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Effect of polyacrylic acid in restoring
chalcopyrite an molybdenite flotation
Ian Wark Research InstituteAustralian Research Council Special Research Centre
For Particle and Material Interfaces
Maria Sinche Gonzalez, D. Fornasiero
and M. Zanin
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Water in mineral processing
Dissolved ases
water
Organic compounds(reagents, micro-organism) Suspended solids
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0.5
0.6
0.7
0.8
0.9
threcovery
0.55
0.6
0.65
0.7
0.750.8
0.85
Overall
recovery
Water quality in flotation
0.4 0.5 0.6 0.7 0.8 0.9
0.1
0.2
0.3
0.4
Collection zone recovery
Fr
o
0
0.05
0.1
0.15
0.2
0.25
0.3
0.35
0.4
0.45
.
Water quality can affect both
froth zone and collectionzone
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Metal ions in solution may depress the
sulphide minerals
- Collection Zone Issues -
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HypothesisMI in solution can:
Precipitate as hydroxide on the surface of Cp and Mo particles,
reducing the overall hydrophobicity and contact angle
Reduce the surface charge of Cp and Mo particles to less negative,
The addition of a charged organic dispersant (PAA) may be beneficial
in preventing/reversing metal ion deposition on the surface of Cp
and Mo
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Al3+
Mg2+
Mn2+
Ca2+
Al3+
Mg2+
Mn2+
Ca2+
Metal hydroxide may form in solution at
typical plant pH (9.3)
pH of hydroxide formation:
FeMn
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MoS2 is negatively charged
MI adsorption reduces the negative
charge and improves floatability
BUT
Increases potential to aggregate with
negatively charged gangue particles
MoSMoS22
MoSMoS22++
CaCa2+2+
MoSMoS22+SiO+SiO22
MoSMoS22+Ca+Ca2+2++SiO+SiO22
MI may favor slime coatings on molybdenite
Zanin et Al., 2010AMIRA P260E
7
Can dispersants counteract ??
Raghavan & Hsu (1984)
MoS2+
--
+
+
-
+
-
SiO2
Ca2+ adsorbed
at the edges
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Experimental approach
amplifier
computer
Single minerals: Chalcopyrite -75+38 um
Molybdenite -250+150 um
zeta potential(Malvern Zetasizer Nano)
detachment force
(related to CA)batch flotation
50 Hz
Effect of Fe, Al and Mn
investigated
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40
60
80
100
veMorecovery%
No metal ionsFeAlMn
Mn
Flotation response in the presence of MI
Chalcopyrite Molybdenite
40
60
80
100
veCurecovery%
No metal ionsFeAlMn
Al Fe
0
20
0 1 2 3 4 5 6 7 8 9
Cumulati
Time (min)
Fe
Effect of metal ions (10-4 M) on chalcopyrite and molybdenite recovery as a
function of flotation time at pH 9.3 ([KNO3] =10-2 M)
0
20
0 1 2 3 4 5 6 7 8 9
Cumul
ati
Time (min)
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Cum
ulativeMo
recovery%
10
20
30
40
50
60
70
80
Cum
ulativeMo
recovery%
10
20
30
40
50
60
70
80
Cum
ulativeCu
recovery%
20
30
40
50
60
70
80
90
Cum
ulativeCu
recovery%
20
30
40
50
60
70
80
90
Effect of metal ions and PAA in flotationChalcopyrite Molybdenite
No
m
etalions
Fe3x10-5
/
8.2x10-7
Fe10-4
/
0
Fe10-4
/4.1x10-7
Al3x10-5
/
4.1x10-7
Al3x10-5
/0
Al10-4
/0
Mn
2x10-5
/4.1x10-7
Fe3x10-5/0
Fe10-4
/2.1x10-7
Al3x10-5
/
8.2x10-7
Al10-4
/
2.1x10-7
Al10-4
/
10-6
Mn
2x10-5/0
Mn
10-4
/0
Mn
10-4
/2.1x10-7
Mn
10-4
/4.1x10-7
Fe3x10-5
/
1.2x10-6
Metal ions (M) / PAA (M)
0
No
m
etalions
Fe3x10-5
/
8.2x10-7
Fe10-4
/
0
Fe10-4
/4.1x10-7
Al3x10-5
/
4.1x10-7
Al3x10-5
/0
Al10-4
/0
Mn
2x10-5
/4.1x10-7
Fe3x10-5/0
Fe10-4
/2.1x10-7
Al3x10-5
/
8.2x10-7
Al10-4
/
2.1x10-7
Al10-4
/
10-6
Mn
2x10-5/0
Mn
10-4
/0
Mn
