system studied a buffer solu-
tion was used; the total oxalate concentration is therefore
the sum of the oxalate concentrations of all oxalate species
300
Fig. 6 Total iron dissolution as function of time with and without
addition of bivalent iron in solution (70°C; pH 3; oxalate concentra-
tion, 0.3 M): diamonds, without Fe2+; blank squares, with 10 ppm
Fe2+
50 100 150 200
Time, min
250
Fig.8 Total iron dissolution as function of time for different oxalate
concentrations (60°C; pH 3)
C39
100
90
80
=
70
0
.....
....
..e
60
0
'"
'" 50
.....
'0
40
30
20
10
0
0
60
50
40
-
t;o
e
30
+
"'G)
20
10
100
90
eo
0:1
70
.S:
.a
:1 17/ I 1.0.lM
.
aO.2M
..,
.. 0.3M
30
50 100
150
200
20
10
Time, min
60
50
40
~
C 30
+
.
""
~ 20
.O.lM
aO.2M
A O.3M
10
50 100 150
Time, min
200 250
Fig. 9 Ferrous ion concentration as function of time for different
total oxalate concentrations (60°C; pH 3)
existing in the system. Iron dissolution and ferrous ion con-
centration in the solution are plotted against time in Figs. 8
and 9, respectively. It is clear that this variable has practically
no effect on the dissolution of magnetite or the generation of
bivalent iron in the solution. At a concentration of 0.1 M the
dissolution rate is slightly lower, without significant effect on
the system. This can be attributed to the slightly decreased
rate of ferrous ion generation in solution at this temperature.
Discussion
The present stUdy has shown that the rate of magnetite disso-
lution depends on the dissolution rate of ferrous ions
contained in the magnetite lattice. The ferrous ion dissolution
is affected significantly by temperature and the pH of the
solution. At low temperatures (30°C) and high pH values
(>3) the dissolution rate increases with time, indicating that
the reaction proceeds via an autocatalytic mechanism.
Under the experimental conditions studied the addition of
10 mg/l Fe2+ to the initial solution had the same effect on the
magnetite dissolution rate as an increase in the temperature
from 70 to 80°C, reducing the time for complete dissolution
by 30% (Figs. I and 6). When all the above data are taken
into account it is probable that the effect of ferrous ion
addition to the initial solution is more significant at lower
temperatures and in less acidic solutions, where dissolution of
the ferrous ions of the magnetite lattice is more difficult.
The pH of the solution, besides affecting the rate of ferrous
ion generation in solution, governs the activation of the
magnetite surface with adsorbed hydrogen ions and the
adsorption of Fe(C204)~- complex ions on surface active
sites. It is, therefore, a very important parameter for the dis-
solution of magnetite.
Finally, the total oxalate concentration in the solution,
although it has almost no effect on the dissolution process,
affects the speciation of the oxalate species and the concen-
tration of Fe(C204)~- ions in solution, which, in tUrn,
influences the adsorption of Fe(C204)~- ions on surface
active sites. The rate of this dissolution process is decreased
when the total oxalate concentration is decreased below 0.2 M
(Fig. 8).
Conclusions
An investigation was carried out into the effects on the disso-
lution of magnetite in oxalate solutions of temperature, pH of
the solution, initial ferrous ion concentration in solution and
oxalate concentration-these being the most important
parameters.
Magnetite dissolution is accelerated by dissolution of the
ferrous ions of the magnetite lattice. The ferrous ion disso-
lution rate is affected significantly by temperatUre. As the
C40
c:..:
temperatUre increases the dissolution rate also increases. At
30°C the dissolution is characterized by an induction period,
which is eliminated at higher temperatures.
