UNDERSTANDING READER RESPONSE THEORY Mrs. Leach AP Literature Chapel Hill High School.
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![Page 1: Solvent Extraction (SX) reagent selection for high temperature, high acid, high chloride and high Cu concentration leach solution at Port Pirie and its.](https://reader036.fdocuments.us/reader036/viewer/2022062304/56649d0b5503460f949deb14/html5/thumbnails/1.jpg)
Solvent Extraction (SX) reagent selection for high temperature, high
acid, high chloride and high Cu concentration leach solution at Port
Pirie and its impact on electrowinning
ByP. Crane, M. Urbani, K. Dudley, A. Horner and M. Virnig
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Nyrstar Port Pirie Smelter
• The smelter is situated 230km north of Adelaide in South Australia on the Spencer Gulf.
Courtesy Google
Port PirieBroken Hill
Rich lead deposit
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The smelter was built on a natural harbour allowing ease of product export
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History: The smelter has been processing lead concentrates since 1889, after the ore field in Broken Hill was discovered.
Much expansion occurred during the 1950s and 1960s.
Zinc production commenced in 1967
Copper production commenced in 1984
Production Capacity: Lead – 235,000 Tonnes
Zinc – 45,000 Tonnes
Silver – 11.5 million troy ounces (357 Tonnes)
Gold - 16,000 million troy ounces (497 kilos)
Sulphuric Acid – 80,000 Tonnes
Copper – 4,500 Tonnes
Background
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NPPS New Copper Inputs (tpa)
Lead Concentrates
71%
External Zinc
Residues
External Lead
Residues17%
4338 T
1041 T
12%711 T
Copper plant Feedstock mainly sourced from lead concentrates
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NPPS Copper Process
• Copper is recovered from the lead furnace in the form of a matte, which is treated in the copper plant
• The Copper recovery process employs a unique mixed chloride-sulphate leach technology (formerly known as the BHAS process) developed by BHAS engineers.
• This aggressive chloride-assisted leach is followed by conventional Cu SX / EW processes operated under fairly harsh conditions.
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Matte from CDF
Leach (primary and secondary)
Solvent Extraction
Residue/Neutralisation
Milling
Residue back to Sinter Plant
Electrowinning
Basic NPPS Copper Plant CircuitProcess description
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•Ball Mill and Feed Hopper
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Grinding• A conventional ball mill in closed circuit with a spiral classifier, treating 12,000 tpa
matte.
• Product goes to Primary Leach after thickening and storage.
To leach
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Overall leach chemistry (effect of chloride not shown)
Cu2S + PbS + H2SO4 + 4H+ + 3/2 O2 PbSO4 + 2Cu2+ + 2S + 3H2O
Black Acid
PLS to Clarifier
Leach Thickener Underflow
PLS Underflow
Primary
Secondary To Neutralisation then Sinter Plant
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•Leach Reactors
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• Thickener U/F from 1st stage leach at 35-40% solids is pumped to a one-stage repulp reactor.
• Salt, white acid and Oxygen added.
• 4-5 hrs residence time.
• 2nd stage leach discharge washed with raffinate in a repulp mixer.
• Polysil added in repulp mixer for silica control, and Magnafloc added to Repulp Thickener as a settling aid.
• Repulp slurry is thickened; solids are sent to neutralisation and return to the sinter plant, whilst liquids go to 1st stage leach.
2nd Stage Leach and washing
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•Salt addition to repulp reactor
NaCl prevents precipitation of CuS from Cu+ and S0.
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•Preg Clarifier
•Leach Thickener
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Was
hin
g
Str
ipp
ing
PregnantLeach Solution
Raffinate
Ext
ract
ion
SpentElectrolyte
AdvanceElectrolyte
Wash Water
Cu2+
Impurities
E1
E2
S2
S1
Cu2+
Cu2+
Cu2+
aqueous
organic
aque
ous
organic
organic
organic
organic
aqueous
aqueous
aqueous
Wash Water
• Conventional 2E x 1W x 2S circuit.
Copper SX
• Pregnant Leach Solution (PLS) containing approx. 40 g/L Cu, 20 g/L acid and 20 g/L Cl- at >40 deg C.
