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CYANEX ® <strong>272</strong><br />

Extractant


2 CYANEX <strong>272</strong> Extractant<br />

Solvent Extraction Reagent<br />

• Selective for cobalt over nickel<br />

from sulfate and chloride media.<br />

• Selective for zinc in the presence<br />

of calcium and cobalt.<br />

• Extracts other metal cations.<br />

INTRODUCTION<br />

CONTENTS<br />

Chemical Structure .............................................................................3<br />

Typical Properties ...............................................................................3<br />

Stability ...............................................................................................3<br />

Solubility Losses .................................................................................4<br />

Toxicity ...............................................................................................4<br />

Suitability of Construction Materials ..................................................4<br />

COBALT RECOVERY<br />

Cobalt Nickel Selectivity .....................................................................5<br />

Sulfate Solution (Table 1) ............................................................5<br />

Chloride Solution (Table 2) ..........................................................5<br />

Calcium Rejection ...............................................................................6<br />

Cobalt Extraction Isotherm.................................................................6<br />

Cobalt Loading ...................................................................................6<br />

Scrubbing Isotherm ............................................................................7<br />

Stripping Isotherms ............................................................................7<br />

Using H 2 SO 4 (Table 7) .................................................................7<br />

Using HCl (Table 8) ......................................................................7<br />

Continuous Separation of Cobalt from Nickel in<br />

Sulfate Solution ..................................................................................7<br />

Effect of Process Variables on Cobalt-Nickel<br />

Separation Factor ...............................................................................8<br />

Effect of Temperature (Table 9) ...................................................9<br />

Effect of Equilibrium pH (Table 10)..............................................9<br />

Effect of Diluent Aromaticity (Table 11) ......................................9<br />

Effect of Phase Modifier (Table 12) .............................................9<br />

OTHER POTENTIAL APPLICATIONS<br />

Diluent Oxidation and Prevention ....................................................10<br />

Recovery from Ammoniacal Solutions (Table 13) ............................10<br />

Extraction from Single Metal Sulfate<br />

Solutions (Table 14) .........................................................................10<br />

Extraction from Single Metal Chloride<br />

Solutions (Table 15) .........................................................................11<br />

ANALYTICAL METHODS<br />

In Organic Solvents by Titration .......................................................13<br />

In Organic Solvents by Gas Chromatography ..................................14<br />

In Aqueous Solutions by Gas Chromatography ...............................15<br />

HEALTH AND SAFETY ..............................................15


INTRODUCTION<br />

CYANEX ® <strong>272</strong> extractant has proven to be the reagent of choice for<br />

the separation of cobalt from nickel from both sulfate and chloride<br />

media. It is now being used to produce a major portion of the<br />

world’s cobalt.<br />

Since the active component of CYANEX <strong>272</strong> extractant is a<br />

phosphinic acid, metals are extracted through a cation exchange<br />

mechanism. Although CYANEX <strong>272</strong> extractant is selective for<br />

cobalt in the presence of nickel, a variety of other cations can also be<br />

extracted depending upon the solution pH.<br />

CYANEX <strong>272</strong> extractant is totally miscible with common aromatic<br />

and aliphatic diluents, and is extremely stable to both heat and<br />

hydrolysis.<br />

Chemical Structure<br />

The active component of CYANEX <strong>272</strong> extractant is<br />

bis(2,4,4-trimethylpentyl)phosphinic acid.<br />

CYANEX <strong>272</strong> Extractant<br />

Typical Properties<br />

Bis(2,4,4-trimethylpentyl)phosphinic acid 85%<br />

3<br />

Appearance Colourless to light<br />

amber liquid<br />

Molecular Weight 290 g/Mol<br />

Specific Gravity at 24ºC 0.92<br />

Viscosity, Brookfield at 25ºC 142cp<br />

50ºC 37cp<br />

Solubility in distilled H 2 O at pH 2.6 16 μg/ml<br />

Stability<br />

pH 3.7 38 μg/mL<br />

Boiling Point >300°C<br />

Pour Point -32°C<br />

Flash Point, closed cup >108ºC<br />

Specific Heat @ 52°C 0.48 cal/gm/°C<br />

Thermal Conductivity 2.7 x 10-4<br />

cal/cm/sec/°C<br />

The hydrolytic stability of CYANEX <strong>272</strong> extractant was examined<br />

in several tests which involved equilibrating the reagent with<br />

aqueous cobalt-nickel sulfate solutions at pH 5 and 50°C.<br />

The experimental procedure involved contacting the aqueous and<br />

organic phases in a stirred vessel for one week and then stripping<br />

the organic phase with sulfuric acid. The solvent was subsequently<br />

returned to the vessel for a further one week contact with a fresh<br />

aqueous solution. The procedure was repeated for a total contact<br />

time of four weeks.<br />

Analysis by titration and 31<br />

P NMR failed to detect any degradation<br />

of the reagent, nor were any statistically significant changes in<br />

cobalt-nickel selectivity observed.<br />

Furthermore, no degradation has been detected in plants which have<br />

been operating continuously for as long as 25 years.