10-4
/2.1x10-7
Mn
10-4
/4.1x10-7
Fe3x10-5
/
1.2x10-6
Metal ions (M) / PAA (M)
0
No
m
etalions
Fe2x10-5/0
Fe2x10-5
/2.1x10-6
Fe2x10-4
/0
Fe2x10-4
/1.1x10-6
Fe2x10-4
/2.1x10-6
Al2x10-5
/
2.1x10-6
Al2x10-5
/
0
Al2x10-5
/
5x10-5
Al10-4/
0
Al10-4
/
2.1x10-6
Al10-4
/
5x10-5
Metal ions (M) / PAA (M)
0
No
m
etalions
Fe2x10-5/0
Fe2x10-5
/2.1x10-6
Fe2x10-4
/0
Fe2x10-4
/1.1x10-6
Fe2x10-4
/2.1x10-6
Al2x10-5
/
2.1x10-6
Al2x10-5
/
0
Al2x10-5
/
5x10-5
Al10-4/
0
Al10-4
/
2.1x10-6
Al10-4
/
5x10-5
Metal ions (M) / PAA (M)
0
Effect of PAA on chalcopyrite and molybdenite recovery in presence of
Fe, Al and Mn ions (pH 9.3)
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-20
-10
0
10
20
30
potential(mV)
(2)
(3)
(1)
b
-20
-10
0
10
20
30
potential(mV)
(2)
(3)
a
Zeta potential in the presence of MI
Chalcopyrite Molybdenite
Zeta potential of Mo, Cp and freshly prepared Fe(OH)3 10-4 and PAA, pH =9.3
-70
-60
-50
-40
-30
0 1 2 3 4 5 6 7 8 9 10 11
z
et
pH
Cp
Cp + PAA 10-5 M
Fe(OH)3 10-4M
Fe(OH)3 10-4 M + PAA 10-5 M
Cp + Fe(OH)3 10-4M
Cp + Fe(OH)3 10-4 M +PAA 10-5 M
-70
-60
-50
-40
-30
0 1 2 3 4 5 6 7 8 9 10 11
z
et
pH
MoMo +PAA 10-5 MFe(OH)3 10-4MFe(OH)3 10-4M + PAA 10-5 MMo + Fe(OH)3 10-4MMo + Fe(OH)3 10-4 M +PAA 10-5 M
(1)
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Measurement of the detachment force
Xu et Al., 2010AMIRA P260E
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5.0E-06
1.0E-05
1.5E-05
2.0E-05
2.5E-05
3.0E-05
3.5E-05
Detachmen
tforce(N)
aIncreasingcollector
IncreasingPAA
5.0E-06
1.0E-05
1.5E-05
2.0E-05
2.5E-05
3.0E-05
IncreasingPAA
etachmentForce(N)
Particle-bubble detachment force: Fe nitrate and PAA
Chalcopyrite Molybdenite
0/
0/1
0/
0/
0.
5
0/
0/
0
2x10-5/
0/
0
2x10-5/
0/
0.
5
2x10-5/
2..
1x10-06/
0.
5
2x10-5/
4.
2x10-06/
0.50.0E+00
Fe ion concentration (M)/ PAA concentration (M) /collector concentration
0/
0
/0
.5
3x10-5/
0/
0.
5
3x10-5/
8.
2x10-07/0.
5
6x10-5
/0/
0.
5
6x10-5/
8.
2x10-07/0.5
6x10-5/
1.
2x10-06/0.
50.0E+00
Fe ion concentration (M)/ PAA concentration (M) /
collector concentration
Detachment force for chalcopyrite and molybdenite particle-bubble in thepresence of Fe nitrate and PAA, at pH 9.3
(*1= 2 g/t SIPX for CuFeS2, and *1= 22 g/t diesel oil for MoS2)
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Particle-bubble detachment force: Al nitrate and PAA
5.0E-06
1.0E-05
1.5E-05
2.0E-05
2.5E-05
5.0E-06
1.0E-05
1.5E-05
2.0E-05
2.5E-05
3.0E-05b
IncreasingPAA
Chalcopyrite Molybdenite
2x10-5/
4.
2x10-06/
0
.5
2x10-5/
0/
0
.5
2x10-5/
6.2
x10-6
/0
.5
0/
0/
0
.5
0.0E+00
Al ion concentration (M)/ PAA concentration(M) /collector concentration
0/
0/
0
.5
3x10-5/
0
/0
.5
6x10-5/
0/
0
.5
6x10-5
/8.
2x10-07/
0
.5
6x10-5
/1.
6x10-06/
0.50.0E+00
Al ion concentration (M)/ PAA concentration(M) /collector concentration
Detachment force for chalcopyrite and molybdenite particle-bubble in thepresence of Al nitrate and PAA, at pH 9.3
(*1= 2 g/t SIPX for CuFeS2, and *1= 22 g/t diesel oil for MoS2)
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Conclusions
Al and Fe ions decrease CuFeS2 and MoS2 flotation recovery,zeta potential and attachment force.
Changes in zeta potential suggest adsorption/precipitation ofmetal hydroxide on the mineral surface of CuFeS2 and MoS2decreasing particles hydrophobicity.
po yacry c ac restore t e otat on o c a copyr te
and molybdenite when Fe, Al and Mn were present at
concentration
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Acknowledgements
The authors acknowledge the financial support of:
Australian Research Council (ARC)
Sponsors of the AMIRA International P260E project
Thank you!