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Separating Dolomite from Phosphate Rock by Reactive Flotation: Fundamentals and Application

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Title:
Separating Dolomite from Phosphate Rock by Reactive Flotation: Fundamentals and Application
Creator:
EL-MIDANY, AYMAN A.
Copyright Date:
2008

Subjects

Subjects / Keywords:
Adsorption ( jstor )
Apatites ( jstor )
Dolomite ( jstor )
Interfacial tension ( jstor )
Particle density ( jstor )
Particle size classes ( jstor )
Phosphates ( jstor )
Polymers ( jstor )
Sulfuric acids ( jstor )
Surfactants ( jstor )
City of Gainesville ( local )

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Source Institution:
University of Florida
Holding Location:
University of Florida
Rights Management:
Copyright Ayman A. El-Midany. Permission granted to University of Florida to digitize and display this item for non-profit research and educational purposes. Any reuse of this item in excess of fair use or other copyright exemptions requires permission of the copyright holder.
Embargo Date:
12/18/2004
Resource Identifier:
57722325 ( OCLC )

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Full Text












SEPARATING DOLOMITE FROM PHOSPHATE ROCK
BY REACTIVE FLOTATION: FUNDAMENTALS AND APPLICATION

















By

AYMAN A. EL-MIDANY


A DISSERTATION PRESENTED TO THE GRADUATE SCHOOL
OF THE UNIVERSITY OF FLORIDA IN PARTIAL FULFILLMENT
OF THE REQUIREMENTS FOR THE DEGREE OF
DOCTOR OF PHILOSOPHY

UNIVERSITY OF FLORIDA


2004

































Copyright 2004

by

Ayman A. El-Midany


































To all who made this work possible, and
To all who had parts in shaping the person that I am today.















ACKNOWLEDGMENTS

In the Name of Allah, the Most Gracious, the Most Merciful.
"Oh Allah! Make useful for me what you have taught me, and teach me knowledge
that will be useful to me. I entrust you with what I have read and studied. Oh Allah!
Bring it back to me when I am in need of it. You are my protector, and the best of
aid.". I thank Allah for blessing me with all of the good that I have, and I ask that I
will be able to use such gifts to help those in need. Amen.

I have fortunate to be able to study in an excellent institution surrounded by a group

of extremely intelligent people. I would like to recognize the amazing staff in Department

of Materials Science and Engineering at University of Florida. I would also like to thank

everyone who helped me arrive at this point. Special thanks and recognition go to my

advisor, Dr. Hassan El-Shall. He gave me the opportunity to do research in his group. His

drive and commitment to research have inspired and motivated me through this work. He

has been a constant source of ideas and encouragement over the years. Many thanks go to

my committee members; especially Dr. Spyros A. Svoronos, who helped me greatly and

bore with me in the modeling part of my study. I would also like to thank the other

members of my committee (Drs. John J. Mecholsky, Wolfgang Sigmund, and Susan

Sinnott from the Department of Materials Science and Engineering, and my external

committee member, Dr. Ben Koopman, Department of Environmental Engineering). I

would also like to recognize the remarkable past and present members of Dr. El-Shall's

research group for their assistance, advice, and support.

Finally, I cannot thank my family enough for all of their love, encouragement, and

counsel. To my parents, I owe everything. They have taught me many things. Above all









they taught me that patience, determination, persistence, and faith are the keys to success.

I thank my wife for her help and patience over the years.

I thank the Particle Engineering Research Center (PERC) staff for helping me to

get started and for providing support and guidance along the way. Much of the

experimental work in my study could not have been accomplished without their help, and

for that I am extremely grateful.

This work was supported by the Florida Institute of Phosphate Research (FIPR),

and the National Science Foundation / Particle Engineering Research Center

(NSF/PERC).
















TABLE OF CONTENTS

page

A C K N O W L E D G M E N T S ................................................................................................. iv

LIST OF TABLES ....................................................... ............ ....... ....... ix

LIST OF FIGURES ......... ......................... ...... ........ ............ xi

ABSTRACT ........ .............. ............. ...... ...................... xiv

CHAPTERS

1 LITERATURE REVIEW ..............................................................................1

In tro du ctio n ......................... ...... .... ...... .... ............ .......... ....................
Previous Efforts to Separate Dolomite from Phosphate Rock............... ..................
A nionic F location .............................................. ................ .. 4
D irect flotation ....................... .............................. .. ......... ............ ..
R everse flotation .......................... ........ .................... .. ..
C ationic F location ....................................................... 8
N onconditioning Flotation.......................................................... ............... 9
Two-Stage Conditioning Process ..... .................... ...................11
The CLD R I Process .......... ........ ....... ................... .... .........12
A cid L each in g ................................................... ................ 14
Physical Separation Methods ........... .. ......... ....... ............... 14
H eavy M edia Separation ............................................. ............................ 14
Sizing, Attrition Scrubbing, and Desliming ................................................15
Problem Statement........ ...................................... .. ........ .. .... .......... 15
N ovelty and Scope of Study .............. ..........................................................15
G o al o f S tu d y ...................... .. ............. .. .................................................16

2 M ATERIALS AND M ETHOD S ........................................ ......................... 17

Flotation Study......................................................... .. .. ............. 18
Screening Design (Plackett-Burman Design).......................... ................18
C central C om posite D esign ................................................ ............... ... 18
Flotation Procedures for Screening and CCD Designs ....................................21
Factorial Design for Conditioning with PVA before Flotation...........................21
Flotation Procedure for Conditioning Statistical Designs...............................21
Density and Surface Area Determination....................................22









PV A Preparation ........ .......................................... .......... ........ .......... 23
Spectrophotometric Determination of PVA...................................................23
Static (Equilibrium surface tension)................... ...... ..............24
Dynam ic Surface Tension (D ST) ............................................. ............... 24
Maximum bubble pressure method............................................................24
Dynamic surface tension setup ............... ............................................. 26
C o n tact A n g le ................................................................... ............... 2 6
M easurem ent of Contact Angle............................................... ........ ....... 27
Surface Characterization by FTIR .................................................................... 28
Zeta Potential M easurem ents ........................................ ......................... 28
A d so rp tio n .................. ................... ............................................. 2 8
Dissolution Kinetic Experim ents...................................................................... 29
Pilot Scale Experim ents .................. ..................................... ..... .. ........ 30
T he Sluice ............................................................................................. ....... 30
Sluice Experim ents .................. .......................... .... .... ... ........ .... 30

3 TECHNICAL ASPECTS OF REACTIVE FLOTATION: PRELIMINARY TESTS32

In tro d u ctio n ............. ...... ... ........................ ......................... 3 2
List of Potential Surfactants: Surfactants Screening ..............................................33
Initial Screening Tests ............................ ............ ................... ..... .... 33
S p ecific T e sts................................................. ................ 3 4
A cid ty p e ......................................................................34
A cid d o sag e .............................................................. ............... 3 5
Su rfactant ty p e ................................................. ........... ............... 3 6
Surfactant dosage ................... .... .......... ............. .... ........37
P article siz e .............................................................3 8
Oil-Surfactant Experiments ................................................... .................. 39
Poly-Vinyl-Alcohol (PVA) Testing ....................................... ............... 41
Effect of acid concentration ........................................ ...... ............... 41
Effect of particle size............ .. .............. ................ ......... .. ............. 43
PVA with acid vs. PVA on the particle surface .......................................44
Preliminary Testing Using PVA Coated Particles ................................................45
Flotation of a Representative Sam ple....................................... ............... 45
Fraction of Representative Sample (-4+1.19 mm) ............................................46
Effect of Time on Weight Percentage of Floated Particles .................................46
Effect of Size on the Flotation............ .............................. ............... 47
Sum m arizing R em arks........................................................................ ..................48

4 OPTIMIZATION OF THE REACTIVE FLOTATION PROCESS
AND PILOT SCALE TESTING........................................... .................... 49

Introduction ......... ..... .... ......................................................... ..... 49
Optimization of the RF Process ............ ..... ........ ................... 49
Screening Statistical Design .....................................................49
C central C om posite D esign........................................................ ............... 52









Research to Reduce the PVA Consumption .................................... ............... 52
Experimental Design of the PVA Conditioning Step........................................56
Saturation Experiment ............ ..... ............... ............... 56
Pilot Scale Testing: Sluice R results ........................................ ......... ............... 57

5 FUNDAM ENTAL STUDIES ............................................................................. 58

Polyvinyl alcohol-Particle Interaction ..... ................ ...............58
In tro d u ctio n ................................................................................................... 5 8
Surface Tension ......... ......... .................. ............... .... ........... 60
Contact Angle ............ ...... ..................... ...... ........ ... .......... 63
W ork of A dhesion .............................. ........................ .. ...... .... ...... ...... 64
Zeta Potential .............................................67
Zeta potential of minerals in supernatant solutions ............. ...............70
Zeta potential in the presence of PVA ............. ..................... ......... ...... 71
Infrared (FTIR) ....... ........ ....... ............................... .... ........72
Adsorption Study ......... ..... ...... ....... ......... .. .......... ................. 75
K inetics of adsorption ............................................................................ 76
Adsorption isotherm ................... ... ................................ 79
Calculation of PVA adsorption and parking area .............. .............82
A dsorbed layer thickness ........................................ ......... ............... 84
Effects of pH .............................. ..... ........ ..... .............. ................ .....84
Adsorption in supernatants .......................... 87
D e so rp tio n ...................................................... ................ 8 8
Desorption in Acidic Solution ...... ................ .. ..................89
Bubble Formation and Stability.......................................... 90
Effect of Particle Size ........... .. ..... ......... .................. ............... 91
Effect of PVA Coating ............................................ ......................94
Modeling of Bubble Formation and Dolomite-Particle Separation .........................96
B lockage of the A cid M odel......... ......... ...... ........................... ..... ......... 96
Disappearance of Active Sites M odel .......... .......... ......... .. ............ 99
Em pirical M odels .............................. .................. .. .......... .... ............. 101
First-order kinetic m odel ........................................... ............ ............... 101
Acid concentration dependence model .................................. 103
Estimation of CO2 Required to Float the Dolomite Particle ........................... 106
B bubbles Stability ................ ..... ...... .. .. .... .. .................. .. .............109
Validation of the Model Using a Different Carbonate Mineral .....................12
Sum m arizing R em arks......... ................. ...................................... ............... 114

6 CONCLUSIONS AND RECOMMENDATIONS FOR FUTURE WORK ............116

C o n c lu sio n s.................... ......... ........................................................................ 1 1 6
Recommendations for Future W ork .............. ............ ........... .... ............... 119

L IST O F R EFER EN CE S ....................... ................. .............................. ............... 120

BIOGRAPH ICAL SKETCH ....................... .......... ........................................... 129


viii
















LIST OF TABLES


Table pge

2-1. Experimental Plackett-Burman design for 11 variables................ .............. ....19

2-2. Rotatable central composite design with 5 levels and 3 variables .........................20

2-3. Factorial design for conditioning with PVA............... .........................................21

3-1. Surface-active agents used in RF tests ........................................ .....................33

3-2. Size analysis of the dolomitic phosphate sample ............................................34

3-3. Chemical analyses of the dolomitic phosphate sample ........................................34

3-4. Effect of sulfuric acid concentration ............................................. ............... 35

3-5. Effect of sulfuric acid concentration on the bubble formation..............................36

3-6. Preliminary tests of high dolomitic phosphate with different surfactants ..............37

3-7. Effect of surfactant concentration (SDSO3, 2 %) ................... ...................... 38

3-8. Effect of particle size on the dolomitic particle floatability ...................................39

3-9. Effect of presence of surfactant and oil layer on particle flotation ..........................40

3-10.Effect of acid concentration... ........................................................... ............... 42

3-11.Effect of acid concentration above 2 %.............................................. 43

3-12.Comparison between coating the particle before adding it to acidic solution and
adding the particle to acid+PVA solution without coating ....................................45

3-13.Results of representative sample (- 4+1.19 mm particle size)...............................46

3-14.Effect of time on the flotation of- 4+1.19 mm particle size ...............................47

3-15.Effect of particle size on flotation ..................................... ............ ....................47

4-1. The MgO % removal in floated fraction for Plackett-Burman design ...................50









4-2. Plackett-Burman calculated t values for different variables..............................51

4-3. Effect of saturated acid on the RF ................... ............ 57

4-4. Comparison of two different coating methods and their effects on MgO removal..57

5-1. Chemical analysis of the samples used in adsorption tests ....................................66

5-2. Fitting parameters of second-order kinetic model............................... ............... 77

5-3. Chemical analysis of the samples used in kinetic tests ........................................91

5-4. A cid-blockage m odel param eters ........................................ ......................... 97

5-5. Active sites disappearance parameters ....................................... ............... 100

5-6. Reaction rate constants of first-order m odel................................... ... ................ 103

5-7. Acid concentration dependence parameters ................................. ............... 105

5-8. Active sites disappearance parameters for dissolution of calcite .........................113
















LIST OF FIGURES


Figure pge

1-1. Simplified flowsheet for phosphoric acid production .............................................3

1-2. Simplified flowsheet of USBM direct flotation .............................. ...............6

1-3. Flowsheet of TVA's diphosphonic depressant process..............................................8

1-4. Flowsheet for IMCF cationic flotation......... ........................................9

1-5. University of Alabama pebble processing, simplified flowsheet...........................10

1-6. Flowsheet for University of Florida two conditioning stages .............................. 11

1-7. Simplified flowsheet for CLDRI dolomite flotation ..........................................13

2-1. Strategic plan to achieve research goals................... ....................17

2-2. Five-level, rotatable central composite design.. ................................... ............... 20

2-3. Characteristic bubble-pressure vs. time curve in MBP. .........................................25

2-4. Setup for the measurement of dynamic surface tension by MBP...........................26

2-5. Contact angle and its relation with surface tension ............................. .................27

2-6. Contact angle measuring apparatus ...................................................................... 28

2-7. Schematic diagram for separation of dolomite from phosphate in sluice ................30

3-1. Effect of acid concentration on bubble formation and flotation time.....................36

3-2. Effect of the particle size on the time needed to float the particle ...........................44

4-1. Effect of PVA dosage and acid conc. on MgO recovery % ...................................53

4-2. Effect of PVA dosage and acid concentration on MgO % ....................................54

4-3. Cube graph for MgO % and MgO recovery %................................................ 56

5-1. Contact angle and interfacial surface tension at solid/liquid/gas interface ..............60









5-2. Structural formula for PVA ...... ........................... ......................................61

5-3. Equilibrium Surface tension for aqueous PVA solutions at 23 C.........................61

5-4. PVA crystal structure; the dotted lines indicate hydrogen bonds.............................62

5-5. Static contact angle variation with the PVA concentration.................................64

5-6. Work of adhesion as a function of PVA concentration................ .............. ....65

5-7. Cumulative pore size distribution for apatite sample ............................................66

5-8. Cumulative pore size distribution for dolomite sample.........................................67

5-9. Zeta potential of dolomite and apatite samples ................................ ............... 68

5-10. Zeta potential of dolomite in absence and presence of polymer ............................68

5-11. Zeta potential of dolomite in absence and presence of polymer ............................69

5-12. Effect of polymer on the shear plane position.............. .................................69

5-13. Zeta potential of apatite and apatite in dolomite supernatant..............................70

5-14. Zeta potential of dolomite and dolomite in apatite supernatant ...........................71

5-15. Zeta potential of dolomite in apatite supernatant before/after PVA adsorption.....72

5-16. Zeta potential of apatite in dolomite supernatant before/after PVA adsorption.....72

5-17. Infrared transmittance spectra of poly vinyl alcohol (PVA) .............................73

5-18. Infrared absorbance spectra of dolomite and dolomite/PVA system ...................74

5-19. Infrared absorbance spectra of apatite and apatite/PVA system. .........................75

5-20. Calibration curve for PVA concentration measurements................... ..............76

5-21. Kinetics of PVA adsorption on dolomite and Apatite................ .............. ....78

5-22. Adsorption isotherm of PVA on dolomite at 23C ..............................................81

5-23. Adsorption isotherm of PVA on apatite at 230C............................... ..............82

5-24. Polymer-conformation changes with increase the concentration ..........................83

5-25. Effect of pH on adsorption of PVA on apatite and dolomite ...............................85

5-26. Adsorption isotherm of apatite in dolomite supernatant solution, and dolomite in
apatite supernatant solution ............... ................ .................... 87









5-27. Desorption of PVA from apatite surface ..... ......... ..................................88

5-28. Desorption of PVA from dolomite surface................................. ............... 89

5-29. The bubble form ation m echanism ........................................ ....... ............... 90

5-30. Schematic diagram of reaction kinetics of the RF ...............................................91

5-31. Dissolution kinetic of different particle sizes in terms of calcium ions ..............92

5-32. Dissolution kinetic of different particle sizes in terms of magnesium ions............93

5-33. Dolomite particle (1-2 mm) before and after the reaction with 3 % H2SO4...........93

5-34. Dissolution kinetics of coated and uncoated 0.2-0.3 mm dolomite particle ..........94

5-35. Growth of the bubbles with time on the dolomite particle surface, 50 X..............95

5-37. Acid blockage model fitting to 0.25-0.35 mm experimental data..........................98

5-38. Active sites disappearance model fitting to 1-2 mm data..................................100

5-39. Active sites disappearance model fitting to 0.25-0.35 mm data.........................100

5-40. First-order model fitting for data of 0.25-0.35 mm particle size..........................102

5-41. First-order model fitting for data of 1-2 mm particle size..................................102

5-42. Model fitting for data of 0.25-0.35 mm particle size.........................................104

5-43. M odel fitting for data of 1-2 mm particle size.................. .................. ................105

5-44. Sequence of calculating the particle density and membrane elasticity ..............108

5-45. Density changes for different particle sizes............................... ............... 109

5-46. Dynamic surface tension of PVA concentration at different CO2 flowrate .........111

5-47. Elasticity of PVA membrane vs. PVA concentration ............... .................... 112

5-48. Calcite dissolution: model vs. experimental data 0.25-0.35 mm particle size .....113

5-49. Calcite dissolution: model vs. experimental data for 1-2 mm particle size..........113















Abstract of Dissertation Presented to the Graduate School
of the University of Florida in Partial Fulfillment of the
Requirements for the Degree of Doctor of Philosophy

SEPARATING DOLOMITE FROM PHOSPHATE ROCK
BY REACTIVE FLOTATION: FUNDAMENTALS AND APPLICATION

By

Ayman A. El-Midany

December 2004

Chair: Hassan El-Shall
Major Department: Materials Science and Engineering

Florida is currently one of the largest phosphate producers in the world.

Unfortunately, the phosphate industry in Florida is suffering from depletion of the

phosphate-rich ore. Dolomite, however, is a major impurity in the ores. The presence of

MgO, in dolomite, can cause several problems during production of phosphoric acid and

final fertilizers. Efforts to solve the dolomite problem have been reported by several

researchers throughout the world. Yet, only heavy media separation process has been

applied commercially. However, the process was discontinued because of its low

separation efficiency in terms of grade and recovery.

In this study, we tested an innovative idea based on simple fact that dolomite, as a

carbonate mineral, generates CO2 when exposed to a slightly acidic solution, capturing

CO2 bubbles at dolomite particle surface can selectively float the dolomite and separate it

from phosphate. Formation of such bubbles requires a surface-active agents) at









solution/dolomite interface. Preliminary tests indicated that polyvinyl alcohol (PVA)

could serve this function. This process is called the Reactive Flotation, RF.