The pH of the solution is very important for magnetite
dissolution because it affects: (1) the rate of ferrous ion disso-
lution, which is optimal at pH 2-3 and decreases in solutions
of lower or higher acidity; (2) the stage of activation of the
magnetite surface with adsorbed hydrogen ions; and (3) the
stage of adsorption of Fe(C204)~- complex ions on surface
active sites. The pH is also a determining parameter for speci-
ation in oxalate solutions that contain ferrous ions. Since the
effect of pH on one leaching stage is opposite to its effect on
another, a compromise has to be reached. The dissolution of
magnetite proceeds most rapidly at pH 3.
In the case of magnetite the addition of bivalent iron in the
oxalate solution has a positive effect on the dissolution rate in
the initial stages of the process, but as the reaction proceeds
the dissolution rates with and without the addition of ferrous
ions become the same. The addition of ferrous ions in the ini-
tial solution eliminates the stage of ferrous ion generation in
solution and, therefore, accelerates the overall dissolution
process. The effect of ferrous ion addition is probably more
significant at lower temperatures or high pH values, at which
the dissolution of lattice ferrous ions is more difficult.
The total oxalate concentration in solution has no serious
effect on the dissolution process, although the interaction
between oxalate speciation, oxalate concentration and pH
has to be taken into consideration for the optimization of
magnetite dissolution.
Acknowledge~ent
The financial support of the European Commission within
the framework of the Brite-Euram II Programme (contract
no. BRE2-CT92-0215) is gratefully acknowledged.
References
I. Baumgartner E. et ai. Heterogeneous electron transfer as a path-
way in the dissolution of magnetite in oxalic acid solutions. Inorg.
Chern., 22, 1983, 2224-6.
2. Blesa M. A. et ai. Mechanism of dissolution of magnetite by
oxalic acid-ferrous ion solutions. Inorg. Chern., 26(22), 1987,
3713-7.
3. Afonso M. et ai. The reductive dissolution of iron oxides by
ascorbate. J. CoiloidInterface Sci., 138, no. 1,74-82.
4. Torres R., Blesa M. A. and Matijevic;:E. Interactions of metal
hydrous oxides with chelating agents. IX. Reductive dissolution of
hematite and magnetite by aminocarboxylic acids. J. Colloid Interface
Sci, 134,no. 2,475-85.
5. Panias D. et ai. Mechanisms of dissolution of iron oxides in
oxalic acid. Hydrornetallurgy, 42, 1996, 257-65.
6. Cooper G. D. and DeGraff B. A. The photochemistry of the
monoxalatoiron(m) ion. J. phys. Chern., 76, 1972,2618-25.
7. Parker C. A. and Hatchard C. G. Photodecomposition of com-
plex oxalates. Some preliminary experiments by flash photolysis. J.
phys. Chern., 63,1959,22-6.
8. Patterson J. 1. H. and Perone S. P. Spectrophotometric and elec-
trochemical studies of flash-photolyzed trioxalatoferrate(m). J. phys.
Chern., 77,1973,2437-40.
9. Harvey A. E., Smart J. A. and Amis E. S. Simultaneous spec-
trophotometric determination of iron(n) and total iron with
1,10-phenanthroline. Analyt. Chern., 27,1955,26-9.
10. Taxiarchou M. et ai. Dissolution of hematite in acidic oxalate
solutions. Hydrornetallurgy,44, 1997, 287-99.
11. Panias D. et ai. Thermodynamic analysis of the reactions of
iron oxides dissolution in oxalic acid. Can. Metall. Q., 35, no. 4,
1996,363-73.
12. Panias D. et ai. Dissolution of hematite in acidic oxalate solu-
tions-Effect of ferrous ions addition. Hydrornetallurgy, 43, 1996,
219-30.
Authors
M. Taxiarchou is a mining and metallurgical engineer employed as
a senior researcher in the Laboratory of Metallurgy, National
Technical University of Athens (NTUA), where she gained her
Ph.D.
Address: Laboratory of Metallurgy, Department of Mining and
Metallurgical Engineering, National Technical University of Athens,
P.O. Box 640 56, 157 10 Zografos, Athens, Greece.