4 CYANEX <strong>272</strong> Extractant<br />

Solubility Losses<br />

Losses of CYANEX <strong>272</strong> extractant by distribution to aqueous<br />

cobalt-nickel sulfate solutions were determined in a number of<br />

shake-out tests. The effect of two variables, pH and aqueous phase<br />

salt concentration, was studied.<br />

Aliquots of the organic and aqueous phases were contacted for<br />

5 minutes at 50ºC and A/O = 1. After coalescence, the aqueous<br />

phases were analyzed for CYANEX <strong>272</strong> extractant using a gas<br />

chromatographic procedure. The solvent was composed of 12 v/o<br />

CYANEX <strong>272</strong> extractant in Kermac* 470B diluent. Ammonium<br />

hydroxide was used for pH adjustment. The results of the extractant<br />

solubility (truly dissolved data) are given below.<br />

Aqueous Composition (g/l) CYANEX <strong>272</strong><br />

Ni Co Total Salt Equilibrium Extractant<br />

Conc. pH Solubility<br />

(μg/ml)<br />

100 2 300 3-5 0.5-1.5<br />

25 25 133 4.6 2<br />

5.3 2<br />

6.2 2<br />

5 5 27 4.6 3<br />

5.5 8<br />

6.5 25<br />

___________________________________________<br />

The solubility losses follow the general pattern expected of an acidic<br />

extractant. Distribution to the aqueous phase was found to be<br />

proportional to pH and inversely proportional to salt concentration.<br />

As can be seen, the losses are not excessive and this is corroborated by<br />

operating plant experience where total annual losses from both solubility<br />

and entrainment are approximately 10-15% of the solvent inventory.<br />

Toxicity<br />

The acute oral (rat) and acute dermal (rabbit) LD 50 values for<br />

CYANEX <strong>272</strong> extractant are >3.5 g/kg and >2.0 g/kg, respectively.<br />

The product produced only limited to mild eye and skin irritation<br />

during primary irritation studies with rabbits. The acute LC 50 , (96<br />

hr) for the bluegill sunfish and rainbow trout are 46 mg/L and 22<br />

mg/L, respectively. When CYANEX <strong>272</strong> extractant was assayed for<br />

mutagenic potential in the Ames Salmonella Test, it was determined<br />

to be non-mutagenic.<br />

CYANEX <strong>272</strong> extractant is considered as a non-toxic material.<br />

* A product of Kerr McGee Refining Corp.<br />

Suitability of Construction Materials<br />

Metals: Samples of stainless steel (304 and 316), mild steel and<br />

aluminum in the form of coupons (approximate dimensions 50mm<br />

x 20mm x 3mm) were immersed in capped jars for 8 1 /2 months at<br />

50°C (temperature was maintained only during working hours). No<br />

corrosion was observed in the three steel samples but aluminum<br />

exhibited minimal corrosion at a rate of 1 mil/year.<br />

Plastics and Rubbers: Samples of various plastics and rubbers were<br />

immersed in CYANEX <strong>272</strong> extractant and kept at 50°C for a total<br />