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•SX Mixer-settlers, S1 and S2
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Spent Electrolyte to S2 after cooling
Advance Electrolyte
• Two stage cascade systems in series with 15 cells per unit.
• Each cell has capacity for 40 stainless steel or titanium cathodes and 41 antimonial lead anodes
• Cathodes and anodes are connected to two 10,000A rectifiers.
Electrowinning
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•Cell house
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The use of the highly effective chloride – sulphate leach process results in several challenges for the operation of the Cu SX-EW plant, namely it:
• Produces a hot PLS, high in acid, chloride and copper content;
• Requires effective silica control and solids liquid separation;
• Requires a high SX extractant concentration and high O/A ratios;
• Requires careful monitoring of organic health and regular, effective, organic treatment.
Process Difficulties
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Cognis visited Port Pirie in mid 2003 to view the plant operation and offer technical assistance. Main observations:
• Operating with high concentration of Acorga® M5640 (C9 aldoxime with TXIB modifier) and high O/A ratio.
• No phase separation under Organic Continuous conditions Forced Aqueous Continuous operation.
• Evidence of silica-based crud.
• Re-oximation stage due to high reagent degradation rate.
• Viscous organic with dark colouration after strong acid strip.
• High entrainment and resultant high Cl transfer to electrolyte (consistently >200 ppm Cl in electrolyte) titanium plates.
• Poor atmospheric environment in EW (low levels Cl2 gas).
Cognis Involvement
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In August 2003, a sample of Port Pirie plant organic was analysed in Cognis’ Tucson laboratory. The main findings were:
• Extremely poor OC phase break >15 minutes at 25C
• Slow stripping kinetics – 62% after 30 sec (typically 95%)
• High nitro-C9 aldoxime level (16.2 % of total oxime)
• Excessive levels of hydrolysis product (aldehyde)
• High TXIB : C9 aldoxime ratio (0.38 compared to 0.28 in Acorga M5640)
• Presence of 2-cyano-4-nonylphenol and 5-nonylsalicylamide
• The organic did not respond to clay treatment
Cognis Involvement, cont.
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33%(v/v) LIX® 674N-LV in SX 12 after a few load strip cycles then completely stripped.Note the clarity.
Stripping tests indicated the scale of the problem
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33%(v/v) LIX® 674N-LV in SX 12 after a few load strip cycles then completely stripped.
Port Pirie plant sample completely stripped – 4 contacts with 250 g/L acid, O/A 2:1.
Red colour warning signs of nitration
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NO2 +
OH
H
R
NOH
O2N
R
H
OH NOH
C9 Aldoxime Nitro C9 Aldoxime
HNO3 + H NO2 + H2O
Requires acid, nitrate and high ORP
Nitration of oximes
Catalysed by presence of modifiers (Virnig, et. al. Copper2003)
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Stripped organic phases of all modified reagents: LIX 622N, M5640 and LIX 84-I + TDA; were red in colour
Effect of Modifiers
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
0 10 20 30 40 50Days
% (w
/v) A
ldeh
yde
or K
eton
eLIX 622N M5640 LIX 984N LIX 84-I LIX 84-I & TDA
Aldoxime + TDA
Aldoxime + TXIB
Ketoxime + TDA
Ketoxime + Aldoxime
Ketoxime
Effect of modifiers on oxime degradation in presence of nitrate
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Cognis Manufactured Oximes
C9H19
OH
C
N
OH
CH3
C9 Ketoxime
C9H19
OH
C
N
OH
H
C9 Aldoxime
C12H25
OH
C
N
OH
H
C12 Aldoxime
© Copyright, Cognis Corporation, 2005
Acorga M5640 (incl. TXIB modifier) LIX 984
INCREASING REAGENT STABILITY
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• Cease re-oximation of the organic, since:
– Re-oximated organics demonstrate poor physical performance
– Re-oximated organics are typically difficult to clean up
– Hydroxylamine may have been at least a partial source of the nitrogen oxide species
Cognis recommendations
Recommendations were all intended to improve the physical state and the performance of the organic phase.