D. Panias is also a senior researcher of the Laboratory of
Metallurgy, NTUA, where he gained his Ph.D.
I. Douni is a researcher of the Laboratory of Metallurgy, National
Technical University of Athens, where she is undertaking work
towards a Ph.D.
I. Paspaliaris is a professor of the Laboratory of Metallurgy,
Department of Mining and Metallurgical Engineering, National
Technical University of Athens.
A. KontopouIos was a professor and director of the Laboratory of
Metallurgy, Department of Mining and Metallurgical Engineering,
National Technical University of Athens.
(:41
... However, the higher temperatures increased the rate of dissolution, because the higher temperature favored the formation of Fe 2+ ions in the solution, which in turn results in the increased rate of dissolution. Additionally, Taxiarchou et al. [44] found that the temperature had a significant effect on the rate of dissolution when dissolving magnetite in acidic oxalate solutions. They also noticed that the shape of the dissolution curve varied at different temperatures and, for example, the concave shape of the curve at 30 • C indicated the autocatalytic dissolution of magnetite. ...
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Ethylenediaminedisuccinic acid (EDDS) was used to dissolve magnetite reductively. Fe2+ ions increased the dissolution rate, and this increase depended on the solution acidity, temperature and [EDDS]:[Fe2+] ratios. The EDDS-Fe2+ complex was able to dissolve magnetite film coated on an iron surface. Iron metal enhanced the dissolution of magnetite from its surface. However, metal exposed to the solution suffered more corrosion than iron free of magnetite.
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Ethylenediaminedisuccinic acid (EDDS), a biodegradable substitute for EDTA, was used as a chelant for dissolving magnetite and magnetite formed on iron metal surface. Dissolution was found to increase in presence of ferrous ions and depend on pH of solution, concentration of ferrous ion, EDDS concentration, applied cathodic potential and temperature. The impedance spectrum for the dissolution of magnetite film formed on iron exhibited two time constants. The first at high frequency range is ascribed to the reductive dissolution of magnetite. It is very crucial to carry out the dissolution process at the appropriate temperature to insure complete removal of oxide layer.
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Iron oxide is the main contaminant of clay and silicate minerals used during the production of high quality ceramics. Its content has to be removed to generally less than 0.1% for achieving the required whiteness of 90% ISO or higher for clay and silicate materials. Oxalate has been used to dissolve iron oxide from various sources. The dissolution is affected by oxalate concentration, solution pH and temperature. The mineral phase is also critical in determining the reaction rate. Hematite is slow to dissolve whereas iron hydroxide and hydroxyoxides such as goethite and lepidocrosite can be easily dissolved. As the dissolution requires a pH controlled in the region 2.5–3.0 for maximum reaction rate, it is essential to create a hydroxide-oxalate mixture for use in the leaching process. The characteristics of NaOH-, KOH- and NH4OH-oxalic acid mixtures were also determined in this study. Due to the precipitation of salts such as Na2C2O4(s) and NaHC2O4(s) the NaOH-oxalic acid could act as pH buffer for the leaching. Such precipitation also reduces the concentration of the free bioxalate, HC2O4− required for the dissolution of iron oxide. KOH behaves the same as NaOH whereas NH4OH precipitates the less stable salt NH4HC2O4(s) which easily re-dissolves forming soluble oxalate species. Ammonium hydroxide is therefore the most suitable reagent that can be used for pH control during the leaching of iron oxide using oxalate. Using STABCAL, several Eh–pH and stability diagrams were developed to explain the dissolution process.
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The mechanism of dissolution of pure iron oxides by means of organic acids comprises two different chemical pathways: (a) non-reductive dissolution and (b) reductive dissolution. In this paper, the thermodynamic analysis of these pathways for the iron oxides-oxalic acid system is presented. In low acid solutions (pH higher than 3) the only thermodynamically stable complex ions of bivalent and trivalent iron are [Fe2+(C204)2]2- and [Fe3+(C204)3]3-. Uncomplexed Fe2+ ion can be identified only in high acid solutions, while uncomplexed Fe3+ ion is not likely to build-up in oxalic acid solutions. In the pH range1-2 the [Fe3+(C204)2]- and [Fe3+(C204)]+ ions are stable, while at pH less than 1, the [Fe3+HC204]2+ is the only ion existing.