of 424 hours. The following observations were made:<br />

Material Remarks<br />

Butyl Rubber Unsuitable. Increase in dimensions<br />

and softening.<br />

Teflon Fluorocarbon Film** Suitable. No measured effect.<br />

Polypropylene Suitable. No measured effect.<br />

Natural and Black Latex Unsuitable. Complete dissolution<br />

in less than 192 hours.<br />

PVC Laboratory Grade Short term suitability. Loss of<br />

plasticity in less than 192 hours.<br />

PVC Solvent Grade Suitable. Only small change in<br />

dimensions observed.<br />

Red Gum Rubber Unsuitable. 100% increase in<br />

weight and dimensions and<br />

softening.<br />

Viton Fluoroelastomer** Suitable. No measured effect.<br />

Silicon Unsuitable. Disintegrated after 56<br />

hours.<br />

EPDM Unsuitable.<br />

** Dupont Dow Elastomers


CYANEX <strong>272</strong> Extractant<br />

5<br />

COBALT RECOVERY<br />

Cobalt-Nickel Selectivity<br />

The results of batch shake-out tests showing the effect of pH on<br />

Co-Ni selectivity from both sulfate and chloride media are given in<br />

Tables 1 and 2, respectively.<br />

TABLE 1 – SULFATE SOLUTION<br />

Solvent (v/o) 12% CYANEX <strong>272</strong> extractant, 5%<br />

isodecanol in Kermac 470B diluent<br />

Aqueous (g/l) 1.96 Co, 98.0 Ni as sulfates<br />

Temperature 50°C<br />

Contact Time 5 minutes<br />

A/O 1<br />

pH Control NH 4 OH<br />

% Extraction Equilibrium Separation<br />

Co Ni pH Factor<br />

21.5 0.04 3.8 700<br />

43.7 0.08 4.2 1000<br />

88.0 0.37 5.3 2000<br />

96.7 1.05 5.7 2700<br />

100 1.81 6.1<br />

TABLE 2 – CHLORIDE SOLUTION<br />

Solvent (v/o) 10% CYANEX <strong>272</strong> extractant, 5%<br />

isodecanol in Kermac 470B diluent<br />

Aqueous (g/l) 0.88 Co, 1.76 Ni as chlorides<br />

Temperature 50°C<br />

Contact Time 5 minutes<br />

A/O 1<br />

pH Control NaOH<br />

% Extraction Equilibrium Separation<br />

Co Ni pH Factor<br />

2.9 0.1 3.2 40<br />

54.2 0.3 4.0 370<br />

98.1 7.0 5.1 680<br />

99.7 30.0 5.5 680<br />

99.9 72.9 6.2 650


6 CYANEX <strong>272</strong> Extractant<br />

Calcium Rejection<br />

Unlike other organophosphorus cobalt extractants, CYANEX <strong>272</strong><br />

extractant will extract cobalt preferentially to calcium when both are<br />

present in the same feed stream. This performance characteristic is<br />

demonstrated in Table 3 and Figure 1.<br />

TABLE 3 – CALCIUM REJECTION IN THE PRESENCE OF<br />

COBALT AND NICKEL<br />

Solvent (v/o) 15% CYANEX <strong>272</strong> extractant, 10%<br />

p-nonylphenol in Kermac 470B diluent<br />

Aqueous (g/1) 1.60 Co, 77 Ni, 0.31 Ca as sulfates<br />

Temperature 50°C<br />

Contact Time 5 minutes<br />

A/0 1<br />

pH Control NH 4 OH<br />

% Extraction Equilibrium<br />

Co Ni Ca pH<br />

3.1 0 0.95 1.99<br />

17.2 0.04 1.24 3.34<br />

54.3 0.17 3.33 3.85<br />

91.7 1.03 12.0 4.84<br />

98.3 3.95 25.7 5.72<br />

100 13.4 5.16 6.63<br />

FIgURE 1<br />

Cobalt Extraction Isotherm<br />

Procedural details and results of our extraction studies are given in<br />

Table 4.<br />

TABLE 4<br />

Solvent (v/o) 12% CYANEX <strong>272</strong> extractant,<br />

5% isodecanol in Kermac 470B diluent.<br />

Aqueous (g/1) 5 Co as sulfate<br />

Temperature 50°C<br />

Equilibrium pH 5.0±0.1<br />

pH Control 1N NaOH<br />

Equilibrium Cobalt Concentration (g/l)<br />

A/O Solvent Aqueous<br />

10 6.32 4.68<br />

5 6.13 4.13<br />

2 5.54 2.58<br />

1 2.72 0.06<br />

The actual loading capacity of this solvent was 6 g/l cobalt, whereas<br />

the stoichiometric capacity is approximately 10 g/l cobalt.<br />

Cobalt Loading<br />

Loading studies were carried out at 50°C and pH 6.0 ± 0.1. The<br />

pH was controlled by the addition of ammonia. Other details and<br />

results are shown in Table 5.<br />

TABLE 5<br />

Solvent (v/o) 30% CYANEX <strong>272</strong> extractant in<br />

Kermac 470B diluent<br />

Aqueous (g/l) 10 Co as sulfate<br />

Theoretical Maximum (g/l) Approximately 24<br />

Contact Time 5 minutes<br />

Co % of Theoretical<br />

A/O in Solvent (g/l) Maximum<br />

0.5 5 21<br />

1.0 10 42<br />

1.5 15 63<br />

3.0 23* 96<br />

5.0 23* 96<br />

*At this loading the solvent was judged to be too viscous for practical use. The 15 g/l<br />

solvent did not exhibit this viscosity problem. The maximum practical loading for the<br />

conditions cited is probably about 65-75 % of theoretical. This would correspond to a<br />

CYANEX <strong>272</strong> extractant:cobalt ratio of 6:2.