To develop this process and to scale it up for industrial use, we conducted

fundamental and applied research studies. Among these studies were optimizing of RF

process by investigating the factors affecting the process (including bench and pilot scale

tests) using statistical experimental designs. It was found that the acid concentration,

PVA concentration, and particle size are the main factors. The optimum conditions were

determined and applied to usage in a gravity separation device, (i.e., a sluice). Using such

a device, a concentrate contains 0.65 % MgO with > 94 MgO % removal can be

achieved. In addition, fundamental studies revealed that the hydrogen bonding is the

adsorption mechanism confirmed by adsorption isotherm of PVA on dolomite and

phosphate, adhesion of PVA to dolomite surface (using contact angle and surface

tension), Fourier Transform InfraRed (FTIR), and Zeta potential. Moreover, PVA film

thickness and polymer film elasticity (using dynamic surface tension) revealed that the

optimum conditions could keep the PVA film at its highest elasticity. On the other hand,

modeling was developed and used to predict CO2 formation rate and subsequent particle

density change.














CHAPTER 1
LITERATURE REVIEW

Introduction

Traditionally, the Florida phosphate industry has effectively responded to the

competitive pressures of the market place by implementing technological improvements

to mining and beneficiation methods. With further expansion of fertilizer production

capacity worldwide and depletion of Florida's high-grade deposits, competitive pressures

are expected to continue. To remain the world leader, Florida must continue to seek

environmentally sound technological improvements in all areas of phosphatic fertilizer

production.

Gu et al. [1999] estimated that the Bone Valley phosphate reserve in Central

Florida (which can be cost effectively processed with available technology) may only last

about 20 years at the current mining rate. In the near future, with the depletion of the

low-dolomite, easy-to-process Bone Valley siliceous phosphate deposits, phosphate

mining will move farther south and southeast. The phosphate matrix in the southern

extension is leaner in grade and high in dolomite. Dolomite is the most troublesome,

causing higher consumption of sulfuric acid, reducing filtration capacity, and lowering

P205 recovery in fertilizer manufacturing. Therefore, the MgO content of dolomite is an

important index in evaluating the quality of phosphate concentrate. In Florida, the MgO

content in final concentrate is usually required to be less than 1 %.

Geological and mineralogical data show that about 50 % of the phosphate resource

would be wasted if the high dolomitic zones were bypassed in mining, and about 13 % of









the resource would be lost if the dolomite pebbles were discarded. Although heavy

media separation (HMS) technology was tried commercially, to process a portion of

dolomite pebbles in Florida, in most cases the high-dolomite phosphate has been

bypassed during mining operations because no technology is available to process high-

dolomite pebbles economically. Technically and economically feasible beneficiation

technology for processing dolomite pebbles is needed to recover phosphate value, extend

Florida phosphate reserves, and prolong the life of Florida phosphate industry [Geo et al.,

2002].

Previous Efforts to Separate Dolomite from Phosphate Rock

Phosphate rock is one of the basic materials for fertilizers. About 90 % of the

phosphate rock output in the world is used for fertilizer production. The United States is

one of the world's largest producers of phosphate rock and fertilizer. Its phosphate

production represents approximately one-third of the world's total [Becker, 1989].

Phosphoric acid is an important intermediate product for production of fertilizers.

Current phosphoric acid technology essentially comprises sulfuric acid attack, and

separation of the phosphoric acid from the calcium sulfate crystals resulting from the

reaction. Both the attack and separation, which are effected by filtration, are considerably

influenced by the nature of the ore and its impurities [Becker, 1989]. Figure 1-1 shows

the main processes in phosphoric acid production.

As mentioned, the main impurity in Florida phosphate ore is dolomite. Dolomite,

(Ca, Mg)C03, is the main source for calcium and magnesium. As impurities, CaO and

MgO affect the phosphoric acid production by increasing sulfuric acid consumption, in

addition to the MgO stays with the acid phase, and greatly increases viscosity.









Calo(PO4)6F2 + 10 H2SO4 + 20 H20 6 H3PO4 + 10 CaSO4.2H20 + 2 HF

Phosphate
Phd o ate Wash Water
Concentrate
Sulfuric acid *

I


Reaction


J* Filration


Phosphoric acid rnospnovDosum

Figure 1-1. Simplified flowsheet for phosphoric acid production

Therefore, because dolomite is the most common impurity, developing an efficient

and economical method for separating dolomite from apatite is an effective way to extend

phosphate mine life. Generally, acidulation of phosphate rock requires a feed of less than

0.8 % MgO, which has not been achieved at a commercial scale with ores high in MgO.

Dolomite is also a worldwide problem. All of the major phosphate-producing countries

have faced, or are going to face, the dolomite problem.

Salt-type minerals (such as apatite, calcite, dolomite, barite, fluorite and scheelite)

have been successfully separated from oxides and silicates by flotation methods.

However, these minerals are often difficult to separate from each other because they

contain similar alkaline earth cations that cause them to exhibit similar surface (electrical)

behavior. All the zero points of charge (ZPC) of phosphates and carbonates are located in

the acid pH range (i.e., 4-5.5) [Smani, 1973; Smani et al., 1975].

Systematic research in carbonate phosphate ore beneficiation started in the early

1950s [El-Shall et al., 2004]. Techniques used include the following:

* Direct flotation of phosphate, using sodium silicate to depress carbonate impurities.









* Reverse flotation of the carbonate impurities by depressing the phosphate using
materials such as fluorides, fluosilicic acid, diphosphonic acid, phosphoric acid,
aluminum sulfate-tartrate, and inorganic phosphate salts.

* Rapid change of conditioning parameters (such as the University of Florida two-
stage conditioning process, Alabama non-conditioning process, the IMC-F process,
and the low-pH conditioning process proposed by Minemet research).

* Physical methods: gravity concentration, sizing, desliming, heavy media
separation.

* Calcination: although expensive because of its energy requirement, high-
temperature destruction of the carbonate followed by leaching has been practiced in
North Africa with low -cost energy.

* Acid leaching: carbonates are easily dissolved by acid, and weak acids can be used
to dissolve the carbonate, leaving the apatite.

Anionic Flotation

Direct flotation

Sodium silicate is widely used as carbonate depressant [Fuerstenau, 1968;

Ananthapadmanabhan and Somasundaran, 1985; Rao, 1988; Dho and Iwasaki, 1990].

Encouraging results were obtained in both batch and continuous pilot tests conducted by

the United State Bureau of Mine, USBM, [Davis et al., 1984]. After 1 lb/t sodium silicate

was added in each of three cleaning stages, a phosphate rougher was upgraded to about

30.7-31.3 % P205, 0.6-1.3 % MgO with a P205 recovery from 55.1 to 89.7. The original

matrix contained 5.47-10.2 % P205, and 1.9-7.6 % MgO.

Rao [1989] studied the effects of major flotation parameters on phosphate grade

and recovery using sodium silicate as a calcite depressant. Maximum flotation of apatite

occurred at pH 8, and phosphate recovery decreased with increasing pH. Sodium silicate

at a concentration below 0.0013 M had no depressive effect on calcite. However, at pH

values above 10, calcite depression was observed even in dilute silicate solution. A

concentrate with 25.6 % P205 at 80 % recovery was obtained.









Efforts to concentrate high-dolomite Florida phosphate ores by flotation, using

conventional fatty-acid/fuel-oil flotation [Liewellyn, 1982], showed that sodium silicate

depression on dolomite was not enough to obtain a concentrate less than 1 % MgO. This

may be due to the presence of silica in this ore in addition to dolomite.

Reverse flotation

Depression of phosphate: This method was used when the apatite was more

abundant than calcite and dolomite (as in most phosphate ore). Among depressants used

are as follow:

Fluosilicic acid: USBM investigated the removal of carbonate from phosphate

rock using fluosilicic acid as a depressing agent and tall oil-fatty acid as a collector for

carbonate mineral flotation (Figure 1-2) [Rule, 1982; 1985]. At collector dosage 0.7 kg/t,

0.45 kg/t depressant, a concentrate of 25.5 % P205 and 0.84 % MgO with P205 recovery

89.5 % was obtained from feed with 20.8 % P205 and 1.1 MgO %.

Abdel Khalek [2000] studied the phosphate depression using fluosilicic acid, but

recovery using this process was less than 60 %. Ataly [1985] pointed out that for

depressing Turkish ores fluosilicic acid was not efficient as other depressants because of

the low recovery (57 %) obtained using fluosilicic acid.

Acid depressants: Orthophosphoric acid was found to decrease adsorption of the

fatty acid on apatite because of the increased surfacial solubility of apatite.









Phosphoric acid also was used to depress apatite (by the USBM, in separating

dolomite from a southern Florida ore) [Liewellyn, 1982]. The produced concentrate's

P205 % did not exceed 28 %, and the MgO % was not less than 1.9 %.

High MgO Pebble


Hammer Mill


Screening I + 28 Mesh
28 Mesh


Desliming
150 Mesh I- -150 Mesh Fines


NaOH Scrub


Desliming -150 Mesh Fines
150 Mesh


Fatty acid/Fuel Oil I ..


Dolomite
Rougher Tail


Dolomite
Cleaner Tail


Figure 1-2. Simplified flowsheet of USBM direct flotation


Sodium Silicate









Lawendy [1993] found phosphoric acid to be the best among conventional

depressants of phosphate. The concentrate was 32-36 % P205, 1 % MgO at 70-75 %

overall P205 recovery from feed 16-25 % P205 and 4-11 % MgO. In other study [Hsieh

and Lehr, 1985], diphosphonic acid was used to depress phosphate (TVA process),

(Figure 1-3), with fatty acid collectors for beneficiating an ore containing 72 % SiO2,

1.05 % MgO and 6.3 % P205. The resulted concentrate contained 73.3 % SiO2, 0.7 %

MgO and 6.4 % P205.

Although sulfuric acid is a phosphate depressant, its ability to attack phosphate and

its high need for pH control limits its usage [Elgilani and Abouzeid, 1993]. Jacob

Engineering [Gruber et al., 1987] used sulfuric acid as a pH regulator to completely

depress phosphate at pH 5.5.

Phosphates: Rao [1979] found that the depressing action of dipotassium hydrogen

phosphate is pH dependent. Phosphate can be depressed at pH 5-8, while carbonate can

be depressed only at alkaline pH; which means that selective flotation can be obtained.

However, the concentrate produced by this process contained no more than 24 % P205.

Sodium chloride: The effect of sodium chloride and other salt addition on

dolomite and apatite flotation has been studied [Rao, 1985]. It was shown that sodium

chloride acts as apatite depressant during flotation at acidic pH values with oleic acid,

while dolomite flotation is not affected. It was, however, observed that dolomite particles

larger than 48-mesh are difficult to float and they tend to remain in the sink fraction.

Trends observed during Hallimond cell tests of single and mixed minerals were

confirmed with mixtures of minerals and a natural ore at bench-scale level. Under more









favorable conditions in the bench-scale tests, MgO content of the mineral mixtures was

reduced from 5 % to 1 % or less, with at least 90 % recovery of P205 in the sink fraction.


High MgO Pebble


+ 48 Mesh
-400 Mesh Fines



-400 Mesh Fines


Float Dolomite Tail


Diphosphonic acid/
Oleic Acid


Dodecylamine
Hydrochloride


Float Silica Tail


Figure 1-3. Flowsheet of TVA's diphosphonic depressant process

Alizarin Red S (ARS): ARS is an organic depressant. It is used to depress either

phosphate or carbonate, depending on pH. ARS can depress calcite impurities at a pH 8-

10, while apatite can be depressed at a pH below 6 [Fu and Somasundaran, 1986; Xiao

and Somasundaran, 1989].

Cationic Flotation

The IMC-F process (Figure 1-4) is a cationic-flotation process for silica-free ores.

The ore is reagentized with a cationic collector aminess or their salts) and the dolomite










separated from phosphate at a rougher stage followed by one or two phosphate-cleaning

steps [Snow, 1979; 1982; Lawyer and Snow, 1980]. By using IMC-F process, a

concentrate of 31 % P205, 0.86 % MgO from feed of 2 % MgO with 83 % P205 recovery

can be obtained.


High MgO Pebble


Acetic acid/Amine


Frother





Phosphate Conc.


- -150 Mesh Fines

--- Silica Tailings









Dolomite
Rougher Tail

Dolomite
Cleaner Tail


Figure 1-4. Flowsheet for IMCF cationic flotation

Nonconditioning Flotation

A research contract between FIPR and Mineral Resources Institute (MRI) at the

University of Alabama aimed to develop a selective flotation process (Figure 1-5) to

separate dolomitic limestone from Florida phosphate ore [Hanna and Anazia 1990]. This

process depends on the difference in adsorption rate of fatty acids on both phosphate and









carbonates. Fatty acids adsorb more rapidly on carbonate surfaces than on phosphate

surfaces. At slightly acidic pH (5.5-6.0), carbonates floated immediately on addition of

collector and brother. After carbonate froth collection, the pulp is conditioned briefly to

float phosphate thereafter with no more addition of collector.


High MgO Pebble


screening I +35 Mesh
35 Mesh


Desliming
150 Mesh Io -150 Mesh Fines


Scrubbing --- Silica Tailings
35% solids

Desliming -
325 Mesh -325 Mesh


Fatty acid/Pine oil
Conditioning


Dolomite Dolomite
Flotation Tail

Sodium silicate/Fatty Condi
acid Conditioning
acid

Phosphate Conc.
Flotation
pH 4-7 Silica Tailings

Figure 1-5. University of Alabama pebble processing, simplified flowsheet









Two-Stage Conditioning Process

This process was investigated through FIRP university of Florida project, in 1983

[Moudgil, 1988]. The process involves conditioning the feed at pH 10, followed by

reconditioning at a lower pH before flotation, Figure 1-6. Selective flotation of dolomite

from apatite was observed for both single and mixed minerals, by reconditioning at pH 4.


High MgO Pebble
65x150 Mesh Feed
Basic pH
Modifier/Fatty Condit
acid Conditioning
pH=10



Flotation 1 Silica (Sink)
PH 9_10


H SO
2 4 Reconditioning




Frother Dolomite Flotation Float Dolomite
pH 4_5


Sink (Apatite & Fine Quartz)


Further processing
to remove silica


Figure 1-6. Flowsheet for University of Florida two conditioning stages

To understand the mechanisms of observed selective flotation, further studies were

conducted involving electrokinetic behavior, oleate adsorption, infrared spectroscopy,









and solubility of the minerals. Selective flotation of dolomite, by reconditioning at pH 4,

is attributed to the combined effect of higher oleate adsorption on dolomite and

hydrolysis of the adsorbed oleate molecules to oleic acid at lower pH values.

The method has been tested in the laboratory with several dolomite-apatite

mixtures and natural magnesium phosphate samples from the Florida phosphate field.

Reductions of the MgO content of the samples from 1.8-4.0 % MgO to below 1 % MgO

at recoveries of about 90 % P205 in the sink fraction have been obtained in bench-scale

flotation tests. Reconditioning pH was determined to be one of the most important

parameters in this process.

The CLDRI Process

In China, over 90 % of the phosphate resources are dolomitic, with MgO content

ranging from 2 % to over 10 %. For economical and rational use of domestic phosphate

resources, China Lianyungang Design and Research Institute (CLDRI) has conducted

studies for many years and developed some flotation technologies for removing MgO

impurity from phosphate ore. These flotation technologies have successful industrial

applications [El-Shall et al., 1996].

Since 1997, CLDRI has conducted extensive studies on Florida high dolomitic

pebble with the objective of using CLDRI's fine particle flotation technology to recover

phosphate (Figure 1-7). In 2000, pilot scale testing (400 lb/h) was carried out jointly by

CLDRI, Jacobs engineering group, and IMC phosphate's company at Jacob's pilot plant

facility. Preliminary economic and technical analysis by Jacob's engineering (based on

pilot plant test results) showed that CLDRI's fine-particle flotation technology could be

used economically and technically for processing Florida's dolomitic phosphate pebbles

[Geo et al., 2002].






































































TO POND
OFloaw OF~
CYCLONES IV THICKENER -
U'Fow |

I ------ ----- I Of Flow
FILTER |io

STOPOND
FINAL CONCENTRATE


Figure 1-7. Simplified flowsheet for CLDRI dolomite flotation









The CLDRI's fine-particle flotation technology (Figure 1-7) utilized for processing

Florida high-dolomitic phosphate pebbles has two steps. The first step is grinding for

liberation and second nondesliming after grinding, which improves flotation recovery and

use of Florida resources, and lowers production cost.

Acid Leaching

Strong and weak acids were used in the acid leaching process. In strong-acid

leaching processes, sulfuric acid was used to completely dissolve the dolomite from

phosphate ore.

In the early 1970s, the USBM investigated magnesium impurity removal from

phosphate concentrates by acid leaching [Rule, 1970]. The MgO level was reduced to

less than 0.1 % by using dilute sulfuric acid, but the phosphate loss was about 6 % P205.

Weak-acid leaching, using weak organic acids, was also studied. Pilot plant studies

[Abu El-shah, 1991] using 6.7 % acetic acid solution could remove more than 80 %

MgO. The advantage of using weak organic acids is that (unlike strong acids), they do

not attack other minerals. The overall disadvantage is that acid leaching, in general, needs

fine particle sizes produced by crushing and grinding which means more expenses.

Physical Separation Methods

Heavy Media Separation

The only commercial process to separate dolomite from phosphate is heavy media

separation [Wiegel and Hwang, 1984]. Heavy media cyclones are used in IMCF mines

for processing the high-dolomite portion of the ore. The concentrate with 1.2 % MgO was

obtained from feed that has 3 % MgO.









Sizing, Attrition Scrubbing, and Desliming

The dolomite is more friable than phosphate rock. Thus, dolomite can be separated

from phosphate by discarding the fine fraction (mainly dolomite) by scrubbing or sizing

[El-Shall and Bogan, 1990].

Problem Statement

The various beneficiating techniques discussed have various limitations or

disadvantages. In acid leaching, strong acids can attack phosphate as well as dolomite

and can be associated with environmental problems associated with this process.

In flotation processes for high dolomitic phosphate, because they could not reduce the

MgO % below 1 % are not applied commercially.

In CLDRI fine flotation process, by which the MgO % could be reduced to less

than 1 %, concerns are as follows: handling of fine concentrate (dewatering and

transport), capital cost (grinding and multiple process steps), and operating cost:

increasing the MgO % in the phosphate rock increases reagent consumption, and requires

grinding, thus increasing energy consumption and plant operating cost. The only process

with commercial application was heavy media separation (HMS), which also suffers from

high MgO % (more than 1 %) in the concentrate in addition to about 50 % phosphate

loss.

Novelty and Scope of Study

We sought a process that separates dolomite from phosphate pebbles resulting in a

phosphate concentrate with less than 1 % MgO. Since the dolomite is mostly in the

pebble fraction and not attached to phosphate, the idea came from well-known reaction

between carbonates and acid producing carbon dioxide gas. Dolomite, as a carbonate









mineral, generates CO2 when exposed to a slightly acidic solution, as shown in the

following chemical reaction:

Dolomite + Acid salt + CO2

Capturing the generated CO2, at the dolomite particle surface, into bubbles using

coating agent (which is a kind of surfactant or polymer) can selectively float dolomite,

and separate it from phosphate rock. Since this process depends on chemical reaction

between dolomite and acidic medium to form a stable bubble at the particle surface and

then to float it, this process is called the Reactive Flotation (RF) process.

The RF has the following requirements (1) presence of acidic medium at low

percentage, and (2) Presence of surfactant that: attaches to the dolomite, is permeable by

acid, allows formation of stable bubbles at the particle surface, is impermeable to CO2

gas, and is stable enough to float the particle to the surface.

Goal of Study

The goal of this study is to develop and to optimize a novel and an effective

process to separate the dolomite from phosphate rock. This process will not only reduce

the MgO % to less than 1 % but also increase the efficiency of the subsequent processes

in phosphoric acid production such as filtration and consequently reduce the phosphate

losses. In addition to develop this novel process, a fundamental study needs to be done to

elucidate Mechanism(s) involved in this novel process.