• Convert reagent to a more stable non-modified reagent type to:
– Reduce rate of nitration
– Reduce rate of degradation
– Reduce viscosity of organic phase
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Port Pirie accepted the Cognis offer.
LIX 984 was selected because:
• 50/50 blend of LIX 84-I (ketoxime) and LIX 860-I (C12 aldoxime), both of which are more stable than the C9 aldoxime present in Acorga M5640.
• LIX 984 contains no modifier Modifiers promote nitration.
• LIX 984 showed good chemical performance in initial screening tests.
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Pre-LIX reagent addition plant profile (April 2004)
• Cu Mass balance OK
• High oxime concentration (43%(v/v))
• Low Cu net transfer (0.14 g/L Cu / % oxime)
• Low % Cu max load
• Laboratory PDT’s – aqueous continuous - 126 seconds, organic continuous - no separation after 15 minutes
• Again clay treatment had no effect, organic not filterable
• Extremely high viscosity (26.5 cSt compared to 3.9 cSt for fresh LIX reagent at 43%(v/v)
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Acorga addition stopped in April 2004 and LIX addition commenced.
Regular plant monitoring involved:
• Chemical composition –C9 and C12 aldoxime, ketoxime, TXIB, hydrolysis and nitration products
• Chemical performance – Cu recovery, % Cu ML, Cu net transfer (g/L Cu / % oxime), extraction and stripping kinetics
• Physical performance – Plant PDTs, mixer continuity, temp, laboratory PDTs, Effect of clay treatment, viscosity
• Monitoring the Cl- concentration in the electrolyte
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CONCENTRATION OF REAGENTS IN NPPS PLANT ORGANIC SINCE THE ADDITION OF LIX REAGENT
-
5
10
15
20
25
30
35
40
45
50
55
60
65
70
75
80
5/1/
04
8/1/
04
11/1
/04
2/1/
05
5/1/
05
8/1/
05
11/1
/05
2/1/
06
5/1/
06
8/1/
06
11/1
/06
2/1/
07
5/1/
07
8/1/
07
11/1
/07
2/1/
08
5/1/
08
Month
% o
f T
ota
l Co
mp
on
ents
by
Vo
lum
e
TXIBC9 AldoximeC12 AldoximeKetoximeC9 nitro aldoximes
Conversion rate tracked by decline in TXIB content
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Parameter
Survey Date
May-04
Nov-04
Jan-05Jun-05
Nov - 06
Apr - 07
Oct - 07
Sept - 08
PLS Cu(g/L) 41.0 45.8 44.6 42.3 45.0 51.9 32.0 45.2
Raffinate Cu(g/L) 12.9 15.4 13.9 15.0 15.5 14.8 8.1 10.9
Cu recovery (%) 68.5 66.4 68.8 64.5 65.6 70.7 65.5 75.8
Reagent Conc. (vol%) 45.0 34.0 30.0 25.8 32.6 33.5 33.3 30.0
Net Transfer (g/L Cu/vol%) 0.150 0.220 0.234 0.255 0.229 0.273 0.174 0.211
% max load 59.0 66.4 65.5 83.9 81.5 88.2 65.5 74.6
Plant chemical performance
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Parameter
Survey Date
May-04
Nov-04
Jan-05Jun-05
Nov - 06
Apr - 07
Oct - 07
Sept - 08
PLS Cu(g/L) 41.0 45.8 44.6 42.3 45.0 51.9 32.0 45.2
Raffinate Cu(g/L) 12.9 15.4 13.9 15.0 15.5 14.8 8.1 10.9
Cu recovery (%) 68.5 66.4 68.8 64.5 65.6 70.7 65.5 75.8
Reagent Conc. (vol%) 45.0 34.0 30.0 25.8 32.6 33.5 33.3 30.0
Net Transfer (g/L Cu/vol%) 0.150 0.220 0.234 0.255 0.229 0.273 0.174 0.211
% max load 59.0 66.4 65.5 83.9 81.5 88.2 65.5 74.6
Plant chemical performance
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Parameter
Survey Date
May-04
Nov-04
Jan-05Jun-05