It should be noted that the loading capacity of CYANEX <strong>272</strong><br />

extractant will vary depending upon several parameters, notably pH,<br />

temperature, and extractant concentration, and may be more or<br />

less than the figure cited. For example, with a 15% CYANEX <strong>272</strong><br />

extractant solution at 50°C and pH 5-5 the solvent can be loaded<br />

to 100% of the theoretical maximum while remaining sufficiently<br />

mobile for practical use.<br />

Scrubbing Isotherm<br />

As can be seen from the results in Table 6, even if a high quantity of<br />

nickel is co extracted with the cobalt, it can be successfully scrubbed<br />

from the loaded solvent.<br />

TABLE 6<br />

Solvent (v/o) 12% CYANEX <strong>272</strong> extractant,<br />

5% isodecanol in Kermac 470B diluent<br />

Solvent Loading (g/1) 1.9 Co, 1.9 Ni<br />

Scrub Feed (g/1) 30 Co (as sulfate), initial pH 3.7<br />

Temperature 50°C<br />

Equilibrium Concentration<br />

in Scrubbed Solvent (μg/ml)<br />

O/A Co Ni Co-Ni Ratio<br />

10 3820 4.5 850<br />

5 3790 2.2 1720<br />

2 3740 1.3 2900<br />

1 3730 1.1 3400<br />

Stripping Isotherms<br />

Stripping from a solvent modified with isodecanol tended to<br />

produce hazing. Substituting p nonylphenol or TBP for the<br />

isodecanol essentially eliminated this problem.<br />

Tables 7 and 8 show stripping isotherms obtained with a<br />

p-nonylphenol modified solvent.<br />

CYANEX <strong>272</strong> Extractant<br />

7<br />

TABLE 7 – USINg H 2 SO 4<br />

Solvent (v/o) 12% CYANEX <strong>272</strong> extractant,<br />

10% p-nonylphenol in Kermac 470B<br />

diluent<br />

Solvent Loading (g/l) 3.26 Co (2 μg/ml Ni)<br />

Temperature 40°C<br />

Contact Time 5 minutes<br />

Strip Feed (g/1) 20.5 Co (as sulfate), 24.5 H 2 SO 4<br />

Equilibrium Cobalt Conc. (g/l)<br />

O/A Solvent Aqueous<br />

6.67 0.58 38.4<br />

5 0.22 35.7<br />

4 0.19 32.5<br />

3.33 0.03 31.3<br />

2.86 0 29.8<br />

2 0 27.0<br />

TABLE 8 – USINg HCl<br />

Solvent (v/o) 12% CYANEX <strong>272</strong> extractant,<br />

10% p-nonylphenol in Kermac 470B<br />

diluent<br />

Solvent Loading (g/1) 9.26 Co<br />

Temperature 50°C<br />

Contact Time 5 minutes<br />

Strip Feed (g/1) 19.4 Co (as chloride) 100 HCl<br />

Equilibrium Cobalt Conc. (g/l)<br />

O/A Solvent Aqueous<br />

2 0 37.9<br />

3 0 47.1<br />

5 0 65.7<br />

7.5 0.01 88.8<br />

10 0.35 108.5<br />

Continuous Separation of Cobalt from Nickel in<br />

Sulfate Solution<br />

In continuous countercurrent tests (four extraction and two scrub<br />

stages) carried out at Warren Spring Laboratory (Stevenage, U.K.),<br />

more than 99.5% of the cobalt in the feed was recovered as a<br />

product containing a Co-Ni ratio of greater than 1000 to 1.


8 CYANEX <strong>272</strong> Extractant<br />

The experimental conditions are shown below. A circuit flowsheet<br />

and the relevant assays are given in Figure 2.<br />

Solvent (v/o) 20% CYANEX <strong>272</strong> extractant (NH4<br />

salt)*, 10% p-nonylphenol in the diluent<br />

MSB 210**<br />

Aqueous Feed (g/l) 2 Co, 100 Ni as sulfates, 20<br />

(NH 4 ) 2 O 4 , pH 5<br />

Scrub Feed (g/l) 40 Co as sulfate, pH 3<br />

Temperature 50°C<br />

Phase Ratios Extraction A/O = 2<br />

Scrubbing O/A = 32<br />

Mixer Residence Time 3.5-4 minutes (Based upon total<br />

liquid flow)<br />

*The phosphinic acid contained in the solvent was converted 70% to the ammonium<br />

salt by reaction with concentrated ammonium hydroxide solution (S.G. = 0.88). A<br />

phase modifier was used since converting more than 50% of the free acid to a salt<br />