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The dissolution of pure iron oxides by organic acids has been extensively reviewed. The mechanism of dissolution comprises three distinct steps: (1) adsorption of organic ligands on the iron oxide surface; (2) non-reductive dissolution; and (3) reductive dissolution. Reductive dissolu-tion involves two stages: an induction period and an autocatalytic period. The overall dissolution process is affected by the pH of the initial solution, temperature, the exposure of solution to UV radiation and the addition of bivalent iron in the initial solution.
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The dissolution of hematite in acidic oxalate solutions has been studied under various experimental conditions. The effect of temperature, oxalate concentration and pH on hematite dissolution were studied. In order to study the effect of atmospheric oxygen and light on the dissolution reaction, experiments were carried out in an inert atmosphere (purging with argon), in an ‘oxidising atmosphere’ (without purging), in the presence of visible light and in darkness. It was found that the dissolution process is much faster in an inert atmosphere under visible light. The dissolution process in all other cases was very slow, including a characteristic induction period, attributed to ferrous ion generation in solution through a heterogeneous, time-consuming reductive pathway. In an oxidising atmosphere the dissolution process is seriously retarded due to the oxidation of ferrous to ferric ions by the dissolved atmospheric oxygen. Iron dissolution is highly dependent on temperature and pH of the solution, while it is practically independent of the total oxalate concentration.
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Chelating agents, such as ethylenediaminetetraacetic acid (EDTA) and its thermal decomposition products [iminodiacetic acid (IDA), N(2-hydroxyethyl)iminodiacetic acid (HIDA)], and oxalic acid, enhance the dissolution of magnetite and hermatite at temperatures above 90°C. The mechanism involves three different processes: (a) acid dissolution assisted by the chelating agent, (b) reductive dissolution brought about by internal electron transfer between the ligand and the constituent Fe(III) ion complexes, followed by the released of Fe(II), and (c) additional autocatalytic dissolution by the ferrous-carboxylate complexes generated in solution by process (b). Hydrogen peroxide quenches pathway (c) by oxidizing dissolved Fe(II). The rates dissolution in the absence and in the presence of high H2O2 concentrations allow for the evaluation of the relative importance of (a) and (b). Hydrazine greatly accelarated the overall dissolution rates through direct heterogeneous redox interaction with the surface Fe(III) ions. In all cases magnetic is more reactive than hematite. Rate constants are calculated for the various dissolution pathways and, in the case of heterogeneous electron transfer, the values are compared with those for analogous homogeneous reactions.
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Spectrophotometric and electrochemical monitoring techniques have been used to follow the intermediates generated by the flash photolysis of trioxalatoferrate(III). The results indicate that there are competing initial photolytic processes followed by a sequence of three secondary reactions. In the first, an oxidizable iron(III) diradical species, formed by the flash, disappears by a rapid first-order reaction. The rate of disappearance of the second intermediate is dependent on the iron(III) oxalate concentration. The third step in the mechanism produces the final product, dioxalatoferrate(II). Of the three sequential steps, only the reaction of the second intermediate can be followed photometrically and has been reported previously. The initial and final reactions can be monitored conveniently electrochemically. The reaction sequence proceeds to completion in less than 1 sec.