Nov - 06
Apr - 07
Oct - 07
Sept - 08
PLS Cu(g/L) 41.0 45.8 44.6 42.3 45.0 51.9 32.0 45.2
Raffinate Cu(g/L) 12.9 15.4 13.9 15.0 15.5 14.8 8.1 10.9
Cu recovery (%) 68.5 66.4 68.8 64.5 65.6 70.7 65.5 75.8
Reagent Conc. (vol%) 45.0 34.0 30.0 25.8 32.6 33.5 33.3 30.0
Net Transfer (g/L Cu/vol%) 0.150 0.220 0.234 0.255 0.229 0.273 0.174 0.211
% max load 59.0 66.4 65.5 83.9 81.5 88.2 65.5 74.6
Plant chemical performance
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Kinetics Aug 03 Jul 05 Mar 06 Jun 06 Dec 06 Feb 07 Sept 08
Extraction @ 30 sec
- - 86 % 90 % 90 % 96 % 92%
Strip @ 30 sec
62 % 71 % 78 % 90 % 92 % 96 % 97%
Laboratory extraction and stripping kinetics
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Date PDT (seconds)
OC AC
Apr 2004 No break 126
Jan 2005 No break 130
July 2005 No break 110
October 2005 >600 90
March 2006 >600 72
June 2006 600 100
December 2006 600 93
February 2007 474 109
April 2007 114 201
Oct 2007 49 26
Feb 2009 90 30
Laboratory PD tests using plant organic and plant PLS.
Plant physical performance
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Extraction (OC) sec Strip (AC) (sec)
Pre CT Post CT Pre CT Post CT
April 04 No break No break - -
March 06 920 22 72 20
June 06 627 22 100 20
PD time before and after clay treatment.
Apr 04
Sep 04
Jan 05
Jul 05 Oct 05
Mar 06
Jun 06
Dec 06
Feb 07
May 08
Sept 08
Visc @ 25oC (cSt)
26.48 19.43 15.06 15.13 13.15 13.90 12.20 9.50 8.93 7.72 6.66
Viscosity of the plant organic
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Chloride in electrolyte (and PLS)
0
20
40
60
80
100
120
140
160
180
200
3/04
/04
31/0
8/04
28/0
1/05
27/0
6/05
24/1
1/05
23/0
4/06
20/0
9/06
17/0
2/07
17/0
7/07
14/1
2/07
12/0
5/08
9/10
/08
Ch
lori
de
in e
lec
tro
lyte
(m
g/L
) a
nd
re
pu
lp O
/F (
g/L
)
0
10
20
30
40
50
60
70
80
90
100
Pe
rce
nt
LIX
re
ag
en
t in
cir
cu
it (
%)
Cl in electrolyte
Cl in repulp O/F
Percent LIX in circuit
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EW Chloride vs TXIB in organic
0
20
40
60
80
100
120
140
160
180
200
3/04
/04
31/0
8/04
28/0
1/05
27/0
6/05
24/1
1/05
23/0
4/06
20/0
9/06
17/0
2/07
17/0
7/07
14/1
2/07
12/0
5/08
9/10
/08
Ch
lori
de
in e
lec
tro
lyte
(m
g/L
) a
nd
re
pu
lp O
/F (
g/L
)
0
3
6
9
12
15
18
21
24
27
30
TX
IB -
Pe
rce
nt
of
tota
l re
ag
en
t in
cir
cu
it
Cl in electrolyte
Cl in repulp O/F
TXIB (Percent of total reagent component)
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• reduction in reagent concentration to <35vol% (now at 30%).
• improvement in extraction and strip kinetics.
• higher net transfer (>0.2gplCu/vol%).
• very significant improvement in phase separation behaviour.
• organic phase viscosity reduced by 75%.
• very significant decrease in chloride transfer to EW.
• reduction in electrolyte chloride level by ~90%.
• much easier plant operation.
Conclusions
The conversion of Acorga modified reagent to the more stable LIX non-modified reagent resulted in:
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Acknowledgements
Nyrstar Port Pirie
Cognis
Co-authors and investigators: Kym Dudley, Mark Urbani, Dr Michael Virnig and Anissa Horner
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Questions?