+ +<br />

(NH4 or Na ) usually requires a modifier to prevent third phase formation.<br />

** A product of Shell Chemical Co.<br />

Effect of Process Variables on Cobalt-Nickel<br />

Separation Factor<br />

The effect of pH, temperature and diluent aromaticity on the<br />

cobalt-nickel separation factor in sulfate solutions was measured<br />

in a series of statistically designed tests and the data fitted to the<br />

following mathematical model:<br />

log 10 S = 1.8827 + 0.0332T + 0.01249A + 0.0033PT -<br />

0.002151PA - 0.0003405T 2<br />

Where:<br />

FIgURE 2 – CONTINUOUS TESTINg OF CyANEx <strong>272</strong> ExTRACTANT<br />

S = Co Ni Separation Factor<br />

T = Temperature (ºC)<br />

A = % Aromatics in diluent<br />

P = Equilibrium pH


The effect of these process variables on the separation factor is<br />

shown in Tables 9 through 11.<br />

TABLE 9 – EFFECT OF TEMPERATURE<br />

Solvent (v/o) 22% CYANEX <strong>272</strong> extractant in the<br />

diluent (95% MSB 210* diluent, 5%<br />

Aromatic 150** diluent).<br />

Aqueous (g/l) 2 Co, 100 Ni as sulfates<br />

pH 5.5<br />

A/O 1<br />

Co-Ni Separation Factor Temperature °C<br />

* A product of Shell Chemical Co.<br />

**A product of Exxon Co., USA.<br />

1320 30<br />

1850 35<br />

2480 40<br />

3220 45<br />

4000 50<br />

4790 55<br />

5510 60<br />

TABLE 10 – EFFECT OF EQUILIBRIUM pH<br />

Temperature 50°C<br />

Diluent (v/o) 95% MSB 210, 5% Aromatic 150<br />

Other Conditions See Table 9<br />

Co-Ni Separation Factor pH<br />

2810 4.5<br />

3010 4.7<br />

3230 4.9<br />

3470 5.1<br />

3730 5.3<br />

4000 5.5<br />

CYANEX <strong>272</strong> Extractant<br />

TABLE 11 – EFFECT OF DILUENT AROMATICITy<br />

Temperature 50°C<br />

Diluent (v/o) 100% MSB 210 (aliphatic) to<br />

pH 5.5<br />

100% Aromatic 150<br />

Other Conditions See Table 9<br />

Co-Ni Separation Aromaticity<br />

Factor v/o<br />

3970 0<br />

4030 10<br />

4090 20<br />

4160 30<br />

4220 40<br />

4280 50<br />

4350 60<br />

4420 70<br />

4480 80<br />

4550 90<br />

4620 100<br />

9<br />

The effect of the phase modifiers TBP, p-nonylphenol, isodecanol<br />

and TOPO (tri-n-octylphosphine oxide) on the separation factor is<br />

shown in Table 12.<br />

TABLE 12 – EFFECT OF PHASE MODIFIER<br />

Extractant (v/o) 22%<br />

Modifier 10 v/o (TBP, isodecanol,<br />

p-nonylphenol) 10 w/o TOPO<br />

(solid)<br />

Aqueous (g/l) 10 Co, 100 Ni as sulfates<br />

A/O 1<br />

Temperature 55°C<br />

Equilibrium pH 5.5<br />

Contact Time 5 minutes<br />

Diluent MSB 210<br />

Co-Ni Separation<br />

Modifier Factor<br />

None 6700<br />

TBP 3400<br />

p-Nonylphenol 1800<br />

Isodecanol 1000<br />

TOPO 1000


10 CYANEX <strong>272</strong> Extractant<br />

OTHER POTENTIAL APPLICATIONS<br />

Diluent Oxidation and Prevention<br />

Hydrocarbon diluents oxidize readily to carboxylic acids in the<br />

presence of a cobalt (Co 2+ ) catalyst. The formation of carboxylic<br />

acids, which are active nickel extractants, can seriously reduce the<br />

cobalt-nickel selectivity obtained with CYANEX <strong>272</strong> extractant.<br />