CHAPTER 2
MATERIALS AND METHODS

To achieve the goals of this research different measurements and techniques are

needed to elucidate polyvinyl alcohol (PVA)/ particle interactions, and bubbles formation

and stability as well as its modeling the following strategy will be followed, Figure 2-1.


SContact Angle Surface Tension


Adsorption Isotherm Work of Adhesion FTIR Zeta Potential


Film thickness

Elasticity (Dynamic -
surface tension) Acid Diffusion

CO2 formation rate Bubble
formation
model
Density balance Time required to
start particle flotation

.............................................................................................................................................................. I ..........................................................................................................................................................
Density change


Figure 2-1. Strategic plan to achieve research goals

As it can be seen form Figure 2-1, the first block represents the required

techniques and measurements to elucidate polyvinyl alcohol (PVA)/ particle interactions.

On the other hand, the second block represents another part of our goal which is bubble

formation and stability as well as its modeling.









Flotation Study

In this study, screening and central composite statistical experimental designs are

used to determine the effect of various factors on the removal of MgO and its recovery.

The Plackett-Burman design was used to screen out which of the 7 factors being

considered were the most statistically significant. In other words, it is a tool that helps

determine which factors made the greatest impact on the MgO removal. A central

composite design was used to determine if there were any interactions between the three

most significant factors determined from the Plackett-Burman design.

Screening Design (Plackett-Burman Design)

The variables examined in the screening stage were acid concentration (1% and 3

%), Polyvinyl alcohol concentration in the coating solution (1 % and 3 %), the PVA

molecular weight (60,000 and 150,000), the degree of hydrolysis (88 %-99 %) of the

PVA, particle size (-0.5 mm and 5-9 mm), and drying time of the coating (0 and 2 hrs).

The levels were chosen according to the exploratory test results from phase I of this

project. The Plackett-Burman design used for this study had 11 factors and 12

experimental runs (Table 2-1). MgO % was determined using chemical analysis.

Chemical analyses were performed using wet chemical methods, acid attack (digestion)

method as described below.

Central Composite Design

A central composite design was used to further investigate the three most

significant factors (acid concentration, PVA concentration, and particle size) determined

from the screening design. Five levels were used. The central composite experimental

design had 17 experimental runs (Table 2-2 and Figure 2-2). For each run, the products

are chemically analyzed as above-mentioned and the MgO % and MgO removal % were










calculated for all the experimental runs. The computer program, Design expert (SAS

Institute, Inc.), was used to perform the statistical analysis for the central composite

design. The data was analyzed by fitting the response variables to a second-order

polynomial model.

Table 2-1. Experimental Plackett-Burman design for 11 variables

Run No. Variable Levels
1 2 3 4 5 6 7 8 9 10 11
1 + + + + + +
2 + + + + + +
3 -
4 + + + + + + -
5 + + + + + +
6 + + ++ + +
7 + + + + + +
8 + + + + + +
9 + + + + + + -
10 + + + + + +
11 + + + + + +
12 + + + + + +

Plackett-Burman Variables Used in the Reactive Flotation Study
Variables Low Level (-) High Level (+)
1) Acid conc 1 % 3 %
2) PVA conc 1 % 3 %
3) dummy *
4) dummy
5) PVA M.W 60,000 150,000
6) Degree of hydrolysis 88 % 99%
7) Time of drying 0 2 h
8) dummy
9) Particle size -0.5mm 5-9 mm
10) dummy
11) dummy
dummy variables are used to calculate the variance of the experimental
runs


















-_X
*--------------






Figure 2-2. Five-level, rotatable central composite design. The X, Y, and Z axes
represent the 3 variables, sulfuric acid concentration, PVA concentration, and
particle size. The circles represent each experimental run.

Table 2-2. Rotatable central composite design with 5 levels and 3 variables
Run No. Acid conc PVA % Particle Size


-1
-1
-1
-1
+1
+1
+1
+1
-1.68
+1.68
0
0
0
0
0
0
0


-1
-1
+1
+1
-1
-1
+1
+1
0
0
-1.68
+1.68
0
0
0
0
0


+1
-1
+1
0
0
0
0
-1.68
+1.68
0
0
0


Levels
Variables -1.68 -1 0 +1 +1.68
Acid conc. (%) 0.32 1 2 3 3.68
PVA, (lb/t) 0.6 2 4 6 7.4
Particle size, mm -0.5 0.5-1 1-2 2-5 5-9









Flotation Procedures for Screening and CCD Designs

Using 300 ml (3 % H2SO4) in 400 ml beaker, particles were pre-coated by spraying

3 % PVA solution (using a mist delivery nozzle) then added to the acidic solution. The

experiment was left for 5 min. Dolomite floats to the surface, which was separated by

decantation on a screen. The products (floated and unfloated fractions) were dried,

weighed, and chemically analyzed.

Factorial Design for Conditioning with PVA before Flotation

This design was used to study the factors affecting the conditioning step with PVA,

which is a promising step for reducing PVA consumption. Table 2-3 shows the design

and levels used.

Table 2-3. Factorial design for conditioning with PVA
Run No. PVA Pulp density Conditioning time, min
concentration, % (S/L ratio)
1 -1 -1 -1
2 -1 -1 +1
3 -1 +1 -1
4 -1 +1 +1
5 +1 -1 -1
6 +1 -1 +1
7 +1 +1 -1
8 +1 +1 +1
9 0 0 0
10 0 0 0
11 0 0 0

Levels
Variables -1 0 +1
PVA concentration, % 0.25 0.625 1
Pulp density 30 % 50 % 70 %
Conditioning time, min 2 11 20

Flotation Procedure for Conditioning Statistical Designs

50 gm of ore were added to 1 % PVA solution in a 600 mL beaker according to

specific solid/liquid ratio. The slurry was mixed for required time at 300 rpm (using 2.5









cm magnetic bar). After the conditioning time is elapsed the solids were screened, the

solids were used for flotation in acidic solution and the filtrate solution was taken to PVA

analysis to determine the PVA residual concentration.

Chemical analysis: About 0.5 gm of the dried and ground representative sample

were digested in 50 ml of aqua regia by boiling on hotplate until the reaction complete.

After cooling, this solution was filtered through a Whatman 42 filter paper into 1000 ml

volumetric flask. The filter paper and residue were then washed at least five times to

remove all the traces of dissolved salts and acid. The filtrate was diluted with distilled

water and thoroughly mixed and the concentrations were measured using Inductively

Coupled Plasma, ICP, emission spectrometer, (Perkin Elmer Optima 3200RL Optical

Emission Spectroscopy, Norwalk, CT). ICP was calibrated using AFPC rock check

No.22.


Standard sample concentrations were measured from time to time in the course of

the analyses to check the accuracy of the calibration curve. Five replicates were taken and

averaged for each element. The following wavelengths were used:

Element Wave lengths, nm
Ca 315.887, 317.933, 393.366, and 396.847
Mg 279.077, 285.213, and 279.553
P 213.617, and 214.914
Fe 238.204, 239.562, 259.939, and 234.349
Al 308.215

Density and Surface Area Determination

Densities of powders were measured using a Quanta Chrome ultrapycnometer. The

specific surface area (m2/g) of dolomite and apatite particles was determined using

Quanta Chrome NOVA 1200 instrument. (Quantachrome Corp., Boynton Beach, FL).









The analysis was performed using a five-point BET (0.10, 0.15, 0.20, 0.25, 0.30) using

Nitrogen gas. The particles were outgased at 600C for 24 hours before analysis.

PVA Preparation

PVA was kindly supplied by Celanese chemicals Co., USA. Different PVA types

with various ranges of molecular weights and degree of hydrolysis are used in screening

factorial design, namely:

Type Average Molecular Wt. Degree of Hydrolysis, %
Celvol 165 150000 99
Celvol 540 150000 88
Celvol 305 60000 99
Celvol 203 60000 88

In the rest of the study, PVA, Celvol 165, was used. PVA flakes were gradually

dissolved in deionized water at 90 C with continuous mixing by magnetic stirrer and

heated at 90 OC for 2 h to produce different PVA concentrations (0.5, 1, 2, 3, and 4 %).

Spectrophotometric Determination of PVA

PVA solution of certain concentration treated with 25 ml of 4 % boric acid solution

and 2 ml of iodine solution (prepared from 1.27g of iodine and 25 g of KI/1), in that

order. The resulting solution is diluted to 100 ml and kept at 250C and its absorbance

measured at 690 nm against a blank solution containing the same amount of boric acid

and iodine solution. Beer's law applies in the concentration range of 0-40 mg of PVA/1 of

solution [Finch, 1973; 1992]. Absorbance spectra were taken using ultraviolet/visible

spectrophotometer (UV-Vis spectrophotometer, Perkin-Elmer Lambda 800). All spectra

were taken at room temperature.









Static (Equilibrium surface tension)

Equilibrium surface tensions were measured for freshly prepared solutions by the

Wilhelmy plate method at room temperature. The platinum plate was always cleaned and

heated to a red/orange color with a Bunsen burner before use.

Dynamic Surface Tension (DST)

Maximum bubble pressure method

The dynamic surface tension (DST) measurement is important in the dynamic

interfacial processes where the equilibrium surface tension is hard to be achieved. The

DST can be measured by different methods such as: the drop weight [Jho and Burke,

1983; Miller et al., 1993], oscillating jet [Thomas and Hall, 1975], capillary wave

[Kelvin, 1871], growing drop technique [Macleod and Radke 1993], and the maximum

bubble pressure method [Mysels, 1986; Ross et al., 1992]. The maximum bubble pressure

(MBP) technique is the most commonly used technique for the measurement of DST, and

has been applied to a variety of surfactant and polymer solutions [Fainerman et al., 1994;

Tamura et al., 1995]. The physical principle behind the MBP measurement is the Laplace

pressure; the pressure inside a curved liquid interface is higher than the ambient. This

excess pressure (P) can be calculated from the Laplace equation [Adamson and Gast,

1997].

2y
P = 27 + pgh
r

Where y is the surface tension, r is the radius of curvature of the bubble, p is the

liquid density, g is the gravitational constant and h is the depth of the bubble in the liquid.

The first term expresses the Laplace pressure due to the curved gas/liquid interface, and

the second term is the hydrostatic pressure due to the liquid height above the forming









bubble. The first term will vary during the life cycle of the bubble, while the second term

will remain constant. Figure 2-3 shows a typical cycle of a bubble and the resulting

pressure within the capillary. After a bubble breaks off from the capillary tip, the pressure

is the lowest. As more gas flows into the capillary, the pressure builds up as the gas is

pushed out of the capillary and the radius of curvature at the tip decreases. During this

expansion process, surfactant is populating the new interface and acting to lower the

surface tension. At the point of minimum interface radius of curvature, where a

hemisphere of gas is formed at the capillary tip, the pressure reaches maximum.


Pressure




Capillary
immersed in
.,e liquid


Point of PM U


Figure 2-3. Characteristic bubble-pressure vs. time curve in MBP.

Both the minimum radius of curvature and the surface tension, as described by the

Laplace equation, govern the maximum pressure experienced. On the incremental

addition of gas, the bubble expands out of the capillary tip and the radius of curvature

gradually increases. This results in a drop in the Laplace pressure, and a resulting rapid

expansion of the bubble. At some point, the bubble breaks off from the capillary tip and

the whole process starts again.










Dynamic surface tension setup

The maximum bubble pressure apparatus was constructed using a differential

pressure transducer purchased from Omega Engineering, Inc. (Stanford, CT), with a

sensitivity of 0 to 10 in. (25 cm) H20 (0 to 2500 Pa). A #23 steel needle was used as a

capillary, with nominal 0.025 in. (0.64 mm) external diameter, 0.013 in (0.33mm)

internal diameter, and a flush cut tip. The capillary diameter was chosen so that the

various resistance of water to bubble growth could be ignored. Such internal and viscous

effects are a potential source of error in these measurements that need to be taken into

consideration [Garrett and Ward, 1989]. All measurements were conducted with the

capillary tip 1 cm beneath the liquid surface. CO2 gas was used as the bubbling gas to

simulate the gas produced in the reaction of acid with dolomite and an oscilloscope

connected to the pressure transducer was used to determine the bubble frequency and the

dynamic surface tension (Figure 2-4).




Rotameter
Pressure Voltage
Pressure
___ -'- Transducer

Oscilloscope
1.0 cm depth
A ir F low........................... .

Polymer Bubble formation
Solution

Figure 2-4. Setup for the measurement of dynamic surface tension by maximum bubble
pressure method.

Contact Angle

The angle formed at a point on the line of contact of three phases, of which at least

two are condensed phases, by the tangents to the curves obtained by intersecting a plane









perpendicular to the line of contact with each of three phases. One of the phases must be

a liquid, another phase may be solid or liquid and the third phase may be gas or liquid.

In other words, it is the angle included between the tangent plane to the surface of

the liquid and the tangent plane to the surface of the solid, at any point along their line of

contact. The surface tension of the solid will favor spreading of the liquid, but this is

opposed by the solid-liquid interfacial tension and the vector of the surface tension of the

liquid in the plane of the solid surface.



Gas


Ys Liquid
Solid


Figure 2-5. Contact angle and its relation with surface tension

Equilibrium wetting properties of liquids and solutions can be interpreted in terms

of the balance of surface tensions (Figure 2-5).

Ysg -Ysl= Yg COS 0

Measurement of Contact Angle

The contact angle goniometer, Figure 2-6, is a device mounted on the optical bench

to examine a single liquid drop or gas bubble resting on the smooth, planar, solid

substrate. The drop/bubble is illuminated from the rear to form a silhouette, which is

viewed through a telescope connected to computer. The image of the drop/bubble appears

on the computer monitor by which the brightness and contrast, focusing and amount of

illumination can be adjusted. After adjusting the image the contact angle can be

measured.









microscope videocamera


light source



frame-
grabber
motor-driven syringe computer

Figure 2-6. Contact angle measuring apparatus

Surface Characterization by FTIR

The spectorometer used for FTIR was a Magna-IR760 spectrometer by Nicolet in

transmission setting. As for the spectra recorded in transmission mode, KBr pellets were

prepared for the background measurements. Another pellets were prepared by mixing

about 1 mg of filtered powder with 50 mg of KBr. Transmission spectra were recorded

using a DTGS detector, with 128 scans and 4 cm-1 resolution.

Zeta Potential Measurements

In the zeta potential measurement tests, 1 g of ground mineral samples was added

into a 250 ml beaker in which 100 ml 0.003 M KNO3 solutions were added. The

suspension was conditioned for 3 min during which the pH was adjusted, followed by 5

min of conditioning after adding the polymer. It was then allowed to settle for 3 min, and

about 10 ml of the supernatant was transferred into a standard cuvette for zeta potential

measurement using a Brookhaven ZetaPlus Zeta Potential Analyzer. Solution temperature

was maintained at 25 C. Ten measurements were taken and the average was reported as

the measured zeta potential.

Adsorption

These studies were carried out at 250C using 0.5gm mineral sample in 50 ml

solution having the desired PVA concentration and the ionic strength fixed at 3X10-3 M









using KNO3. One set of experiments was performed first to determine the effect of

conditioning time at a fixed pH (pH 7) and PVA concentration was 100 ppm (3.33X10-8

M). Then set of experiments was also carried out as a function of pH at the same PVA

concentration. Adsorption isotherm was also determined for PVA/dolomite, PVA/apatite,

PVA/dolomite/apatite supernatant, PVA/apatite/dolomite supernatant systems at pH 7

and 3X10-3 M KNO3 as an ionic strength. After the conditioning step, the suspension

was centrifuged at 3000 rpm for 5 min using an IEC-Medispin centrifuge (Model 120).

Then a volume of the clear solution was withdrawn for measurement of the PVA residual

concentration.

In adsorption kinetic experiments, a 0.5 gm of dolomite or apatite were added to

100 ppm (3.33X10-8 M) PVA solution a 30 ml screw-capped bottle and was shaken at

room temperature using Wrist hand shaker for a given recorded time (0.05, 0.083,

0.0166, 0.25, 0.5, 1, 2, 4, 6, 8, 10, 16, 20, 24 h). After that the contents of each bottle

were allowed to settle, followed by centrifugation step using an IEC-Medispin centrifuge

(Model 120). The amount of PVA adsorbed was determined by difference between the

initial and final concentrations measured spectrophotometrically with a Uv-vis

spectrophotometer (UV-Vis spectrophotometer, Perkin-Elmer Lambda 800). These

experiments were used to establish the equilibrium time for adsorption of PVA on

dolomite and apatite. This equilibrium time was used as contact time in adsorption

isotherm experiments.

Dissolution Kinetic Experiments

Dolomite specimens (1-2 mm and 0.2-0.3 mm), uncoated and coated with PVA,

were added to 2000 ml aqueous medium (3 % H2SO4) at 23 + 0.50C to carry out 120 min

static dissolution tests. After a definite time interval, solution samples were collected









periodically and concentrations of Mg2+ and Ca2+ were determined with ICP. The

relations of concentration, C, with time, t was plotted to explore the dissolution kinetics

of the dissolution process.

Pilot Scale Experiments
The Sluice

The pre-conditioned material is introduced into a feed box, which contains 3 %

sulfuric acid. The reaction of sulfuric acid with particles starts in the feed box forming

bubbles around dolomite particles and creating the required density difference for the

separation in that device. The particles soon enter the moving stream and, because of the

bubbles on dolomite particles, they settle at lower rate and float to the surface when the

enough bubbles formed and carried away till they reach the lip of the trough and

discharged with liquid overflow. Since phosphate particles do not produce C02, and have

no bubbles at their surfaces, they are collected at the bottom of the trough (Figure 2-7).


Pre-conditinned Feed
3% Sulfuric acid


O Dolomite Reiect F
O Feed Box
O O
* Phosphate
Trough angle
Inclination angle to horizontal
Concentrate
Figure 2-7. Schematic diagram for separation of dolomite from phosphate in sluice

Sluice Experiments

250 gm of ore (a mixture of dolomite and phosphate), with particle size 1-2 mm,

were conditioned in 1 % polyvinyl alcohol solution for 5 minutes, then screened to

separate the solids from PVA solution. The screened solution was analyzed to determine

the actual PVA consumption by depletion method. Or the material was sprayed with the






31


equivalent amount of PVA and was tumbled to attain a good coating. After that, the

coated solids were poured into sluice feed box which the sulfuric acid and the reaction

starts to generate CO2 bubbles. The particles move through the sluice at flow rate 125

ml/sec (2 GPM). The floated fraction, dolomite, was collected on 0.5 mm screen and the

sink fraction, phosphate, was collected in the sluice trough. The floated and sink products

were analyzed for MgO, P205, CaO, and insoluble residue (I.R.).














CHAPTER 3
TECHNICAL ASPECTS OF REACTIVE FLOTATION: PRELIMINARY TESTS

Introduction

The reactive flotation process, as mentioned earlier, requires certain conditions to

give good results and separate dolomite from phosphate rock. The main requirements for

RF to work properly are the acidic medium and surfactant or polymer, which attaches to

the dolomite, to allow the acid to diffuse through but at the same time remain

impermeable to the CO2 gas produced by the reaction. Moreover, the formation of CO2

will lead to stretching of the membrane-like surfactant layers, which requires an elastic

behavior of that membrane. The elasticity of the membrane formed around the particle

will then allow the formation of stable bubbles. The stable bubbles are the main criterion

in RF to float the dolomite particles and separate them from others.