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The photochemistry of the monoxalatoiron(III) ion in aqueous perchloric acid with and without excess Fe3+ was studied by kinetic spectroscopy. Deaerated solutions of Fe(C2O4)+ flash irradiated in the charge-transfer spectral region display absorbance changes distinctly characterized by the time scale on which they occur. The initial decay, complete within 50 μsec, is controlled by the rate of photolysis and is due to the primary photoredox and reactions of the resulting ·C2O4- free radical with Fe(C2O4)+, Fe3+, or itself. Subsequent absorbance changes are the result of the decomposition of the product of the ·C2O4- + Fe(C2O4)+ reaction and, for experiments using excess Fe3+, the anation of Fe(III) by HC2O4-. In contrast to the bis- and trisoxalatoferrate (III) ions, photoaquation is not a significant primary process. Quantitative kinetic values are reported for the various reactions.
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Long-lived intermediates have been observed in solutions of the ferrioxalate, cobaltioxalate and uranyl oxalate ions when they are subjected to flash photolysis. The compound produced in neutral ferrioxalate solutions disappears at a rate which is nearly independent of the concentration of ferrioxalate. Under these conditions, therefore, the rate controlling stage is not the expected bimolecular reaction between radical and ferrioxalate, and the simple reaction scheme originally proposed is not sufficient to explain the results. Some possible additional rate-controlling stages have been considered including dissociation of an excited ferrioxalate ion (or ferrous-radical complex) and dissociation of a complex between ferric iron, oxalate ion and oxalate radical. Oxygen is found to intervene directly in the photochemically initiated reaction chain, not only in neutral solution, but also in acid solution where, with high concentrations of ferrioxalate and continuous irradiation at low intensity, it has little effect. As examples of systems involving efficient electron transfer reactions, both cobaltioxalate and uranyl oxalate as well as ferrioxalate are worth much more detailed investigation.
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The kinetics of the reductive dissolution of magnetite by ferrous ions in solutions of high oxalate concentration has been studied at 30°C and various pH values. The rate-determining step is proposed to be the outer-sphere electron transfer from FeII(C2O4)22-, located in the Stern plane, to a surface oxalate-iron(III) complex. Analysis of the work term and electron-transfer Gibbs energy shows that FeII(C2O4)22- is a reasonable choice for the reductant species. Dissolution also requires protonation of the surface sites, in a process described by a Freundlich-type isotherm.
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The dissolution of metal oxides is a process of importance in several fields such as hydrometallurgy, passivity of metals, and cleaning of boilers and metal surfaces in general. Oxalic acid is one of the most effective reagents for dissolution of magnetite under mild acid conditions. Magnetite is the oxide that confers passivity to steel surfaces. In the present communication, the more salient features of the mechanism of dissolution of magnetite by oxalic acid solutions are discussed with special focus on the role played by ferrous ions in the process. Oxalate plays an unique role among complexing carboxylic ligands in the dissolution of magnetite; it not only facilitates the electron-transfer reaction but also mediates in a relatively fast dissolution during the initial induction period (the induction period is much shorter than in the case of the dissolution of magnetite by ethylenediaminetetraacetic or nitrilotriacetic acid). This unique role has been used in the development of a very efficient scale removal formulation used in the decontamination of nuclear power plants.
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Studies on the dissolution of hematite in acidic oxalate solutions have shown that there is a strong relationship between dissolution rates and ferrous ion generation in the solution. The effects of temperature, pH of the solution, oxalate and ferrous ions concentration on the dissolution of hematite in acidic oxalate solutions containing ferrous ions were studied. It was found that the pH of the solution is very important for the dissolution as it affects: (1) the activation of hematite surface with adsorbed hydrogen ions; (2) the adsorption of [Fe(C204)2 ]2- complex ions on surface active sites and (3) the speciation in oxalate solutions containing ferrous ions. Iron dissolution is highly dependent on temperature and ferrous ion concentration, while it is practically independent of the total oxalate concentration. The dissolution of hematite in oxalate solutions comprises three stages: (1) activation of the solid surface; (2) generation of ferrous ions in the solution (induction period); and (3) an autocatalytic dissolution period. When ferrous ions are added, the induction period is eliminated and dissolution proceeds through the autocatalytic pathway.