However, inhibitors such as BHT can be used to prevent this<br />

oxidation. Plants following this practice have run for many years<br />

without loss of selectivity.<br />

Recovery from Ammoniacal Solutions<br />

CYANEX <strong>272</strong> extractant can be used to recover cobalt from<br />

ammoniacal as well as acidic solutions. The data in Table 13 show<br />

that it outperforms other organophosphorus extractants.<br />

TABLE 13 – ExTRACTION FROM AMMONIACAL<br />

SOLUTIONS<br />

Solvent (v/o) 20% extractant, 5% isodecanol in<br />

Kermac 470B diluent<br />

Aqueous (g/L) 0.97 Co 3+ , 0.95 Ni 2+ , (NH4 ) 2SO4 for<br />

2-<br />

a total SO4 concentration of 16<br />

Temperature 50°C<br />

pH Control 11.6 with NH 4 OH<br />

Contact Time 5 minutes<br />

A/0 1<br />

% Extracted Co/Ni<br />

Extractant Co Ni Separation Factor<br />

CYANEX <strong>272</strong> 91.5 15.6 58<br />

PC-88A 91.4 22.0 18<br />

D2EHPA 90.4 46.9 7<br />

Although CYANEX <strong>272</strong> extractant is designed primarily for cobaltnickel<br />

separations, the data in Tables 14 and 15, and Figures 3 and<br />

4 show that it will extract a variety of metal cations and indicate its<br />

potential for other selective separations.<br />

TABLE 14 – ExTRACTION FROM SINgLE METAL SULFATE<br />

SOLUTIONS<br />

Solvent 0.6 M CYANEX <strong>272</strong> extractant, 10 v/o<br />

p-nonylphenol in Kermac 470B<br />

diluent<br />

Aqueous 0.015 M metal as sulfate<br />

Temperature 50ºC<br />

pH Control NH 4 OH or H 2 SO 4 as appropriate<br />

Contact Time 5 minutes<br />

A/O 1<br />

Metal % Ext. Final pH Metal % Ext. Final pH<br />

8.8 0.25 27.6 6.33<br />

23.6 0.85 36.0 6.59<br />

Fe 3+ 61.2 1.33 Ni 2+ 52.3 6.72<br />

88.1 1.75 84.0 7.22<br />

98.7 2.31 92.8 7.47<br />

14.6 0.90 14.5 3.00<br />

24.2 1.42 29.7 4.20<br />

Zn 2+ 53.3 1.88 Mg 2+ 67.1 4.76<br />

87.7 2.40 82.0 4.99<br />

99.4 3.08 97.4 5.81<br />

6.4 1.73 23.9 1.11<br />

17.7 2.64 41.9 2.50<br />

Cu 2+<br />

21.7 2.90 Al 3+<br />

87.5 2.92<br />

73.9 3.56 97.2 3.14<br />

85.7 3.84<br />

94.8 4.08<br />

9.2 1.78 42.3 3.40<br />

Co 2+ 19.0 3.34 Mn 2+ 86.1 3.96<br />

70.8 4.11 99.8 5.66<br />

99.8 5.98<br />

Ca 2+ 3.4 4.15 7.9 1.11<br />

20.4 4.53 V 4+ 21.1 1.34<br />

81.7 5.38 46.5 1.44<br />

99.6 6.52 85.1 1.81<br />

4.2 2.00<br />

19.7 3.00<br />

Cd 2+ 63.1 3.51<br />

91.0 4.00<br />

99.5 5.00


TABLE 15 – ExTRACTION FROM SINgLE METAL<br />

CHLORIDE SOLUTIONS<br />

Solvent 0.6 M CYANEX <strong>272</strong> extractant in<br />

Exxsol D-80<br />

Aqueous 0.015 M metal as chloride<br />

Temperature 50°C<br />

pH Control NH 4 OH or HCl as appropriate<br />

Contact Time 5 minutes<br />

A/O 1<br />

Metal % Ext. Final pH Metal % Ext. Final pH<br />

0.0 3.33 32.6 0.2<br />

25.7 4.36 35.2 0.3<br />

Ca 2+ 48.9 5.00 Fe 3+ 66.4 0.7<br />

91.9 5.90 95.2 1.1<br />

99.4 6.45 99.0 1.4<br />

1.9 2.8 0.0 2.0<br />

48.0 3.5 8.5 2.6<br />

Co 2+ 86.7 4.1 Cu 2+ 51.9 3.1<br />

95.9 4.4 86.2 3.5<br />

100.0 5.5 97.6 3.9<br />

0.0 3.6 12.6 0.9<br />

19.3 4.9 22.6 1.2<br />

Ni 2+ 44.7 5.2 Zn 2+ 54.2 1.6<br />

84.8 5.9 67.9 1.7<br />

95.1 6.3 76.2 1.8<br />

99.7 7.0 92.9 2.1<br />

1.2 3.4<br />

41.2 4.4<br />

Mg 2+ 66.2 5.0<br />

89.1 5.4<br />

99.0 6.4<br />

99.9 6.6<br />

CYANEX <strong>272</strong> Extractant<br />

11


12 CYANEX <strong>272</strong> Extractant<br />

Figure 3 – Extraction of Metals by CyANEx <strong>272</strong> Extractant from Sulfate Solutions<br />