At the starting point of this process, the most well behaved acids and surfactants,

under RF conditions, were not known. Different acids and surfactants can be used but it

was unknown which one would best fulfill the previously mentioned requirements for the

RF process. For that reason, in the current study, preliminary tests were conducted using

different acid types (sulfuric, hydrochloric, nitric, acetic) within a particular

concentration range (0.5 4 % v/v) as well as different types of surfactants (anionic,

cationic, and non-ionic), which were prepared as 1-2 % surfactant solution and used in

two different ways: (1) surfactant was added to acidic solution and/or (2) surfactant was

used to coat the particle before adding the particle to the acidic solution. Also, poly-vinyl-









alcohol (PVA) was used in this study. Vegetable and corn oil were used at the acidic

solution/ air interface and oil height was 0.5-0.6 cm.

List of Potential Surfactants: Surfactants Screening

A list of potential surfactants used in this study, are given in Table 3-1. The list

contains different types of surfactants, (i.e., cationic, anionic, and non-ionic, as well as

polymers).

Table 3-1. Surface-active agents used in RF tests
Surfactant Chemical Name Type
Arquad 12-50 Dodecanaminium+isopropyl alcohol Cationic
Lilamine N-3-aminopropyl-N-tallow alkyltrimethylenedi- Cationic
Armac HT Amines, hydrogenated tallow alkyl acetates Cationic
Armid HT Amides Cationic
Armeen 12 D dodecanamine Cationic
Ethofat Tall Oil Anionic
SDSO3 Sodium dodecyl-sulphonate Anionic
SDSO4 Sodium dodecyl-sulphate Anionic
Oleic acid Oleic acid Anionic
Arlacel Sorbitan sesquioleate Non-ionic
Span-20 Sorbitan monolautrate Non-ionic
G-1096 Polyoxyethelene-sorbitol hexaoleate Non-ionic
Brij-97 Polyoxyethelene oleyl ether Non-ionic
Arlatone T Polyoxyethelene polyofatty acid ester Non-ionic
Tween-21 Polyoxyethelene Sorbitan monolautrate Non-ionic
Tween-85 Trioleate Non-ionic
PVA Poly-Vinyl-Alcohol Non-ionic

Initial Screening Tests

A 100-pound sample of high-dolomitic phosphate oversize pebble was obtained

from the IMC Four Corer's mine. This is not "normal" high MgO rock, but the

oversized high MgO rock that is removed from pebble. As such, neither the screen

weight fractions nor the chemical analyses are representative of pebble. However, the

rock is representative of the high-dolomitic rock that needs to be separated. The rock was

screened, and each fraction is chemically analyzed in Tables 3-2 and 3-3.









Table 3-2. Size analysis of the dolomitic phosphate sample
Size, mesh Size, mm Wt. % % Cumulative % Cumulative
(passed) (retained)
+ 3/8 in +9.5 11.62 100.00 11.62
- 3/8 in +3.5 9.5+5.6 65.36 88.38 76.98
-3.5+6 -5.6+3.36 18.14 23.02 95.12
-6+9 -3.36+2 2.05 4.88 97.17
-9+16 -2+1 1.6 2.83 98.77
-16 1 1.23 1.23 100
100.00

Table 3-3. Chemical analyses of the dolomitic phosphate sample
Size, mesh P205 % CaO % MgO % Fe203 % A1203 %
+3/8 in 19.86 32.23 4.02 0.93 0.52
-3/8 in +3.5 21.25 36.34 3.43 1.15 0.84
-3.5+6 17.09 27.92 2.34 1.32 0.86
-6+9 24.32 38.90 2.75 1.08 1.17
-9+16 20.42 28.71 2.12 1.27 1.07
-16 13.62 22.75 2.44 1.13 0.95

Since most of the rock was relatively coarse, a portion of it was crushed and re-

screened to obtain smaller fractions that could be used in the tests.

Specific Tests

The results of some preliminary testing are shown in the following paragraphs in

terms of acid type and dosage, surfactant type and dosage, particle size, and using of oil

layer at the water/acidic solution interface.

Acid type

Different acids (H2SO4, HC1, HNO3, and Acetic acid) were used. Inorganic acids:

HC1, HNO3, and H2SO4 gave the same results at 2 % acid concentration. On the other

hand, the acetic acid (RCOOH) formed a very small number of bubbles at 2 % acid

concentration. Increasing the concentration of acetic acid to 5 % gave no significant

variation in bubble formation, which means that the organic acids are weak acids.

Consequently, a large amount of organic acids is needed relative to inorganic ones.









Acid dosage

Since all the inorganic acids behave in the same manner, sulfuric acid was used in

the rest of the experiments. Table 3-4 shows the effect of acid concentration on the

bubble formation rate, amount of bubbles formed, and particle floatability that were taken

as a criterion to compare the results. The surfactant used for coating the dolomitic particle

was dodycyl sulphonate (SDS03).

Table 3-4. Effect of sulfuric acid concentration
Sulfuric acid concentration, %
0 0.25 0.5 1 2
Bubble Very slow Slow Fast IRpid
formation rate

Amount of Very small The interval Increasing the Continuous Continuous
bubbles number of between formation rate and formation of and quick
formed bubbles (about 5 of two bubbles number of bubbles but at formation of
bubbles for 10 was about 30 bubbles rate higher than many
minutes then no seconds formed 0.5 % bubbles
bubbles formed)

Flotation of No flotation Float after 5-10 Float after 1
dolomite minutes minute
particle

From Table 3-4, we notice that the reaction between dolomite and acid to produce

CO2 decreases noticeably with decreasing acid concentration and the flotation of

dolomite particle takes longer time (5-10 min) in 1 % acid than in 2 % acid.

Consequently, the 2 % sulfuric acid concentration is the most suitable acid concentration

for bubble formation in terms of both bubble formation rate and amount of bubble

formed. Because of the wide gap between 1 % and 2 % acid concentration another set of

experiments were conducted as shown in Table 3-5 to get the optimum acid

concentration.










Table 3-5. Effect of sulfuric acid concentration on the bubble formation


Sulfuric acid concentration, %
1 1.2 1.4 1.6 1.8 2


Bubble Increases
formation rate

Amount of
bubbles Continuous and small No. of tiny bubbles Continuous & large No. of tiny bubb
formed

Flotation of Takes 20 minutes to Floats and stays at water/oil Floats and stays
dolomite float, not stable (particle (W/O) interface for 5 min. Then (W/O) interfac
particle goes up and down) oscillates within 2 min intervals

Table 3-5 shows that the flotation at 1 % & 1.2 % is not stable and flotation

occurs after the particle loses part of its weight due to reaction with acid. Accordingly,

this concentration deals with a small particles (smaller than 1mm) rather than large

particles. The bubble formation rate is decreased with the acid percentage from 2 % to 1

%, but as the difference was narrower between 1.6-2 %, 1.6 % acid concentration was

found to be optimal. The effect of acid concentration on the RF criterion was

schematically summarized in Figure 3-1.


les


at
e


A B C
Bubble Number of Flotation
formation bubbles time
rate formed




Acid conc. Increases Acid conc. Increases Acid conc.

Figure 3-1. Effect of acid concentration on: A) Bubble formation rate, B) Number of
bubbles formed, C) Flotation time.

Surfactant type

Table 3-6 shows the anionic, cationic and non-ionic surfactants used. According to

RF criterion, the performance of Anionic surfactant was superior to Non-ionic, which

was superior to Cationic. Anionic surfactants, especially SDSO3, formed stable


Increases


\










"membranes" that captured CO2 and persisted for 10 minutes. This may be due to its

ability to work at low pH. Therefore, SDSO3 was used in the next experiments.

Table 3-6. Preliminary tests of high dolomitic phosphate with different surfactants
Surfactant Name Remarks
Arquad 12-50 (1%) stable bubbles for 20-30 sec, particle 2-3 mm can float

Lilamine (1%) less stable bubbles, stay 10 s, particle does not reach to surface of the solution
(air-water interface)

Armac HT (1%)

Armid HT (1%) surfactant precipitated in the solution
Armi HT 10/o


Armeen 12 D (1%)

Ethofat (1%)
SDSO3 (1%)
(2%)
SDSO4 (1%)
(2%)
Oleic acid


Formation of bubbles on the particle surface then particle floats

Bubbles form and go up to solution surface, but particle doesn't float
Particle takes 2-3 sec to float

Bubbles form and go up to solution surface, but particle doesn't float
Flotation rate in case of SDSO4 < Flot.rate in case of SDSO3

Added as it is, particle stays at surface of the solution (air-water interface) with
formation of many small bubbles.


Arlacel Common observations for non-ionic surfactants:
Span-20 No significant change in behaviour of different non-ionic surfactants used
G-1096
Brij-97 The flotation of high dolomitic particle after 3-5 seconds and stay at the surface,
Arlatone T while the low dolomitic does not float.
Tween-21
Tween-85 Formation of stable bubbles on the floated particle surface

Surfactant dosage

The results of different dosages of surfactant sodium dedocyl sulfonate (SDS) are

shown in Table 3-7 in terms of bare and coated particles. It is indicated from Table 3-7

that bare particles, without coating, forms bubbles quickly and in large quantity due to

rapid dolomite/acid reaction but the bubbles are not stable at the interface where they can

be collected.









Table 3-7. Effect of surfactant concentration (SDSO3, 2%)
SDSO3 (2 %)
2% 4% 6%
Many bubbles formed Many bubbles Many bubbles
Particle Small particle (1-2 mm) formed formed
without floats Particles (1-2 Particles (1-2
coating Large particle (3-4 mm) mm) and (3-4 mm) mm) and (3-4 mm)
goes up and down float float

Particle
coated with Many bubbles formed -small particle floats-large particle does not float
SDSO3

On the other hand, the coated particles take more time to float due to the diffusion

of acid through the surfactant layer around each particle. Also, a greater number of

bubbles are formed when no coating is used. Finally, when coating is not used each

bubble forms as a separate bubble, while formation of bubbles clusters occurs when with

a coating with SDS is used.

Increasing the surfactant concentration increases the flotability of the particles and

large particles (3-4 mm) can float at high surfactant concentrations of up to 4 %; after

that, there is no noticeable change in floatability-(i.e., 6 % is very much similar to 4 %).

The oscillated motion of large particles (3-4 mm) for short period of time (3-5 sec) was

noticed at 2 % surfactant concentration; however, the same size floats without oscillation

at 4 % and 6 %. This means more surfactant is needed.

Particle size

The particle size effect on the RF process was studied for coated and uncoated

particles. The observations of different size ranges were recorded in Table 3-8 which

indicates that the coating affects the stability of the bubbles on the particle surface as well

as the stability of the floated particle at the interface; however, even uncoated particles









release many bubbles and float quickly for very short time due to their rapid reaction with

acid.

Table 3-8. Effect of particle size on the dolomitic particle floatability
Particle Size, mm

0.5-1 1-2 2-4 4-6
Without Particle floats and Particle floats for few No flotation -the particle oscillates
treatment stays at water/air seconds then oscillates without reaching the interface
interface

With Floats and stays at Floats after 30 sec and Oscillates and Floats after 1
treatment interface stays at (w/a) interface finally stays at min then
w/a interface oscillates for 5
min


This rapid rate of reaction causes rapid reduction in particle weight. In addition, it

causes the production of many bubbles at a faster rate than bubbles-particle detachment,

leading to presence of uncoated particle at the interface, although for shorter time than

coated ones. But once the uncoated particle reaches the interface, the bubbles will not be

stable anymore due to high surface tension, which is the reverse of coated particles.

Large size particles need more bubbles; the bubbles formed were not enough to lift

the particle causing the particle to oscillate up and down. On the contrary, the small

particles 1-2 mm and smaller do not oscillate and float directly to the interface.

To improve the stability of the floated particles at the interface, the reduction of the

surface tension is required. Therefore, the oil layer was used at the interface for that

purpose.

Oil-Surfactant Experiments

Addition of an oil layer, either vegetable or corn oil, to the acidic solution/ air

interface was attempted with different types of surfactants to enhance the bubble stability

at the interface, as shown in Table 3-9. The selected surfactants for this set of









experiments were the best ones from Table 3-6. The particle was coated with the

surfactant before its addition to acidic medium.

Table 3-9. Effect of presence of surfactant and oil layer on particle flotation
Surfactant Type Observations
2 % sulfuric Arquad Cationic Formation of bubbles due to dissolution of
acid solution + Lilamin dolomite, but no flotation.
oil layer Ethofat Bubble formation,
SDSO3 Anionic Particle floats to water/oil interface for 10 min
SDSO4 and then comes back to acidic solution.
2 % sulfuric Arquad Cationic Formation of cluster of bubbles on particle
acid solution + Lilamin surface, but no flotation.
1 % surfactant Ethofat Bubble formation and particle oscillates and
SDSO3 Anionic the bubble bursts at water/air interface.
SDSO4
2 % sulfuric Arquad Cationic The same as before
acid solution + Lilamin
1 % surfactant Ethofat Bubbles form No flotation
+ oil layer SDSO3 Anionic Bubbles form on particle surface and particle
SDSO4 floats to water/oil interface then to oil/air
interface

It is clear that, as can be seen in Table 3-9, the oil layer enhance the bubbles'

stability on the particle and at the interface. When the particle floats to the acidic

medium/oil interface, the floated particle stays at the interface for up to 10 min. The

presence of oil layer may add another layer, an oil layer, in addition to the surfactant

layer on the particle surface, although this would depend on the adsorption of the

surfactant to the particle as well as the type of the surfactant and its interaction with oil.

From Table 3-9, it was observed that the presence of a low percentage of surfactant

(1 %) in the acidic solution slightly increases the stability of bubbles in the absence of an

oil layer. The presence of 1 % surfactant in the solution may reduce the fast detachment

of surfactant molecules from the particle surface through reduction of the diffusion of

surfactant molecule to bulk solution.









By using acidic solution in combination with 1 % surfactant and an oil layer (Table

3-9), it was found that the oil layer causes more stable formation of bubbles on the

particle when the particle floats to oil/air interface. The particle does not go back into the

acid solution but stay at oil/ air interface. Consequently, large particles of up to 3 mm

can float in the presence of the surfactant and oil layer.

SDS is a good surfactant under these experimental conditions. However, Ethofat

and cationic surfactants did not work well in the presence of surfactant mixed with acidic

solution. This may be due to the interaction between the oil layer on the particle and

those surfactants possibly causing the formation of a non-flexible surfactant layer, which

cannot capture the CO2 gas and cannot form the bubbles required for flotation.

Poly-Vinyl-Alcohol (PVA) Testing

PVA was used as a viscous polymer to coat and to float the dolomite particles. The

effect of acid concentration, particle size, and different PVA concentration were studied.

Effect of acid concentration

PVA forms a membrane on the particle. This membrane needs a high acid

concentration to penetrate it and to perform the reaction between the acid and particle

surface. It was observed that there were a very small number of bubbles generated.

However, most of the bubbles formed a cluster on the particle surface, which increased

the volume of the bubbles at the surface and floated the particle. The floated particles

were not stable at the beginning, going up and down at interface, but ultimately staying at

the interface for long time (sometimes more than 2 days).

On the other hand, PVA also floated the low dolomite-content particles, which

were able to form bubbles. This observation is due to PVA's very low permeability by

CO2, which makes it the best among the surfactants used. By increasing the PVA









concentration, longer time was taken to form a bubble and to float the particle, which

requires high acid concentration, but in this case it became possible to float large particle

sizes (up to 8 mm).

Table 3-10. Effect of acid concentration
Acid concentration, %
0.5 1 1.5 2
Particle Formation of cluster of bubbles Cluster of bubbles formed
coated with Very low bubble formation rate Low bubble formation rate
PVA No particle flotation (up and down at Particle floats
1.5%)

From Table 3-10, it is evident that the findings were that the PVA forms a

membrane on the particle. This membrane needs a high acid concentration to penetrate it

and to perform the reaction between the acid and particle surface to release the gas, which

is responsible for floating the particle. No quick release of bubbles was observed at low

acid concentrations, but rather only a very small number of bubbles at the beginning;

furthermore, the rate of bubble formation and particle flotation was very slow. After a

while, an increasing number of bubbles appeared and clustered on the particle surface,

which then caused the particle to float.

Moreover, at low acid concentrations, the floated particles were not stable, going

up and down at the interface due to absence of surfactant. Even at high acid

concentrations, the acid takes time to penetrate the PVA membrane and react with

particle surface. For that reason, the bubble formation rate was low. But after the

formation of bubbles began to cover the particle surface with clusters of bubbles, the

particles started to float.

The acid concentrations of less than 2 % were not effective due to the high

viscosity of PVA membranes, which requires a high concentration difference to permeate









the membrane and the reach the particles' surface. Because the previous set indicated that

the 2 % acid concentration was optimal, another set of experiments was conducted at

higher acid concentration (> 2 %) under the premise that a concentration higher than 2 %

would be even better. Therefore, additional experiments were conducted using 2.5-4 %

acid concentrations. Table 3-11 shows the results of those experiments.

Table 3-11. Effect of acid concentration above 2 %
Sulfuric acid concentration, %
2.5 3 3.5 4
Bubble formation Increases with increasing acid conc. %
rate
Amount of bubbles Cluster of bubbles formed on the Rapid reaction no stable
formed particle surface bubbles are seen on the
surface (bubbles released
in high rate from particle
surface)
Flotation of Particle Floats Particle floats Particle oscillates and
dolomite particle Is more stable than Less stable finally goes down
higher acid conc. than 2.5-3 %

There was no flotation at acid concentrations above 3 % due to the high bubble

formation rate and absence of stable bubbles that can attach to the surface of the particle

and float it. The bubble formation rate increases with increasing acid concentration, 4 %

> 3.5 % > 3 % > 2.5 %; however, 2.5-3 % resulted in the most stable bubbles.

Different PVA concentrations (2 %, 3 %, and 4 %) were also used and the

experiments indicated that 3-4 % concentration is most suitable for dolomite flotation.

However, increasing PVA concentration increased the time it takes each particle to float.

Effect of particle size

Increasing the particle size increased the time needed to float the particle. This can

be explained by variation of surface area to weight of the particle ratio, which decreases

with increasing particle size. The results of these tests are shown in Figure 3-2.










30


20


10-


0
-1 1-2 2-5 5-9 +9

Particle size, mm


Figure 3-2. Effect of the particle size on the time needed to float the particle in 3 %
H2SO4 when the particle is pre-coated with 3 % PVA

PVA with acid vs. PVA on the particle surface

By using two beakers, one of them containing uncoated particles added to 3 %

PVA + 3 % acid solution and the other containing PVA coated particles added to 3 %

acidic solution, the comparison between the performance of different application of PVA

was obtained. Table 3-12 shows the results in terms of bubble formation, rate of

formation, and particle flotation.

When uncoated particles were added to the PVA+acid solution, the acid attacked

the particle surface. Consequently, the dissolution of dolomite is higher than in case of

coating the particle with PVA before adding it to the acidic solution. Presence of micro-

bubbles (cotton shape) at the particle surface indicated the dissolution of dolomite.

Bubbles were vertically distributed rather than horizontally in first beaker, while

the bubble distribution was horizontally uniform (spreading on the particle surface) in the

second beaker. The bubble formation rate is higher in the first case than in the second.









The flotation of the particles was better in the second case due to the presence of

relatively large bubbles and uniform bubble distribution. Despite rapid dissolution of

dolomite particles in the first case, flotation of the particles took a long time due to the

small size of the bubbles. In both cases, the particles floated stay at interface for a long

period of time (days).

Table 3-12. Comparison between coating the particle before adding it to acidic solution
and adding the particle to acid+PVA solution without coating
First beaker Second beaker
PVA + acidic solution in the beaker Particle was pre-coated with PVA
and the particle added without coating before adding it to acidic solution
Bubble Tiny bubbles were formed Relatively large bubbles were
formation rate formed

Amount of Cluster of the bubbles grows vertically Cluster of the bubbles grows almost
bubbles and cover parts of the particle horizontally and uniformly
formed surface- no uniform distribution of distributed on the particle surface.
the bubbles on the particle surface.