Figure 4 – Extraction of Metals by CyANEx <strong>272</strong> Extractant from Chloride Solutions


ANALYTICAL METHODS<br />

Analysis for Active Component in CYANEX <strong>272</strong><br />

Extractant in Organic Solvents by Titration<br />

The active component of CYANEX <strong>272</strong> extractant is bis(2,4,4trimethylpentyl)phosphinic<br />

acid. Its concentration in an organic<br />

solvent is determined by titration with standard caustic solution.<br />

The extractant contains small quantities of a dibasic impurity (2,4,4-<br />

trimethylpentyl phosphonic acid) which also titrates with caustic.<br />

The endpoints are detected potentiometrically.<br />

Apparatus<br />

pH meter<br />

Magnetic stirrer<br />

Standard laboratory glassware<br />

Reagents<br />

75 v/o 2-propanol in distilled water<br />

0.1N Standard NaOH solution in 75 v/o 2-propanol<br />

100 g/l H 2 SO 4<br />

All reagents are AR grade.<br />

Procedure<br />

1. Contact approximately 50 ml of the solvent to be analyzed<br />

with 50 ml of 100 g/l H 2 SO 4 for 5 minutes at 50°C. Separate<br />

the phases and allow to stand for 15-30 minutes. Centrifuge the<br />

solvent or filter through PS paper* to remove entrained aqueous.<br />

2. To prepare the analyte solution, pipette a 25 ml aliquot of the<br />

solvent and dilute to 200 ml in a volumetric flask with the<br />

appropriate diluent (Escaid**, Kermac*** etc.). Alternatively, the<br />

75 v/o solution of 2-propanol may be used for volume make-up.<br />

3. Pipette 25 ml of the analyte solution into a 150 ad tall-form<br />

beaker. Dilute to approximately 50 ml with the 2-propanol<br />

solution. Insert the pH electrodes and begin stirring.<br />

* Phase separation paper available from Whatman Inc.,Clifton, NJ.<br />

** A product of Exxon Chemical Co., USA<br />

*** A product of Kerr McGee Refining Corp.<br />

CYANEX <strong>272</strong> Extractant<br />

13<br />

4. Note the initial pH and begin to titrate with 0.1N NaOH.<br />

Record the pH as a function of the volume of NaOH added.<br />

Three endpoints should be observed. As each endpoint is<br />

approached, the incremental addition of NaOH should be<br />

reduced to 0.1 ml to facilitate calculation of the titer by the<br />

method of second differences.<br />

Calculation<br />

A typical potentiometric curve is as follows:<br />

The titer T1 corresponds to the neutralization of sulfuric acid<br />

dissolved in the solvent. T2 represents the neutralization of the<br />

phosphinic acid plus the reaction of the first of two replaceable<br />

hydrogen ions associated with the phosphonic acid. The phosphonic<br />

acid is totally neutralized at T3.<br />

0.1N NaOH First Second<br />

(ml) pH Differential Differential<br />

9.8 7.50<br />

9.9 8.00<br />

50<br />

90<br />

+40<br />

10.0 8.90<br />

180<br />

+90<br />

10.1 10.70<br />

50<br />

-130<br />

10.2 11.20<br />

10<br />

-40<br />

10.3 11.30<br />

Then, T2 = (10.0 + 0.1) x ____90___ = 10.04 ml<br />

90 + 130


14 CYANEX <strong>272</strong> Extractant<br />

T 1 and T 3 may be calculated in an analogous manner.<br />

When all three titers are known, the concentration of bis(2,4,4trimethylpentyl)phosphinic<br />

acid may be determined.<br />

bis(2,4,4-trimethylpentyl) phosphinic acid (g/1) =<br />

[T 2 – (T 3 – T 2 ) – T1] x N(NaOH) x 290 x 1000<br />

1000 x 25 x 25<br />

200<br />

Similarly the concentration of the phosphonic acid and dissolved<br />

sulfuric acid may also be calculated.<br />

2,4,4-trimethylpentyl phosphonic acid (g/1) =<br />

Notes<br />

T 3 – T 2 x N(NaOH) x 194 x 1000<br />

1000 x 25 x 25<br />

200<br />

H 2 SO 4 (g/l) = T 1 x 49 x N(NaOH) x 1000<br />

1000 x 25 x 25<br />

200<br />

1. A minimum net titer, i.e. [T 2 – (T 3 – T 2 ) – T 1 ], of 10 ml is<br />

recommended to obtain reproducible results. In this procedure,<br />

10 ml of 0.1N NaOH is equivalent to approximately 100 g/l<br />

concentration of phosphinic acid. Where necessary, the size of the<br />

aliquots and dilutions may be varied to ensure a sufficient volume of<br />

titrant is consumed.<br />

2. Approximate pH’s corresponding to the T 1 , T 2 and T 3 endpoints are<br />

4, 9 and 11, respectively. However these values may vary depending<br />

upon the composition of the solvent. After gaining experience with<br />

a system, the NaOH may be added rapidly until the particular<br />

endpoint pH is approached and then added in 0.1 ml increments to<br />

define the point of inflexion in the curve.<br />

3. The concentrations of sulfuric and phosphonic acids in the solvent<br />

are usually small and these endpoints may not be observed. In this<br />

case T 1 and T 3 should be assigned a value of zero in the calculations.<br />

Typically, T 1 and T 3 - T 2 ) will be < 0.2 and < 0.1 ml of 0.1N<br />

NaOH, respectively, corresponding to


Detector Parameters<br />

Type Flame Ionization Detector (FID)<br />

Temperature 300°C<br />

Helium Flow 8 mL/min<br />

Hydrogen Flow 35 mL/min<br />

Air Flow 400 mL/min<br />

Makeup Flow 35 mL/min<br />

Makeup Gas Type Helium<br />

Sample Injection<br />

Volume 0.1 μL<br />

Peak Areas Electronic integration. The compound has a<br />

retention time of about 17.8 minutes.<br />

Analysis for Active Component in CYANEX<br />

<strong>272</strong> Extractant in Aqueous Solutions by Gas<br />

Chromatography<br />

The concentration of the active component, bis(2,4,4trimethylpentyl)phosphinic<br />

acid in water is determined by gas<br />

chromatography of its methylated derivative.<br />

Procedure<br />

1. Transfer approximately 1 L of the aqueous solution into a<br />

plastic container and place it in a water bath set for 45°C for<br />

a few hours.<br />

2. Remove the solution from the water bath and allow to cool to<br />

room temperature.<br />

3. From the bottom of the plastic container, dispense 600 g of<br />

the solution into a 1 L separatory funnel.<br />

4. Add to the solution 5 mL of concentrated sulphuric acid, 50<br />

mL of toluene and approximately 100 g of sodium chloride.<br />

5. Separate both aqueous and organic phases.<br />

6. Pipette a 1000 μL aliquot of the organic phase and transfer<br />

it into a HP autosampler vial. Add 200 μL of Methyl-8 ®<br />

Concentrate.<br />

7. Prepare standard solutions of CYANEX <strong>272</strong> extractant in<br />

toluene.<br />

8. Pipette a 1000 μL aliquot of the standard solutions and<br />

transfer it into a HP autosampler vial. Add 200 μL of<br />

Methyl-8 ® Concentrate.<br />

9. Analyze the methylated sample and standard solutions by<br />

gas chromatography. The chromatographic conditions<br />

are identical to those previously described in the section<br />

“Analysis for Active Component in CYANEX <strong>272</strong> Extractant<br />

in Organic Solvents by Gas Chromatography,” except the<br />

volume injected by the GC autosampler is 1.0 μL.<br />

CYANEX <strong>272</strong> Extractant<br />

Health and Safety<br />

15<br />

The oral and dermal toxicity of CYANEX <strong>272</strong> extractant is low.<br />

CYANEX <strong>272</strong> extractant produces moderate eye and skin irritation<br />

upon contact. CYANEX <strong>272</strong> extractant did not produce an allergic<br />

dermal reaction in guinea pigs after repeated dermal exposure.<br />

This product did not produce mutations in bacteria. CYANEX<br />

<strong>272</strong> extractant is toxic to fish and invertebrates and care should be<br />

exercised to avoid environmental exposure.<br />

Technical reference list available upon request.


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contained herein represents Cytec’s best knowledge thereon without constituting any express or implied guarantee or warranty of any kind (including, but not limited to, regarding the accuracy, the completeness<br />

or relevance of the data set out herein). Cytec is the sole owner or authorized user of the intellectual property rights relating to the information communicated. The information relating to the use of the products<br />

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