Flotation of Takes long time (hours) to float Takes short time (min) to float
dolomite
particle

Preliminary Testing Using PVA Coated Particles

In the following preliminary tests, all particles were pre-coated with PVA

Flotation of a Representative Sample

Flotation of a representative sample, a mixture of phosphate and dolomite, was

attempted in a one-liter beaker. The percentage of floated fraction by weight obtained

after 6 hours was about 22 % and un-floated fraction was about 78 %. It was noticed that

the smaller particle sizes (less than 1mm) floated immediately. It was then determined

that using small size fractions of about 1 mm coated with PVA would reduce the flotation

time with very low chance to dissolve the particle; it appears that good PVA coating









prevented rapid acid-attack to the particle. On other hand, we should take into account

that the PVA consumption will increase due to increased surface area.

Fraction of Representative Sample (-4+1.19 mm)

A bucket (11 in diameter and 15 in height) was filled with a solution of 15 liters of

water containing 3 % sulfuric acid and 3 % PVA. The water height in the bucket was

about 1 foot. Most of the particles were in monolayer form to avoid mechanical

entrapment of the particles.

After applying the finalized procedure, the MgO percentage in the representative

sample was reduced to less than 1 % of the sink fraction; P205 percentage was reduced to

less than 4 % (Table 3-13).

Table 3-13. Results of representative sample (- 4+1.19 mm particle size)
Sample Chemical analysis, % Recovery, %
Wt% MgO CaO P205 I.R. MgO CaO P205 I.R.
Float 14.55 13.21 32.56 2.71 6.89 75.1 13.73 2.33 10.01
Sink 85.45 0.75 34.83 19.35 10.55 24.9 86.27 97.67 89.99
Balance 100 2.56 34.50 16.93 10.02 100 100 100 100
Feed 100 2.6 34.78 16.84 10.32 100 100 100 100

Effect of Time on Weight Percentage of Floated Particles

Two samples of- 4+1.19 mm size were gathered at different flotation time (30 min

and 60 min). The samples were immersed in a beaker containing a solution of 3 % PVA

and mixed to ensure the coating of all particles with PVA before adding the sample to

acidic water (3 % sulfuric acid). The same bucket as in the previous test was used and at

the same conditions. Each experiment was observed for two days and the floated fraction

was collected. Most of the particles (about 90 %) floated within 30 minutes and about 10

% in the remaining two days of the experiment. The results are shown in Table 3-14.









Table 3-14. Effect of time on the flotation of- 4+1.19 mm particle size
Time, Chemical Analysis Recovery
min Wt% MgO% CaO% P205% MgO% CaO% P205%
30 Float 16.75 13.62 24.25 0.76 77.84 13.55 0.8
Sink 83.25 0.78 31.12 18.89 22.16 86.45 99.2
Balance 100 2.93 29.97 15.73 100 100 100
Feed 100 3.03 30.38 15.76 100 100 100

60 Float 17.44 13.6 26.17 0.94 78 15.22 1.03
Sink 82.56 0.81 30.8 19.06 22 84.78 98.97
Balance 100 3.04 29.99 15.90 100 100 100
Feed 100 3.03 30.38 15.76 100 100 100

The percentage of MgO was reduced to about 0.8 %; the percentage of P205 was

reduced to less than 1 % in the float fraction, which indicates that using PVA in a pre-

coating solution is a promising process for separation of dolomite from phosphate

pebbles.

Effect of Size on the Flotation

Two samples were crushed in a closed circuit to obtain the following sizes: -

4+1.19 mm and -3.36 +1.19 mm. The conditions were the same as in the previous two

tests. The results of these tests are shown in Table 3-15 within 5 minutes flotation time.

The percentage of MgO was reduced to less than 1 % (0.6 % of the un-floated fraction in

first experiment and 0.95 % in the second).

Table 3-15. Effect of particle size on flotation
Size, mm Sample Wt% Chemical analysis, % Recovery, %
MgO CaO P205 I.R. MgO CaO P20 I.R.
-4+1.19 Float 20.5 12.13 30.34 3.31 8.1 83.9 20.55 4.27 17.87
Sink 79.5 0.6 30.24 19.13 9.6 16.1 79.45 95.73 82.13
Balance 100 2.96 30.26 15.89 9.29 100 100 100 100
Feed 100 3.03 30.38 15.76 9.46 100 100 100 100

-3.36+1.19 Float 17.8 11.84 34.53 3.86 7.04 72.96 16.43 4 12.84
Sink 82.2 0.95 38.02 20.07 10.35 27.04 83.57 96 87.16
Balance 100 2.89 37.40 17.18 9.76 100 100 100 100
Feed 100 2.95 37.07 17.41 9.93 100 100 100 100









Summarizing Remarks

Separation of dolomite from apatite using CO2 generated in the chemical reaction

between dolomitic particles and slightly acidic media was explored by testing different

parameters effecting this process, including: acid type and concentration, surfactant type

and concentration, particle size, and use of polymer (PVA). The results were promising

with anionic surfactants, especially SDSO3, and Mr. Bubble solution with a concentration

of 1.6 % sulfuric acid; however, low dolomite-content particles did not float.

The most encouraging results were obtained with PVA, which floats the low

dolomite-content particles, in addition to floatation of large particle sizes. Additional

testing with a representative sample of ore mixture (phosphate and dolomite) showed the

ability to reduce the MgO content to less than 1 % by using a PVA concentration of 3 %

in an acidic medium concentration of 3 %. The next step will be the optimization of the

RF process using PVA as well as performance of this process under dynamic conditions.














CHAPTER 4
OPTIMIZATION OF THE REACTIVE FLOTATION PROCESS
AND PILOT SCALE TESTING

Introduction

In previous chapter, it was demonstrated that when PVA coated high MgO

phosphate rock is immersed in a 3 % sulfuric acid solution, effectively all the high MgO

particles will float to the surface leaving a sink phosphate rock phase that is a low in

MgO. In this chapter, the optimization of separation process using PVA as well as

development of a separation continuous process is discussed.

In this chapter, the RF is optimized using statistical designs (i.e., screening

statistical design and central composite design (CCD)). Also, the reduction of PVA

consumption was studied using statistical design, (i.e., factorial design). The tests show

that as little as less than one pound of PVA per ton of feed rock can be effective in

floating the dolomite. The tests also show that there is no significant adverse effect of

having the sulfuric acid solution saturated with calcium sulfate. Furthermore, pilot scale

testing of a simple sluice was carried out and demonstrated the effectiveness of this

approach in giving a good separation between the phosphate and dolomite particles.

Optimization of the RF Process

Screening Statistical Design

The MgO % removal in floated fraction, Table 4-1, was used as the response in

calculating the statistical effect of variables. The effect of variables are calculated as

follows:









Table 4-1. The MgO % removal in floated fraction for Plackett-Burman design.
Runs Response
(MgO % removal)
1 3
2 3
3 3
4 3
5 86
6 90
7 3
8 12
9 3
10 20
11 3
12 3


Re sponse(+ Re sponse
Ei = (4.1)
6

The variance is estimated by evaluating the effect of dummy variables and using

this equation:


0"2 = ef E (4.2)
n

where Ed = effect of dummy variable and n = number of dummy variables = 5.

The statistical significance of the effects is evaluated using the student t-test as calculated

using:


t- (4.3)
/ 2

where the degrees of freedom = 5, confidence level = 95 % and t,0.05 = 2.015.

Comparing the absolute t-values to 2.015 led to acceptance of variables with a higher t-

value and rejecting the variables with lower t-values. In other words, the variables

accepted were significant within 95 % confidence level. This comparison of the Plackett-

Burman design is presented in Table 4-2. The PVA molecular weight t-value is 2.761,









which is higher than 2.015. Nevertheless, the higher PVA molecular weight was used

because of its significance. From the Plackett-Burman design, the most significant

variables are acid concentration, PVA concentration, and particle size.

From the screening design, a model relating the MgO % removal to the different

variables could be represented by:

y = -91.75 + 14.83X1 +12X2 3.2X3, (4.4)

where y represents MgO % removal and Xi, X2, and X3 represent acid concentration,

PVA concentration, and particle size, respectively. All coefficients are statistically

significant close to 95 % confidence level. The negative sign for particle size coefficient

indicates that increase the particle size can lead to a decrease in the MgO % removal. On

the other hand, the positive acid concentration and PVA concentration values indicate

that an increase in both concentrations lead to higher MgO % removal. In order to

further investigate the interaction among these three significant variables with respect to

their effect on MgO % removal, a central composite design focusing on these three

variables with five levels was used.

Table 4-2. Plackett-Burman calculated t values for different variables. The decisions to
accept or reject the significance of variables on the bases of comparing t-value
to critical value at 95 % confidence level.
Factors Effect on MgO % removal Significant Variable
(t-value)*
Sulfuric acid concentration 2.69697* Accept
PVA concentration 2.181818* Accept
PVA Molecular Weight (MW) 2.969697' Accept
PVA degree of hydrolysis (D.H.) 0.181818 Reject
Particle size 2.45455* Accept
Drying time 0.333333 Reject
*Statistically significant (95 % confidence level)
"(+ ve) sign indicates more MgO % removal
"(- ve) sign indicates less MgO % removal









Central Composite Design

Central composite design (CDD) results of dolomite flotation experiments are

given in Figures 4-1 and 4-2 in terms of MgO removal % in floated fraction and MgO %

in sink (nonfloat) fraction respectively. The confidence interval is within 95 %. In other

words, the effects are statistically significant at the 95 % level. The standard deviation

and R-Squared for both of them are 13, 0.9287 and 0.36, 0.9287 respectively.

It was indicated, from these figures, that the % MgO recovery and MgO % in

concentrate are greatly and positively affected by increasing either acid concentration or

PVA dosage, (i.e., % MgO recovery increases from 30 to more than 90 % and MgO % in

the concentrate decreases from more than 2.1 to 0.6 respectively). However, particle size

negatively affects the % MgO recovery and MgO % in concentrate. With increasing

particle size the % MgO recovery decreases. At the maximum acid concentration and

PVA dosage, it decreases from 90 to 75 % and % MgO concentration in the concentrate

increases from 0.6 to 1.1 %.

As it can be seen from these results that the PVA consumption is high (about 4.5

lb/t), which is economically unfeasible, to get a concentrate contains < 1 % MgO with

high recovery > 90 %. Therefore, further study is needed to reduce that consumption,

which is discussed in next section.

Research to Reduce the PVA Consumption

From the results obtained from the experimental designs following the screening

the main factors, then studying the main factors, unfortunately, the PVA consumption

was about 4-6 lb/t (calculated according to used amount of PVA to certain weight of rock

including the losses on the coating device), which threaten the success of this process

economically. At this point, it was necessary to find a method to reduce the

consumption.












6 MgO Removal (floated) %



5-


4- A
74

3-



2--A
1.0 1.5 2.0 2.5

Acid concentration, %




6 MgO R







4- 14 34
5
-n\


S M RO Removal (floated) %



5- 93
5-K


-73 B


3 43
3-


2-
1.0 1.5 2.0 2.5


Acid concentration, %


1.0 1.5 2.0 2.5 3.0


Acid concentration, %



Figure 4-1. Effect of PVA dosage and acid cone. on MgO recovery % in floated fraction
at different particle size
A) Particle size = -0.5 mm
B) Particle size = 1-2 mm
C) Particle size = 5-9 mm








53






54


Mg O% in unfloated fraction MvgO% in unfloated fra@


I\ ) \
5- 5-

A B
4- 0.9 4-
1.3

1.3 3

3- 3-

1.0 1.5 2.0 2.5 3.0 1.0 1.5 2.0 2.
Acid concentration, % Acid concentration, %

S MgO% in unfloated fraction


5- C
C


4- 2.5 2.1 1.7 1.3 0.9

3-\
2.9


1.0 1.5 2.0 2.5 3.0
Acid concentration, %

Figure 4-2. Effect of PVA dosage and acid concentration on MgO % in Unfloated
fraction at different particle size
A) Particle size = -0.5 mm
B) Particle size = 1-2 mm
C) Particle size = 5-9 mm









In this regard many tests were conducted among these tests were:

* Using compatible compounds with PVA like starch and cellulose. It was found that
the presence of these compounds negatively affected the stability of the bubbles at
the interface.

* Using fine particles (- 40 mesh) with different PVA (1, 2, 3 %) and acid conc.(1, 2,
3 %). It was found that the 3 % PVA and 3 % acid were needed which is the same
condition as before and in addition the reaction was too fast due to the high surface
area of the small particles.

* PVA + Drimax (spreading agent): to spread the PVA on the particle surface and
then reduce the amount needed to cover the particles. The results of these
experiments indicates that there is an interaction between the PVA and Drimax in
such a way that prevented the formation of stable bubble at the particle / solution
interface, probably by interfering with the crosslinking of the polymer layers that is
necessary for the formation of a membrane and consequently stable bubbles.

* PVA + Boric acid: as it is in the literature [Finch, 1973; 1992], the boric acid and
borax are used in PVA crosslinking. Using the boric acid (5 % of PVA) helps in
reducing the PVA consumption due to polymer crosslinking but we did not go
further in these experiments because of toxicity of boric acid and environmental
reasons.

* PVA + Na2SO4: sulfate ions lead to coagulation of the PVA according to literature
[Finch, 1973; 1992]. It was found that the coagulation is not enough to float the
dolomite particle at low PVA concentration.

* Conditioning of the rock particles with PVA and screening it (or filtering it) to
recover the excess PVA. Actually, this step was a most promising one in which the
consumption of PVA was reduced to 1 lb/t instead of 4-6 lb/t in previous coating
procedure. The conditioning step (with about 1 % PVA) in the same manner as a
regular flotation is followed by a filtration step and calculation of the actual PVA
consumption.

On the other hand, it was found that the full coverage of the particle with PVA is

not needed since the formation of some bubbles may be enough to create the density

difference and by using sluice or spiral in which the dolomite particles will be lighter and

follow the liquid stream. In this manner, the dolomite particle can be separated from the


phosphate.







56


Experimental Design of the PVA Conditioning Step

Due to the high PVA consumption as indicated from experimental designs,

different methods were tested as mentioned before, the conditioning step as in regular

flotation circuits was tested since this step can reduce the consumption to one-fourth or

more (The PVA consumption was reduced to 1-2 lb/t from 4-6 lb/t). For that reason

statistical design with three factors, (i.e., conditioning time, PVA concentration, and pulp

density) was used. It is indicated, from Figure 4-3, that the PVA concentration is the main

factor and then the conditioning time while the pulp density (solid liquid ratio) has a very

slightly effect on the % MgO in the concentrate and % MgO recovery in floated fraction.



Cube Graph Cube Graph
MgO% in Concentrate ube
MgO recovery in floated fraction, %






0 o

m m
S................ 2C+ 846583 2 C+

C PVAConc, % C PVAConc, %

B- 29 282 C- B- 550 888 C-
A- A+ A- A+
A Conditioning time, mln A Conditioning time, mm


Figure 4-3. Cube graph for MgO % and MgO recovery %

Saturation Experiment

The CaCO3 was used to saturate the solution with calcium sulfate by adding CaCO3

to 3 % sulfuric-acid solution. The formation of the precipitate of CaSO4 indicated that the

solution was saturated. It was found that 1.78gm/l of CaCO3 would cause the precipitate

to form. After the formation of the CaSO4 precipitate, the flotation test was run as an

indication of the acid performance after its saturation. Table 4-3 shows the results of

these experiments before and after the saturation is reached.









Table 4-3. Effect of saturated acid on the RF
Before saturation After saturation
Wt% MgO% P205% Wt% MgO% P205%
Float 22.1 11.1 4.2 21.3 10.95 4.15
Sink 77.9 0.8 21.1 78.7 0.85 21.2

Pilot Scale Testing: Sluice Results

It was shown that the PVA consumption could be reduced to 1 lb/t on lab scale.

Testing of the reactive flotation process using a simple sluice was conducted on pilot

scale. Starting from the point that the formation of the bubbles on the dolomite surface

creates a density difference between dolomite and phosphate particles. Therefore, the

gravity separators are the promising techniques to do this separation.

In that regard, two tests were run using the sluice under two different coating

conditions. The first was spraying the particles with 3 % PVA solution before adding the

particles to the sluice and the second was conditioning the particles in 1 % PVA solution

and screening the particles to remove the excess PVA solution to reuse it (the PVA

consumption is estimated to be 0.8 lb/t), then adding the particles to the sluice. The

results of these two tests are given in Table 4-4. From these results, it can be seen that by

applying the optimum conditions, the reactive flotation process can reduce the MgO % to

less than 1 % with high recovery. In the rest of this work, the fundamental interpretations

of what are observed experimentally were carried out.

Table 4-4. Comparison of two different coating methods and their effects on MgO
removal
Sample Coating Conditioning
Wt% MgO% P205% CaO% I.R% Wt% MgO% P205% CaO% I.R%
Float 20.74 12.3 2.9 32.82 9.8 20 12.41 2.85 33.55 10.01
Sink 79.26 0.65 22.3 38.33 11.22 80 0.68 21.90 37.93 11.14
Calc. Feed 100 3.06 18.27 37.19 10.97 100 3.03 18.09 37.05 10.93
Feed 100 3.04 18.13 37.45 11.05 100 3.04 18.13 37.45 11.05














CHAPTER 5
FUNDAMENTAL STUDIES

Polyvinyl alcohol-Particle Interaction
Introduction

Generally, adsorption of a polymer is utilized in many applications, such as:

dispersion of particles, flotation, flocculation processes, treatment of surfaces, etc. If a

solvent is a poor solvent (i.e., the interaction energy between the polymer segment and

the solvent molecules is unfavorable when compared to polymer-polymer or solvent -

solvent molecular interaction energy), then the effective polymer -surface interaction can

be strongly attractive and the polymer will seek any opportunity to minimize the contact

points with the solvent. Hence, in cases where a poor solvent is used, adsorption will

increase on almost any surface, even the liquid-air interface. Adsorption is, therefore,

always accentuated before precipitation will occur. The surfaces will act as a nucleation

sites for polymer precipitation. This means, the poorer the solvent, the higher the

adsorption and vice versa. In addition to the solvent quality, there are other factors that

can affect the polymer adsorption and change its conformation, including: polymer

molecular weight, polymer concentration, pH, and ionic strength.

Previous studies of polymer adsorption suggest a number of qualitative trends that

have been noticed in most polymer adsorption systems. The most important of them are

as follows: many polymers adsorb on a variety of surfaces, Reach a plateau at few

mg/m2, a sharp isotherm sometimes is obtained, and molecular weight is a main factor,

especially in a poor solvent.









In this work, the polymer (PVA) is used as a membrane-forming agent to capture

produced CO2 gas on dolomite particles and makes them lighter than other particles

leading to their flotation and separation from non-carbonate (apatite) particle.

To understand this process and to elucidate the interaction mechanism between

polyvinyl alcohol (PVA) and dolomite and apatite surfaces in the reactive flotation

process, different techniques were used, such as: estimation of work of adhesion using

surface tension and contact angle measurements, adsorption/desorption isotherms, Zeta

potential, and surfaces characterization using Fourier Transform InfraRed (FTIR), etc.;

the details of each one of these techniques are discussed in this chapter.

The strength of adhesion to a solid surface can be estimated from the value of the

thermodynamic 'work of adhesion' or Wa, a concept first introduced by [Harkins, 1928].

In a simple system where a liquid L adheres to a solid S, Figure 5-1, the work of adhesion

is defined as:

Wa = Yi + -Y 7sl ............................ (5.1)

where Ys y and Ysl are the interfacial tensions of the solid/air, liquid/air and solid/liquid

interfaces respectively.

The problem with using Equation 5.1 is that, of the three interfacial tensions, only

y1 can be measured with fluid phases, in this case the liquid and air. Those tensions

involving the solid cannot be measured independently. Another approach, then, is to

combine Equation 1 with the Young-Dupre equation (Equation 5.2), to provide a more

useful expression for the work of adhesion [Adamson and Gast, 1997]:

Ys 7sl = yl cos ........... .............. (5.2)









where 0 is the contact angle that the liquid makes with the solid surface. Provided

that y1 and 0 can be measured experimentally, it is then possible to use Equation 5.3 to

calculate the work of adhesion.

W a = y i(1 + cos0) ............... .......... (5.3)

Therefore, the measurements of surface tension and contact angle are essential

towards the calculation of the work of adhesion of the polymer (PVA) with solid

surfaces, which will be discussed in the following sections.


Y1 Gas






Ys g Liquid Ysi
^ ------- -v ----- [ --------
Solid


Figure 5-1. Contact angle and interfacial surface tension at solid/liquid/gas interface

Surface Tension

The equilibrium surface tension values of fully hydrolyzed PVA solutions (average

Mw =150000) as a function of the initial bulk concentration at room temperature (23 OC)

are shown in Figure 5-3. The surface tension of PVA decreases with increasing

concentration of PVA until it reaches a region where the surface tension (59 60

dyne/cm) no longer decreases with increasing the polymer concentration. The critical

concentration at which the surface tension starts to be constant is 1 % PVA in aqueous

solution. These results coincide with the literature concerning the surface tension of fully

hydrolyzed polyvinyl alcohol (PVA). The fully hydrolyzed polymer has less effect on









surface tension than partly hydrolyzed PVA [Fbiehn and Erusberger, 1951; Kim and

Luckham, 1991]. The chemical structure of both is shown in Figure 5-2.

A B


OHi




Figure 5-2. Structural formula for PVA: A) partially hydrolyzed; B) fully hydrolyzed.

It is reported that the surface tension reaches a constant level at 1-3 % PVA

depending on the PVA molecular weight and degree of hydrolysis [Finch 1973; 1992].

These results are similar to several findings reported in the literature regarding polymer

systems; the stabilization of the surface tension of high-Mw PEO (> 100000) solutions

was associated with the saturation of the air/water interface by the polymer chains [Zeno

et al., 2004].


75

S70

S65

S60

55

50
0 1 2 3 4 5
PVA Concentration, %

Figure 5-3. Equilibrium Surface tension for aqueous PVA solutions at 23 C










An explanation of this phenomenon is that the surface activity of a polymer mainly

relies on its conformation in the aqueous solution, whereas the conformation of

macromolecule depends on its chemical structure and composition, etc. At low

concentrations, the chains of macromolecule are stretched in the water due to the

formation of hydrogen bonding with water molecules. These long chains lying on the

liquid/air interface can dramatically decrease the surface tension of water, even though

the adsorbed amount on the liquid/air interface is very small. With the increase of

concentration, the polymer's molecules that adsorb on the surface increase and a tight

macromolecular film is formed, which makes the surface tension decrease. When the

polymers occupy all the surface of solution, the adsorption reaches a level of saturation

corresponding to the lowest value of surface tension. As this concentration further

increases, the polymers in the solution begin to aggregate and form micelle-like clusters;

at this point, the surface tension shows no more changes. In the case of PVA, it may also

be related to degree of crystallinity due to formation of hydrogen bonding as indicated in

Figure 5-4 [Finch 1973].




OH CH
CH,

CH,
CH > OH ... ...... O
CH ? <. .............
OH
OH CH
..' CH,
CH OH
OH
CH, ....
OH





Figure 5-4. PVA crystal structure; the dotted lines indicate hydrogen bonds.









It is expected that the surface tension will have higher values in the presence of

the acidic media since the S04-2 ions increases the surface tension, affects the polymer

solubility, and enhances the formation of polymer aggregates at even a slightly high acid

concentration [Sun, 1994].

Contact Angle

The phenomenon of wetting or non-wetting of a solid by a liquid is better

understood by studying contact angle, which is the most universally applied method of

quantifying wettability. Contact angle methods have been developed extensively over the

past four decades. The contact angles of dolomite and apatite surfaces with PVA

aqueous solutions at different concentrations are shown in Figure 5-5. From the figure, it

can be seen that the contact angle increases with the increase of PVA concentration for

both minerals' surfaces. This phenomenon can be explained by the structure of PVA in

the solution shown in Figure 5-4. When a droplet of PVA placed on the surface of

dolomite or apatite, the PVA adsorbs to the surface by hydrogen bond. As the PVA

concentration increases, more and more hydrogen bonds form; as a result of hydrogen

bonds among its molecules, the PVA begins to form clusters. These clusters result in a

local viscosity increase, which controls the droplet shape as well as its tendency to

spread. This, in turn, increases the contact angle accordingly.

The dynamic behavior of the molecules, their conformation at solid-liquid

interface, and diffusion of macromolecules will affect the adsorption of more molecules,

with a subsequent increase in contact angle. The increase in contact angle is proposed to

result from polymer cluster formation and preferential coverage of the hydrophilic sites

by polymer molecules. This phenomenon is observed for PVA and also for some

modified PVA end groups [Finch 1992].











40



S30



S20
-- Dolomite
-*- Apatite
10
0 1 2 3 4 5

PVA concentration, %

Figure 5-5. Static contact angle variation with the PVA concentration

All measurements shown in Figure 5-5 were conducted immediately after

application of the drop. Evaporation of water caused the drop to contract and a

consequent change in the contact angle.

Work of Adhesion

Figure 5-6 shows the dependence of work of adhesion, W,, on the PVA

concentration. The work of adhesion decreases with increasing PVA concentration

(increase in AG, where W, = AG [Lloyd, 1994]). The increase in AG reflects the

formation of polymer clusters and increase of its crystallinity. This is due to the

formation of OH-group bonds between PVA molecules causing them to favor adhesion to

a solid surface. Additionally, the polymer's diffusivity decreases with higher

concentrations.

With increasing PVA concentration, the PVA molecules not only adsorb to the

surface but also form hydrogen bonds among themselves. This behavior affects the









conformation of the molecules at the solid-liquid interface till they reach the saturation

stage, when the work of adhesion becomes constant. It appears that this saturation stage

is the same region of PVA concentration, 1-3 %, at which constant surface tension and

contact angle are achieved.




E 160
S-4- Dolomite
140 --- Apatite


1 120


too
S 100


80 i ,
0 1 2 3 4 5
PVA concentration, %

Figure 5-6. Work of adhesion as a function of PVA concentration on dolomite and
apatite substrates

Additional Studies

To substantiate the presence of hydrogen bonding hypothesis and to establish an

adsorption mechanism additional studies were conducted and their results are discussed

in the paragraphs that follow.

Adsorption study: Research grade samples were purchased from Wards Natural

Science and used to conduct the adsorption study. These samples were chemically

analyzed by the wet chemical method and the results are listed in Table 5-1.










Table 5-1. Chemical analysis of the samples used in adsorption tests
MgO% P205% CaO% A1203% Fe203% I.R.% L.O.I. %
Dolomite 20.39 0.58 31.6 0.97 0.10 2.52 42.6
Apatite 31.73 49.50 2.64 1.04 4.95 5.0

Specific surface area measurements (BET method): The specific surface area

of dolomite and apatite particles was determined by the BET in order to be used in

adsorption isotherm calculations (applied in the next section). Using nitrogen as the

adsorbate, the measured surface areas for dolomite and apatite were 0.9 and 1.48 m2/g

respectively.

Pore size distribution: The results of cumulative pore size distribution for apatite

and dolomite are shown in Figures 5-7 and 5-8. It is clear that the apatite has a higher

cumulative pore area, 9 m2/g, than the dolomite, 1.8 m2/g. Mean pore sizes for apatite and

0 o
dolomite are 28 A and 42.5 A respectively.



10













0
0 200 400 600 800 1000
Pore diameter, A


Figure 5-7. Cumulative pore size distribution for apatite sample











2


S1.6


1.2


0.8


3 0.4


0
0 200 400 600 800 1000
Pore diameter, A


Figure 5-8. Cumulative pore size distribution for dolomite sample

Zeta Potential

In order to obtain a more detailed description of the adsorption and electrical

properties of the solid-solution interface, measurements of the zeta potential were taken.

The tendency of zeta potential to vary with nonionic polymer adsorption may be caused

by one of two different factors: 1) the shift of the position of the shear plane, or 2) the

blocking of the active sites on the surface by adsorbing polymer chains. The participation

of these effects was estimated by the determining the difference in the values of the zeta

potential with no polymer and with polymer present. The use of a KNO3 solution (3X10-

3 M) acted as a control in these experiments.

The results of measuring the zeta potential of apatite and dolomite in 3X10-3 KNO3

solution as function of pH are presented in Figure 5-9. It can be seen that the iso-electric

points (IEP) of apatite and dolomite are about 6.8 and 9, respectively. This is in

agreement with the results reported in the literature [Amankonah and Somasundaran,

1985; Chander and Furestenau, 1982; Pugh and Stenius, 1985].








68




50
40 3X10 3M KNO3
30
20

0

1 -10 2 4 6 8 10 12
S20
-30
-40 DDolomite
-50 Apatite
-60
pH




Figure 5-9. Zeta potential of dolomite and apatite samples


Zeta potential in the presence of PVA was determined as well. Figures 5-10 and 5-


11 show the results of measuring the zeta potential in the presence of a PVA solution. It


is evident that the presence of PVA does not change the IEP of the apatite or dolomite. It


does, however, cause compression in the electrical double layer.



60

50 3X10 3M
KNO,
40




a 10
0
2 4 6 8 1
-10
-20
Dolomite
-30 4Dolomite + PVA
-40


Figure 5-10. Zeta potential of dolomite in absence and presence of polymer











40
30 3X103M KNO,
20
10
0
-10 2 4 6 8 0 12 1
-20

30 Apatite
Apatite + PVA
-40
-50
pH

Figure 5-11. Zeta potential of dolomite in absence and presence of polymer

The results indicate that the surface sites remain accessible to potential determining

ions (H+ and OH-) and the IEP remains unchanged during PVA adsorption, thus implying

that the polymer does not alter the surface potential. It can be considered, as other

investigators asserted [Ottewill, 1967; M'pandou and Siffert, 1984; 1987; Luckham et al.,

1983] that the decrease in zeta potential relating to adsorption of PVA is not due to a

decrease in charge and surface potential, but rather to a shift of the shear plane (Figure 5-

12).


Ster plane Ster plane
Surface Potential A
i Shear plane Shear plane B



ZeaZP l -- eta potential before adsorption
Zeta Potential -_-- oO lS --
S- Zeta potential after adsorption
*S* e

Distance from surface Distance from surface



0 Ions counter ions e\ Polymer chain

Figure 5-12. Effect of polymer on the shear plane position, A) without polymer, B) after
polymer adsorption










In short, the changes of the zeta potential produced by the adsorption of

substances with high molecular weight, result from blocking of the active sites on the

minerals' surface and as well as from the shift of the shear plane.

Zeta potential of minerals in supernatant solutions

In natural ores, the dolomite and apatite form a mixture. Their presence together

may affect the adsorption of the polymer on both of the minerals' surfaces. Therefore, the

adsorption on the dolomite in presence of apatite supernatant and apatite in presence of

dolomite supernatant were studied.

The effect of the supernatant of dolomite on the zeta potential of apatite is shown in

Figure 5-13. The results show that the apatite surface becomes more positive over the

entire pH range and that the IEP has shifted from 6.8 to 8.6. Both effects are

hypothesized to be due to the presence of calcium and magnesium ions in the solution.


50
40 3X10-M KNO3
30 6
>20
10
0 .
-10 2 4 6 8 10 12
-10
-20

--30 -Apatite
-40
Apatite in Dolomite
-50
pH

Figure 5-13. Zeta potential of apatite and apatite in dolomite supernatant










Similarly, the zeta potential of dolomite in an apatite supernatant was measured as

a function of pH. The results, given in Figure 5-14, show the zeta potential of dolomite

to be reduced drastically in presence of apatite supernatant. The IEP shifts from 9 to 6.5.


50
40 3X10MM KNO3
30
20
-. 10


2 4 6 8 10 12
M-10
N-20

-30 -Dolomite
-40 -Dolomite in Apatite supernatant
-50
pH
Figure 5-14. Zeta potential of dolomite and dolomite in apatite supernatant

Zeta potential in the presence of PVA

Moreover, the zeta potential of dolomite in apatite supernatant in presence of PVA

was determined. The results in Figure 5-15 indicate that the PVA deals with surface of

dolomite, when suspended in an apatite supernatant, as an apatite surface. This is due to

the faster diffusion of small ions and molecules from the solution to the dolomite surface,

which converts it to surface similar to apatite. As can be expected, the movement and

diffusion of these ions is quite faster than that of polymer molecules. Consequently, The

polymer's role is applied after the surface changing and the adsorption of the polymer

appears as if it is on apatite surface.

The same argument mentioned in the previous paragraph can be applied in the case

of PVA present with apatite in a dolomite supernatant. The results of the zeta potential of

this system are shown in Figure 5-16.














40
3X10 M KNO,
30
20



S10 2 4 6 12




-40
N -30

-40 Dolomite in apatite supernatant + PVA
-50 Dolomite in Apatite supernatant
-60
pH

Figure 5-15. Zeta potential of dolomite in apatite supernatant before and after PVA
adsorption


40 3X10MM KNO3

30

> 20

10
0 T
S 2 4 6 8 11

-20
-30 "4'Apatite in Dolomite supernatant + PVA
Apatite in Dolomite supernatant
-40
pH

Figure 5-16. Zeta potential of apatite in dolomite supernatant before and after PVA
adsorption

Infrared (FTIR)

The FTIR spectra of the powders, both with and without polymer adsorbed to them,

were compared in order to obtain the mechanism of adsorption of PVA on dolomite and

apatite surfaces. This method was applied in previous studies [Kiselev and Rygin, 1972;










Paradip and Moudgil, 1991; Howard, and McConnel, 1967; Behl and Moudgil, 1993;

Bjelopavlic et al., 2000; Zaman et al., 2002; Mathur and Moudgil, 1997; Moudgil and

Prakash, 1998] to explain polymer-solid interactions. The major peaks for dolomite and

apatite are identified according to Ince et al. [1991] and Farmer [1974].

FTIR spectroscopic studies were carried out on the dolomite and apatite and

polymer samples both before and after adsorption. The assignments of the various bands

and peaks made in this study are in reasonable agreement with those reported in the

literature for similar functional groups [Finch, 1973; Chanchani, 1986; Ince, 1987].

The FTIR spectrum of PVA is shown in Figure 5-17. A broad-band, is displayed at

3450 cm-1, which may be attributed to hydrogen-bonded surface hydroxyl groups. The

sharp band at 2930 cm-1 is attributed to strong C-H stretching. The band at 2860 cm-1 is

attributed to shoulder C-H stretching. The transmission band at 1650 cm-1 is due to the

presence of moisture in the sample. The band at 1460 cm-1 can be attributed to O-H and

C-H bending. These results are in good agreement with the spectra of PVA reported by

other workers [Finch, 1973; 1992].










'2930

81650
3450 1460 V862
594
1110

4000 3600 3200 2800 2400 2000 1600 1200 800 400
Wave number, cm-1

Figure 5-17. Infrared transmittance spectra (FTIR) of poly vinyl alcohol (PVA)











The FTIR spectrum of the bare-dolomite sample as well as those that had

previously interacted with PVA is shown in Figure 5-18. The isolated hydroxyl group

peak is present in dolomite powder without polymer, but the spectra with polymer shows

the disappearance of this peak. Moreover, the peak intensity of the hydrogen-bonded

hydroxyl groups is smaller in case of the powder with the polymer than without. These

observations indicate that the adsorption of PVA on dolomite occurs by hydrogen

bonding involving -OH groups of the polymer. This finding is in concurrence with

earlier studies on silica-PEO [Rubio and Kitchener, 1976; Cheng, 1985] and silica-

Polyacrylic acid PAA [Tadros, 1978], which showed that the presence of isolated OH-

groups on the surface is responsible for the adsorption of polymer molecules by hydrogen

bonding.



Dolomite + PVA 1460
Dolomite 883

728
1820

3450 1460
3640 3030 2910 2550
A 2640 883
728
1820

2550
3450 2910 26402550
3030

4000 3600 3200 2800 2400 2000 1600 1200 800 400
Wave number, cm-1

Figure 5-18. Infrared absorbance spectra (FTIR) of A) dolomite alone, and B)
dolomite/PVA system.









The FTIR spectrum of the apatite sample after having interacted with PVA is

shown in Figure 5-19. However, unlike the case of dolomite, this figure indicates that the

adsorption mechanism of the polymer on apatite is not clarified by using FTIR-no

change is shown in the bands' intensities or positions, either for bare apatite or apatite

with polymer adsorbed on it. This finding is in agreement with the current literature

[Chanchani, 1986; Ince, 1987]. It is pertinent to mention that FTIR spectroscopic studies

on the dolomite-PVA and apatite-PVA systems revealed the presence of hydrogen

bonding only.


1050


-Apatite 607
-Apatite + PVA 1460

866
3450 1650

A






4000 3600 3200 2800 2400 2000 1600 1200 800 400
Wave number, cm1

Figure 5-19. Infrared absorbance spectra of A) apatite alone, and B) apatite/PVA system.

Adsorption Study

An adsorption study was used for the purpose of determining PVA adsorption on

both dolomite and apatite. The calibration curve for PVA concentration was determined

colometrically. Figure 5-20 shows the calibration curve and its equation, which was used

in this study to calculate the residual concentration of PVA in adsorption experiments.









The limitation of the PVA concentration to create this curve is 40 ppm [Finch, 1973;

1992].


0.16
0.14

S0.1
0.08 -
I 0.06
0.04 -
0.02
0
0 10 20 30 40 50

PVA Concentration, ppm

Figure 5-20. Calibration curve for PVA concentration measurements

Kinetics of adsorption

A study of the kinetics of adsorption is mainly to determine the equilibrium time of

adsorption. The rate by which equilibrium is established during adsorption depends on

the chemical nature of the polymer and its molecular weight, the solvent, and the type of

adsorbent. In most cases, the kinetic curves indicate an increase in the amount of

adsorbed polymer over time, with an asymptotic approximation of the equilibrium value

[Lipatov and Sergeeva, 1974]

The adsorption of a polymer on solid surfaces occurs by a three-step mechanism

[Dijit et al., 1990; Somasundaran and Ramachandran, 1988]. First, the polymer is

diffused from the bulk to the interface. Second, adsorption of the polymer molecules

occurs on the initially bare solid surface. Finally, polymer conformation and orientation

changes in the surface layer to accommodate the adsorption of more polymer molecules.









To ascertain the time required for the adsorption equilibrium to be attained, kinetic

tests were carried out at a natural pH of 7 for a period of 24 hours; PVA concentration

was 100 ppm (6.7X10-7 M). Figure 5-21 shows results on the adsorption of PVA onto

dolomite and apatite as a function of time. It is evident that the equilibrium is attained at

about one hour. The equilibrium values are 0.04X10-6 and 0.011X10-6 mole/m2 for

dolomite and apatite respectively. In consideration of these findings, a 2-hour

conditioning time was selected for the adsorption studies.

It was observed that the adsorption followed a typical second-order adsorption

process. The second-order model predicts the behavior over the whole range of

adsorption and is in agreement with an adsorption mechanism being the rate-controlling

step. The second-order rate expression [Ozacar, 2003] based on solid capacity is

generally expressed as follows:

= k(Feq F)2 ....... .............. (5.4).
dt
Or, by integration

F t ................. (5.5)
1 t
+
kF2 r
keq Feq

Where F is adsorption density (mole/m2) and Feq is equilibrium adsorption density

(mole/m2), K is second-order adsorption rate constant (hr-1), and t is time (hr). By fitting

the experimental data to Equation 5.5, the parameters Feq and K were determined. These

are listed in Table 5-2.

Table 5-2. Fitting parameters of second-order kinetic model
Feq X 10-6 mole/m2 K, hr-1
Dolomite 0.04 361.6
Apatite 0.011 200










It can be seen that the Feq values for dolomite and apatite match the experimental

values. The higher Feq value of dolomite indicates the presence of more sites available for

PVA adsorption than on apatite. Moreover, the Kad for dolomite is higher than the Kad

for apatite, which indicates the higher adsorption rate on dolomite. However, the plateau

was reached almost at the same time for both minerals.




5.E-02


4.E-02
2

h 3.E-02


~ 2.E-02


1.E-02


O.E+00


0 5 10 15 20 25
Time, hr


Figure 5-21. Kinetics of PVA adsorption on dolomite and Apatite
(Initial PVA concentration 6.7X107 M, pH 7, 2X10 -3 M KNO3 and 230C).

Explanation of the higher adsorption rate on dolomite: The higher adsorption

rate on dolomite may be explained by: (1) The higher solubility of dolomite and

production of more ions in the solution, which affects the solution's property as a solvent

(effectively converting it to poorer solvent). This property also affects the polymer's

conformation, which will either be flat on the solid surface-greater tendency for

molecules of polymer to be adsorbed on the solid surface or attach to each other, (2) The

neutrality of apatite (pH 7) while having an IEP of 6.8, which means less ions in the

solution are available to act as additional driving force for PVA to adsorb on the apatite


Dolomite
A Apatite
Dolomite-2nd order model
-Apatite- 2nd order model

-A A AA


f









surface. This is especially significant as there is high competition between the interaction

of PVA with water molecules and interaction of PVA with the apatite surface, and (3)

OH-groups on dolomite surface (isolated and hydrogen-bonded hydroxyls) are greater

than those on apatite surface (hydrogen-bonded hydroxyls). In other words, the isolated

OH is exclusive to the dolomite surface, which is confirmed with FTIR spectra

measurement.

Adsorption isotherm

Most isotherms of the adsorption of polymers from dilute solutions can be visually

represented as curves that reach saturation at specific concentrations [Lipatov and

Sergeeva, 1974]. It is important to note that polymers may adsorb on surfaces in various

conformations depending on bulk (solvent) and surface chemical properties of the

substrate, as well as other physical conditions of the system [Hong et al., 2001].

At low concentrations, the polymer chain behaves like isolated coil. If the

concentration of the polymer in the solution is raised, the chains become close to each

other, which allows polymer-polymer intermolecular interactions to influence the motion

of the polymer chains. The effects may be expected to be cumulative until the point of

chain-overlapping concentration, which is the close packing of the polymer coils in

solution. Once the overlapping concentration has been reached, the polymer motion will

be dominated by the presence of direct polymer-polymer interaction. As polymer

concentration is increased, the polymer diffusivity decreases. If the concentration

increases even further, a pseudo-matrix-gel will be formed. The resulting viscosity is

governed mainly by intermolecular interaction, which is related to polymer chains

overlap [Izmailova et al., 1975; Gotze and Sonntag, 1987; Andreyeva et al, 1973;

Babayevskii et al., 1986; Koopal et al., 1988].









For PVA, -OH is the only functional group [Koopal and Lyklema, 1979;

Chibowski and Paszkiewicz, 1995; Chibowski et al., 2000]. Increasing the degree of

hydrolysis reduces acetate groups, which usually show preferential adsorption. Thus, the

conformation of the polymer chain at the solid-polymer solution interface will depend on

the number of acetate groups in a PVA macromolecule. The lower the degree of

hydrolysis, the flatter the polymer chains; conversely, at high degree of hydrolysis, the

polymer chains should be oriented perpendicularly to the surface [Santhiya et al., 1999;

Sjoberg et al., 1999; Bajpai and Vishwakarma, 2003; Koopal and Lyklema, 1979]. This

conformation of the PVA macromolecule will favor the adsorption of the polymer on the

surfaces of dolomite and apatite, which is shown in Figures 5-22 and 5-23.

Chibowski [2000] reported that the adsorption of PVA on alumina increases with

an increase in the degree of hydrolysis. This is also confirmed by previous experimental

results and polymer screening experiments. In this work, it was found that the fully

hydrolysed PVA was the best among different degrees of hydrolysis PVAs' (Chapter 3 in

this thesis).

The adsorption density (mol/m2) of fully hydrolyzed PVA (acetate groups < 1 %)

on the minerals' surface as a function of the initial polymer concentration (0 to 4X10-6

mole) was determined at 230 Celsius and a pH 7 for dolomite and apatite. The results

obtained are presented in an adsorption isotherm plot (Figures 5-22 and 5-23 for dolomite

and apatite, respectively).

The analysis of these adsorption isotherms shows formation of a plateau for both

apatite and dolomite. Such behavior of the macromolecules comes from a different

adsorption affinity towards different surfaces. This result suggests that the observed







81


increase in PVA adsorption is mainly caused by the change in conformation of the

polymer chain at the minerals' surface. Following this change, a number of active sites

on the surface become available for further adsorption of polymer molecules. As

mentioned previously, the greater porosity of apatite leads to high number of adsorption

sites available and the horizontal stretching of the polymer to cover these sites. This, in

turn, explains the lower adsorption layer thickness and higher parking area of apatite.

The shape of the adsorption isotherms shown in Figures 5-22 and 5-23 is typical for

physical adsorption and is an acceptable shape for that range of polymer molecular

weight. [Adamson and Gast, 1997]. The measurements were repeated three times and

error bars were plotted on each graph. From the figures we can see that the adsorption

isotherm is S-shaped, which suggests a physical adsorption of PVA onto the dolomite and

apatite surfaces.




@ 2.5
S Dolomite
2.0

^1.5

5 1.0

I 0.5

0.0
0.0 0.4 0.8 1.2 1.6 2.0
Equilibrium PVA cone., 107 mole

Figure 5-22. Adsorption isotherm of PVA on dolomite at 230C











2.0
~ Apatite
1.5


S1.0


0.5

0.0
0.0 0.4 0.8 1.2 1.6 2.0
Equilibrium PVA Conc., 10 mole
Figure 5-23. Adsorption isotherm of PVA on apatite at 230C

Calculation of PVA adsorption and parking area

The amount of PVA adsorption was calculated using the following formula:

(C -C )* V
S= (C -C)* (5.6)
m*SA

Where, F is the amount of PVA adsorption (mole/m2), (Ci-Cr) is PVA concentration on

the particle (mole/ml), Ci is initial PVA concentration, Cr is residual PVA concentration,

V is the volume of solution (ml), m is the mass of dolomite or apatite particles (g), and

SA is the specific surface area of particles (dolomite 0.9 and apatite 1.48 m2/g).

The parking area of PVA molecules was calculated using the following formula:

ix 10O xxMw}

Parking area = (5.7)
Av

Where MW = 150,000 g/mole, Av is Avogadro's number (6.023 x 1023 #/mol) and

parking area is nm2/#. The calculated parking areas for dolomite and apatite at the first

plateau are (23.72 nm2) and (75.47 nm2) respectively. Taking into account that the









parking area per stretched molecule is 0.2 nm2 [Koopal and Lyklema, 1979], it was

observed that PVA-molecule forms a wavy or zigzag shape on the solid particles with the

higher thickness on the dolomite particles. Moreover, this conformation on dolomite

appears at lower relative concentration range. It is worth noting that in the case of

dolomite the adsorption isotherm is both steeper and reaches a plateau at lower

concentrations than in case of apatite.

The observed results may be explained based on the following hypothesis, which is

Schematically illustrated in Figure 5-24: macromolecules are generally more tightly

bound to surfaces due to the multiple points of attachment. The figure shows the

conformation of single polymer chain (5-24A) and/ or several chains (5-24B). It may be

concluded that without intermolecular H-bonds, spiral conformations of PVA are

favorable and with intermolecular H-bonds, zigzag conformations is expected.








Dolomite/ Apatite Dolomite / Apatite Dolomite/ Apatiti





DolomiteDolomitApDolomiteite ite i Dolomite/ Apatit(


Figure 5-24. Polymer-conformation changes with increase the concentration: A)
conformation of a single molecule, B) conformation of more than one
molecule.









Adsorbed layer thickness

The thickness of PVA layer adsorbed on dolomite and/or apatite can be calculated

from the adsorption isotherm by using the following relationship:


h = -(5.8)

Where, h is the adsorbed layer thickness, m; F is adsorption density, g/m2, and p is

PVA density, g/m3.

Using this relationship, the thickness of the adsorbed layer was found to be 27 nm

on dolomite and 9 nm on apatite, which indicates that the vertical polymer chains are

stretched three times longer in the case of the dolomite than in the case of the apatite.

This explains the greater adsorption on dolomite; since, according to their conformation,

the polymer chains occupy smaller number of sites. In addition, more sites are available

on dolomite than on apatite.

Note: The length of the PVA molecule of this molecular weight is about 600 nm,

which indicates that the polymer conformation would be like Figure 24B.


Effects of pH

Ionic sites at the surface generally control the surface charges, on salt-type minerals

such as apatite and dolomite. Specifically, for dolomite are: Mg+, Ca+, CO3--, HC03-,

OH-, MgHCO3+, MgOH+, Mg(OH)2, CaHCO3+, CaOH+, Ca(OH)2 and for apatite are:

Ca+, HP04--, CaOH Ca(OH)2, H2PO4-, CaH2PO4 The nature of the mineral surface,

pH, the presence of solutes, and the functional group of the polymer all affect the

adsorption behavior. Previous studies on different minerals (i.e., alumina, silica, kaolin,

clays) showed that the OH group of PVA is mainly responsible for adsorption on the










surface of a mineral [Santhiya et al., 1999; Sjoberg et al., 1999; Bajpai and Vishwakarma,

2003]. The effect of pH on the adsorption of PVA onto dolomite and apatite is shown in

Figure 5-25. It can be seen that adsorption is pH-dependent in the studied range of 2 to

12.


6.0E-02

S5.E0-02

S4.0E-02

S3.0E02

5 2.0E02

1.0E02

0.0E+00
1 3 5 7 9 11 13
pH

Figure 5-25. Effect of pH on adsorption of PVA on apatite and dolomite

Studying the adsorption of PVA on both minerals gives evidence that, due to

fluctuations in pH, the adsorption is due to formation of hydrogen bonding between the

dolomite or apatite surface from one side and OH- polymer functional group from

another side.

Effects of pH on Apatite: It is evident from Figure 5-25 that the adsorption

density decreases with an increase of pH. The decrease in the adsorption density as a

function of pH may be explained by taking into consideration the surface charge of the

apatite particles as well as the surface species, both of which are dependent on pH. It is

interesting to note that the decrease of CaH2PO4 and H2PO4- species, according to the

apatite activity chart [Attia and Fuerstenau, 1989] in entire pH range, are responsible for




Full Text

PAGE 1

SEPARATING DOLOMITE FROM PHOSPHATE ROCK BY REACTIVE FLOTATION: FU NDAMENTALS AND APPLICATION By AYMAN A. EL-MIDANY A DISSERTATION PRESENTED TO THE GRADUATE SCHOOL OF THE UNIVERSITY OF FLOR IDA IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY UNIVERSITY OF FLORIDA 2004

PAGE 2

Copyright 2004 by Ayman A. El-Midany

PAGE 3

To all who made this work possible, and To all who had parts in shaping the person that I am today.

PAGE 4

ACKNOWLEDGMENTS In the Name of Allah, the Most Gracious, the Most Merciful. Oh Allah! Make useful for me what you have taught me, and teach me knowledge that will be useful to me. I entrust you with what I have read and studied. Oh Allah! Bring it back to me when I am in need of it. You are my protector, and the best of aid.. I thank Allah for blessing me with all of the good that I have, and I ask that I will be able to use such gifts to help those in need. Amen. I have fortunate to be able to study in an excellent institution surrounded by a group of extremely intelligent people. I would like to recognize the amazing staff in Department of Materials Science and Engineering at University of Florida. I would also like to thank everyone who helped me arrive at this point. Special thanks and recognition go to my advisor, Dr. Hassan El-Shall. He gave me the opportunity to do research in his group. His drive and commitment to research have inspired and motivated me through this work. He has been a constant source of ideas and encouragement over the years. Many thanks go to my committee members; especially Dr. Spyros A. Svoronos, who helped me greatly and bore with me in the modeling part of my study. I would also like to thank the other members of my committee (Drs. John J. Mecholsky, Wolfgang Sigmund, and Susan Sinnott from the Department of Materials Science and Engineering, and my external committee member, Dr. Ben Koopman, Department of Environmental Engineering). I would also like to recognize the remarkable past and present members of Dr. El-Shalls research group for their assistance, advice, and support. Finally, I cannot thank my family enough for all of their love, encouragement, and counsel. To my parents, I owe everything. They have taught me many things. Above all iv

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they taught me that patience, determination, persistence, and faith are the keys to success. I thank my wife for her help and patience over the years. I thank the Particle Engineering Research Center (PERC) staff for helping me to get started and for providing support and guidance along the way. Much of the experimental work in my study could not have been accomplished without their help, and for that I am extremely grateful. This work was supported by the Florida Institute of Phosphate Research (FIPR), and the National Science Foundation / Particle Engineering Research Center (NSF/PERC). v

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TABLE OF CONTENTS page ACKNOWLEDGMENTS .................................................................................................iv LIST OF TABLES .............................................................................................................ix LIST OF FIGURES ...........................................................................................................xi ABSTRACT .....................................................................................................................xiv CHAPTERS 1 LITERATURE REVIEW.............................................................................................1 Introduction...................................................................................................................1 Previous Efforts to Separate Dolomite from Phosphate Rock......................................2 Anionic Flotation...................................................................................................4 Direct flotation...............................................................................................4 Reverse flotation............................................................................................5 Cationic Flotation..................................................................................................8 Nonconditioning Flotation.....................................................................................9 Two-Stage Conditioning Process........................................................................11 The CLDRI Process.............................................................................................12 Acid Leaching.....................................................................................................14 Physical Separation Methods......................................................................................14 Heavy Media Separation.....................................................................................14 Sizing, Attrition Scrubbing, and Desliming........................................................15 Problem Statement......................................................................................................15 Novelty and Scope of Study.......................................................................................15 Goal of Study..............................................................................................................16 2 MATERIALS AND METHODS...............................................................................17 Flotation Study............................................................................................................18 Screening Design (Plackett-Burman Design)......................................................18 Central Composite Design...................................................................................18 Flotation Procedures for Screening and CCD Designs.......................................21 Factorial Design for Conditioning with PVA before Flotation...........................21 Flotation Procedure for Conditioning Statistical Designs...................................21 Density and Surface Area Determination............................................................22 vi

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PVA Preparation..................................................................................................23 Spectrophotometric Determination of PVA........................................................23 Static (Equilibrium surface tension)....................................................................24 Dynamic Surface Tension (DST)........................................................................24 Maximum bubble pressure method..............................................................24 Dynamic surface tension setup.....................................................................26 Contact Angle......................................................................................................26 Measurement of Contact Angle...........................................................................27 Surface Characterization by FTIR.......................................................................28 Zeta Potential Measurements..............................................................................28 Adsorption...........................................................................................................28 Dissolution Kinetic Experiments.........................................................................29 Pilot Scale Experiments..............................................................................................30 The Sluice............................................................................................................30 Sluice Experiments..............................................................................................30 3 TECHNICAL ASPECTS OF REACTIVE FLOTATION: PRELIMINARY TESTS32 Introduction.................................................................................................................32 List of Potential Surfactants: Surfactants Screening..................................................33 Initial Screening Tests................................................................................................33 Specific Tests.......................................................................................................34 Acid type......................................................................................................34 Acid dosage..................................................................................................35 Surfactant type..............................................................................................36 Surfactant dosage.........................................................................................37 Particle size..................................................................................................38 Oil-Surfactant Experiments.................................................................................39 Poly-Vinyl-Alcohol (PVA) Testing....................................................................41 Effect of acid concentration.........................................................................41 Effect of particle size....................................................................................43 PVA with acid vs. PVA on the particle surface...........................................44 Preliminary Testing Using PVA Coated Particles......................................................45 Flotation of a Representative Sample..................................................................45 Fraction of Representative Sample (-4+1.19 mm)..............................................46 Effect of Time on Weight Percentage of Floated Particles.................................46 Effect of Size on the Flotation.............................................................................47 Summarizing Remarks................................................................................................48 4 OPTIMIZATION OF THE REACTIVE FLOTATION PROCESS AND PILOT SCALE TESTING................................................................................49 Introduction.................................................................................................................49 Optimization of the RF Process..................................................................................49 Screening Statistical Design................................................................................49 Central Composite Design...................................................................................52 vii

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Research to Reduce the PVA Consumption...............................................................52 Experimental Design of the PVA Conditioning Step..........................................56 Saturation Experiment.........................................................................................56 Pilot Scale Testing: Sluice Results.............................................................................57 5 FUNDAMENTAL STUDIES....................................................................................58 Polyvinyl alcohol-Particle Interaction........................................................................58 Introduction.........................................................................................................58 Surface Tension...................................................................................................60 Contact Angle......................................................................................................63 Work of Adhesion...............................................................................................64 Zeta Potential.......................................................................................................67 Zeta potential of minerals in supernatant solutions......................................70 Zeta potential in the presence of PVA.........................................................71 Infrared (FTIR)....................................................................................................72 Adsorption Study.................................................................................................75 Kinetics of adsorption..................................................................................76 Adsorption isotherm.....................................................................................79 Calculation of PVA adsorption and parking area.........................................82 Adsorbed layer thickness.............................................................................84 Effects of pH................................................................................................84 Adsorption in supernatants...........................................................................87 Desorption...........................................................................................................88 Desorption in Acidic Solution.............................................................................89 Bubble Formation and Stability..................................................................................90 Effect of Particle Size..........................................................................................91 Effect of PVA Coating........................................................................................94 Modeling of Bubble Formation and Dolomite-Particle Separation............................96 Blockage of the Acid Model................................................................................96 Disappearance of Active Sites Model.................................................................99 Empirical Models..............................................................................................101 First-order kinetic model............................................................................101 Acid concentration dependence model......................................................103 Estimation of CO 2 Required to Float the Dolomite Particle.............................106 Bubbles Stability...............................................................................................109 Validation of the Model Using a Different Carbonate Mineral........................112 Summarizing Remarks..............................................................................................114 6 CONCLUSIONS AND RECOMMENDATIONS FOR FUTURE WORK............116 Conclusions...............................................................................................................116 Recommendations for Future Work.........................................................................119 LIST OF REFERENCES.................................................................................................120 BIOGRAPHICAL SKETCH...........................................................................................129 viii

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LIST OF TABLES Table page 2-1. Experimental Plackett-Burman design for 11 variables...........................................19 2-2. Rotatable central composite design with 5 levels and 3 variables...........................20 2-3. Factorial design for conditioning with PVA.............................................................21 3-1. Surface-active agents used in RF tests.....................................................................33 3-2. Size analysis of the dolomitic phosphate sample.....................................................34 3-3. Chemical analyses of the dolomitic phosphate sample............................................34 3-4. Effect of sulfuric acid concentration........................................................................35 3-5. Effect of sulfuric acid concentration on the bubble formation.................................36 3-6. Preliminary tests of high dolomitic phosphate with different surfactants................37 3-7. Effect of surfactant concentration (SDSO 3 2 %).....................................................38 3-8. Effect of particle size on the dolomitic particle floatability.....................................39 3-9. Effect of presence of surfactant and oil layer on particle flotation..........................40 3-10.Effect of acid concentration......................................................................................42 3-11.Effect of acid concentration above 2 %....................................................................43 3-12.Comparison between coating the particle before adding it to acidic solution and adding the particle to acid+PVA solution without coating......................................45 3-13.Results of representative sample (4+1.19 mm particle size)..................................46 3-14.Effect of time on the flotation of 4+1.19 mm particle size....................................47 3-15.Effect of particle size on flotation............................................................................47 4-1. The MgO % removal in floated fraction for Plackett-Burman design.....................50 ix

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4-2. Plackett-Burman calculated t values for different variables.....................................51 4-3. Effect of saturated acid on the RF............................................................................57 4-4. Comparison of two different coating methods and their effects on MgO removal..57 5-1. Chemical analysis of the samples used in adsorption tests......................................66 5-2. Fitting parameters of second-order kinetic model....................................................77 5-3. Chemical analysis of the samples used in kinetic tests............................................91 5-4. Acid-blockage model parameters.............................................................................97 5-5. Active sites disappearance parameters...................................................................100 5-6. Reaction rate constants of first-order model...........................................................103 5-7. Acid concentration dependence parameters...........................................................105 5-8. Active sites disappearance parameters for dissolution of calcite...........................113 x

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LIST OF FIGURES Figure page 1-1. Simplified flowsheet for phosphoric acid production................................................3 1-2. Simplified flowsheet of USBM direct flotation.........................................................6 1-3. Flowsheet of TVAs diphosphonic depressant process..............................................8 1-4. Flowsheet for IMCF cationic flotation.......................................................................9 1-5. University of Alabama pebble processing, simplified flowsheet.............................10 1-6. Flowsheet for University of Florida two conditioning stages..................................11 1-7. Simplified flowsheet for CLDRI dolomite flotation................................................13 2-1. Strategic plan to achieve research goals...................................................................17 2-2. Five-level, rotatable central composite design.........................................................20 2-3. Characteristic bubble-pressure vs. time curve in MBP............................................25 2-4. Setup for the measurement of dynamic surface tension by MBP.............................26 2-5. Contact angle and its relation with surface tension..................................................27 2-6. Contact angle measuring apparatus..........................................................................28 2-7. Schematic diagram for separation of dolomite from phosphate in sluice................30 3-1. Effect of acid concentration on bubble formation and flotation time.......................36 3-2. Effect of the particle size on the time needed to float the particle...........................44 4-1. Effect of PVA dosage and acid conc. on MgO recovery % ....................................53 4-2. Effect of PVA dosage and acid concentration on MgO % ......................................54 4-3. Cube graph for MgO % and MgO recovery %.........................................................56 5-1. Contact angle and interfacial surface tension at solid/liquid/gas interface..............60 xi

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5-2. Structural formula for PVA......................................................................................61 5-3. Equilibrium Surface tension for aqueous PVA solutions at 23 C...........................61 5-4. PVA crystal structure; the dotted lines indicate hydrogen bonds.............................62 5-5. Static contact angle variation with the PVA concentration......................................64 5-6. Work of adhesion as a function of PVA concentration............................................65 5-7. Cumulative pore size distribution for apatite sample...............................................66 5-8. Cumulative pore size distribution for dolomite sample............................................67 5-9. Zeta potential of dolomite and apatite samples........................................................68 5-10. Zeta potential of dolomite in absence and presence of polymer............................68 5-11. Zeta potential of dolomite in absence and presence of polymer............................69 5-12. Effect of polymer on the shear plane position........................................................69 5-13. Zeta potential of apatite and apatite in dolomite supernatant.................................70 5-14. Zeta potential of dolomite and dolomite in apatite supernatant.............................71 5-15. Zeta potential of dolomite in apatite supernatant before/after PVA adsorption.....72 5-16. Zeta potential of apatite in dolomite supernatant before/after PVA adsorption.....72 5-17. Infrared transmittance spectra of poly vinyl alcohol (PVA)..................................73 5-18. Infrared absorbance spectra of dolomite and dolomite/PVA system.....................74 5-19. Infrared absorbance spectra of apatite and apatite/PVA system............................75 5-20. Calibration curve for PVA concentration measurements.......................................76 5-21. Kinetics of PVA adsorption on dolomite and Apatite............................................78 5-22. Adsorption isotherm of PVA on dolomite at 23C................................................81 5-23. Adsorption isotherm of PVA on apatite at 23C....................................................82 5-24. Polymer-conformation changes with increase the concentration...........................83 5-25. Effect of pH on adsorption of PVA on apatite and dolomite.................................85 5-26. Adsorption isotherm of apatite in dolomite supernatant solution, and dolomite in apatite supernatant solution......................................................................................87 xii

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5-27. Desorption of PVA from apatite surface................................................................88 5-28. Desorption of PVA from dolomite surface.............................................................89 5-29. The bubble formation mechanism..........................................................................90 5-30. Schematic diagram of reaction kinetics of the RF..................................................91 5-31. Dissolution kinetic of different particle sizes in terms of calcium ions ................92 5-32. Dissolution kinetic of different particle sizes in terms of magnesium ions............93 5-33. Dolomite particle (1-2 mm) before and after the reaction with 3 % H 2 SO 4 ...........93 5-34. Dissolution kinetics of coated and uncoated 0.2-0.3 mm dolomite particle ..........94 5-35. Growth of the bubbles with time on the dolomite particle surface, 50 X...............95 5-37. Acid blockage model fitting to 0.25-0.35 mm experimental data..........................98 5-38. Active sites disappearance model fitting to 1-2 mm data.....................................100 5-39. Active sites disappearance model fitting to 0.25-0.35 mm data...........................100 5-40. First-order model fitting for data of 0.25-0.35 mm particle size..........................102 5-41. First-order model fitting for data of 1-2 mm particle size....................................102 5-42. Model fitting for data of 0.25-0.35 mm particle size............................................104 5-43. Model fitting for data of 1-2 mm particle size......................................................105 5-44. Sequence of calculating the particle density and membrane elasticity................108 5-45. Density changes for different particle sizes..........................................................109 5-46. Dynamic surface tension of PVA concentration at different CO 2 flowrate.........111 5-47. Elasticity of PVA membrane vs. PVA concentration ..........................................112 5-48. Calcite dissolution: model vs. experimental data 0.25-0.35 mm particle size.....113 5-49. Calcite dissolution: model vs. experimental data for 1-2 mm particle size..........113 xiii

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Abstract of Dissertation Presented to the Graduate School of the University of Florida in Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy SEPARATING DOLOMITE FROM PHOSPHATE ROCK BY REACTIVE FLOTATION: FUNDAMENTALS AND APPLICATION By Ayman A. El-Midany December 2004 Chair: Hassan El-Shall Major Department: Materials Science and Engineering Florida is currently one of the largest phosphate producers in the world. Unfortunately, the phosphate industry in Florida is suffering from depletion of the phosphate-rich ore. Dolomite, however, is a major impurity in the ores. The presence of MgO, in dolomite, can cause several problems during production of phosphoric acid and final fertilizers. Efforts to solve the dolomite problem have been reported by several researchers throughout the world. Yet, only heavy media separation process has been applied commercially. However, the process was discontinued because of its low separation efficiency in terms of grade and recovery. In this study, we tested an innovative idea based on simple fact that dolomite, as a carbonate mineral, generates CO 2 when exposed to a slightly acidic solution, capturing CO 2 bubbles at dolomite particle surface can selectively float the dolomite and separate it from phosphate. Formation of such bubbles requires a surface-active agent(s) at xiv

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solution/dolomite interface. Preliminary tests indicated that polyvinyl alcohol (PVA) could serve this function. This process is called the Reactive Flotation, RF. To develop this process and to scale it up for industrial use, we conducted fundamental and applied research studies. Among these studies were optimizing of RF process by investigating the factors affecting the process (including bench and pilot scale tests) using statistical experimental designs. It was found that the acid concentration, PVA concentration, and particle size are the main factors. The optimum conditions were determined and applied to usage in a gravity separation device, (i.e., a sluice). Using such a device, a concentrate contains 0.65 % MgO with > 94 MgO % removal can be achieved. In addition, fundamental studies revealed that the hydrogen bonding is the adsorption mechanism confirmed by adsorption isotherm of PVA on dolomite and phosphate, adhesion of PVA to dolomite surface (using contact angle and surface tension), Fourier Transform InfraRed (FTIR), and Zeta potential. Moreover, PVA film thickness and polymer film elasticity (using dynamic surface tension) revealed that the optimum conditions could keep the PVA film at its highest elasticity. On the other hand, modeling was developed and used to predict CO 2 formation rate and subsequent particle density change. xv

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CHAPTER 1 LITERATURE REVIEW Introduction Traditionally, the Florida phosphate industry has effectively responded to the competitive pressures of the market place by implementing technological improvements to mining and beneficiation methods. With further expansion of fertilizer production capacity worldwide and depletion of Florida's high-grade deposits, competitive pressures are expected to continue. To remain the world leader, Florida must continue to seek environmentally sound technological improvements in all areas of phosphatic fertilizer production. Gu et al. [1999] estimated that the Bone Valley phosphate reserve in Central Florida (which can be cost effectively processed with available technology) may only last about 20 years at the current mining rate. In the near future, with the depletion of the low-dolomite, easy-to-process Bone Valley siliceous phosphate deposits, phosphate mining will move farther south and southeast. The phosphate matrix in the southern extension is leaner in grade and high in dolomite. Dolomite is the most troublesome, causing higher consumption of sulfuric acid, reducing filtration capacity, and lowering P 2 O 5 recovery in fertilizer manufacturing. Therefore, the MgO content of dolomite is an important index in evaluating the quality of phosphate concentrate. In Florida, the MgO content in final concentrate is usually required to be less than 1 %. Geological and mineralogical data show that about 50 % of the phosphate resource would be wasted if the high dolomitic zones were bypassed in mining, and about 13 % of 1

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2 the resource would be lost if the dolomite pebbles were discarded. Although heavy media separation (HMS) technology was tried commercially, to process a portion of dolomite pebbles in Florida, in most cases the high-dolomite phosphate has been bypassed during mining operations because no technology is available to process high-dolomite pebbles economically. Technically and economically feasible beneficiation technology for processing dolomite pebbles is needed to recover phosphate value, extend Florida phosphate reserves, and prolong the life of Florida phosphate industry [Geo et al., 2002]. Previous Efforts to Separate Dolomite from Phosphate Rock Phosphate rock is one of the basic materials for fertilizers. About 90 % of the phosphate rock output in the world is used for fertilizer production. The United States is one of the worlds largest producers of phosphate rock and fertilizer. Its phosphate production represents approximately one-third of the worlds total [Becker, 1989]. Phosphoric acid is an important intermediate product for production of fertilizers. Current phosphoric acid technology essentially comprises sulfuric acid attack, and separation of the phosphoric acid from the calcium sulfate crystals resulting from the reaction. Both the attack and separation, which are effected by filtration, are considerably influenced by the nature of the ore and its impurities [Becker, 1989]. Figure 1-1 shows the main processes in phosphoric acid production. As mentioned, the main impurity in Florida phosphate ore is dolomite. Dolomite, (Ca, Mg)CO 3, is the main source for calcium and magnesium. As impurities, CaO and MgO affect the phosphoric acid production by increasing sulfuric acid consumption, in addition to the MgO stays with the acid phase, and greatly increases viscosity.

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3 Ca 10 (PO 4 ) 6 F 2 + 10 H 2 SO 4 + 20 H 2 O 6 H 3 PO 4 + 10 CaSO 4 .2H 2 O + 2 HF Reaction Sulfuric acid Filtration Counter-Current Washing Phos p ho gyp sum Phosphoric acid Wash Water Phosphate Concentrate Figure 1-1. Simplified flowsheet for phosphoric acid production Therefore, because dolomite is the most common impurity, developing an efficient and economical method for separating dolomite from apatite is an effective way to extend phosphate mine life. Generally, acidulation of phosphate rock requires a feed of less than 0.8 % MgO, which has not been achieved at a commercial scale with ores high in MgO. Dolomite is also a worldwide problem. All of the major phosphate-producing countries have faced, or are going to face, the dolomite problem. Salt-type minerals (such as apatite, calcite, dolomite, barite, fluorite and scheelite) have been successfully separated from oxides and silicates by flotation methods. However, these minerals are often difficult to separate from each other because they contain similar alkaline earth cations that cause them to exhibit similar surface (electrical) behavior. All the zero points of charge (ZPC) of phosphates and carbonates are located in the acid pH range (i.e., 4-5.5) [Smani, 1973; Smani et al., 1975]. Systematic research in carbonate phosphate ore beneficiation started in the early 1950s [El-Shall et al., 2004]. Techniques used include the following: Direct flotation of phosphate, using sodium silicate to depress carbonate impurities.

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4 Reverse flotation of the carbonate impurities by depressing the phosphate using materials such as fluorides, fluosilicic acid, diphosphonic acid, phosphoric acid, aluminum sulfate-tartrate, and inorganic phosphate salts. Rapid change of conditioning parameters (such as the University of Florida two-stage conditioning process, Alabama non-conditioning process, the IMC-F process, and the low-pH conditioning process proposed by Minemet research). Physical methods: gravity concentration, sizing, desliming, heavy media separation. Calcination: although expensive because of its energy requirement, high-temperature destruction of the carbonate followed by leaching has been practiced in North Africa with low cost energy. Acid leaching: carbonates are easily dissolved by acid, and weak acids can be used to dissolve the carbonate, leaving the apatite. Anionic Flotation Direct flotation Sodium silicate is widely used as carbonate depressant [Fuerstenau, 1968; Ananthapadmanabhan and Somasundaran, 1985; Rao, 1988; Dho and Iwasaki, 1990]. Encouraging results were obtained in both batch and continuous pilot tests conducted by the United State Bureau of Mine, USBM, [Davis et al., 1984]. After 1 lb/t sodium silicate was added in each of three cleaning stages, a phosphate rougher was upgraded to about 30.7-31.3 % P 2 O 5 0.6-1.3 % MgO with a P 2 O 5 recovery from 55.1 to 89.7. The original matrix contained 5.47-10.2 % P 2 O 5 and 1.9-7.6 % MgO. Rao [1989] studied the effects of major flotation parameters on phosphate grade and recovery using sodium silicate as a calcite depressant. Maximum flotation of apatite occurred at pH 8, and phosphate recovery decreased with increasing pH. Sodium silicate at a concentration below 0.0013 M had no depressive effect on calcite. However, at pH values above 10, calcite depression was observed even in dilute silicate solution. A concentrate with 25.6 % P 2 O 5 at 80 % recovery was obtained.

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5 Efforts to concentrate high-dolomite Florida phosphate ores by flotation, using conventional fatty-acid/fuel-oil flotation [Liewellyn, 1982], showed that sodium silicate depression on dolomite was not enough to obtain a concentrate less than 1 % MgO. This may be due to the presence of silica in this ore in addition to dolomite. Reverse flotation Depression of phosphate: This method was used when the apatite was more abundant than calcite and dolomite (as in most phosphate ore). Among depressants used are as follow: Fluosilicic acid: USBM investigated the removal of carbonate from phosphate rock using fluosilicic acid as a depressing agent and tall oil-fatty acid as a collector for carbonate mineral flotation (Figure 1-2) [Rule, 1982;1985]. At collector dosage 0.7 kg/t, 0.45 kg/t depressant, a concentrate of 25.5 % P 2 O 5 and 0.84 % MgO with P 2 O 5 recovery 89.5 % was obtained from feed with 20.8 % P 2 O 5 and 1.1 MgO %. Abdel Khalek [2000] studied the phosphate depression using fluosilicic acid, but recovery using this process was less than 60 %. Ataly [1985] pointed out that for depressing Turkish ores fluosilicic acid was not efficient as other depressants because of the low recovery (57 %) obtained using fluosilicic acid. Acid depressants: Orthophosphoric acid was found to decrease adsorption of the fatty acid on apatite because of the increased surfacial solubility of apatite.

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6 Phosphoric acid also was used to depress apatite (by the USBM, in separating dolomite from a southern Florida ore) [Liewellyn, 1982]. The produced concentrates P 2 O 5 % did not exceed 28 %, and the MgO % was not less than 1.9 %. High MgO Pebble N aOH Concentrate Cleaning Phosphate Flotation Ro ugher Phosphate Flotation Conditioning Desliming 150 Mesh Scrub Desliming 150 Mesh Screening 28 Mesh Hammer Mill Sodium Silicate Fatty acid/Fuel Oil + 28 Mesh 150 Mesh Fines 150 Mesh Fines Dolomite Rough e r T ail Dolomite Cleaner T ail Figure 1-2. Simplified flowsheet of USBM direct flotation

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7 Lawendy [1993] found phosphoric acid to be the best among conventional depressants of phosphate. The concentrate was 32-36 % P 2 O 5 1 % MgO at 70-75 % overall P 2 O 5 recovery from feed 16-25 % P 2 O 5 and 4-11 % MgO. In other study [Hsieh and Lehr, 1985], diphosphonic acid was used to depress phosphate (TVA process), (Figure 1-3), with fatty acid collectors for beneficiating an ore containing 72 % SiO 2 1.05 % MgO and 6.3 % P 2 O 5 The resulted concentrate contained 73.3 % SiO 2 0.7 % MgO and 6.4 % P 2 O 5 Although sulfuric acid is a phosphate depressant, its ability to attack phosphate and its high need for pH control limits its usage [Elgilani and Abouzeid, 1993]. Jacob Engineering [Gruber et al., 1987] used sulfuric acid as a pH regulator to completely depress phosphate at pH 5.5. Phosphates: Rao [1979] found that the depressing action of dipotassium hydrogen phosphate is pH dependent. Phosphate can be depressed at pH 5-8, while carbonate can be depressed only at alkaline pH; which means that selective flotation can be obtained. However, the concentrate produced by this process contained no more than 24 % P 2 O 5 Sodium chloride: The effect of sodium chloride and other salt addition on dolomite and apatite flotation has been studied [Rao, 1985]. It was shown that sodium chloride acts as apatite depressant during flotation at acidic pH values with oleic acid, while dolomite flotation is not affected. It was, however, observed that dolomite particles larger than 48-mesh are difficult to float and they tend to remain in the sink fraction. Trends observed during Hallimond cell tests of single and mixed minerals were confirmed with mixtures of minerals and a natural ore at bench-scale level. Under more

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8 favorable conditions in the bench-scale tests, MgO content of the mineral mixtures was reduced from 5 % to 1 % or less, with at least 90 % recovery of P 2 O 5 in the sink fraction. 48+ 40 0 Mesh High MgO Pebble Diphosphonic acid/ Oleic Acid Phosphate Concentrate Silica Flotation Dolomite Flotation Scrubbing & Desli m ing Classification Ball Mill Grinding Dodecylamine Hydrochloride + 4 8 Mesh 40 0 Mesh Fines 400 Mesh Fines Float Dolomite T ail Float Silica T ail Figure 1-3. Flowsheet of TVAs diphosphonic depressant process Alizarin Red S (ARS): ARS is an organic depressant. It is used to depress either phosphate or carbonate, depending on pH. ARS can depress calcite impurities at a pH 8-10, while apatite can be depressed at a pH below 6 [Fu and Somasundaran, 1986; Xiao and Somasundaran, 1989]. Cationic Flotation The IMC-F process (Figure 1-4) is a cationic-flotation process for silica-free ores. The ore is reagentized with a cationic collector (amines or their salts) and the dolomite

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9 separated from phosphate at a rougher stage followed by one or two phosphate-cleaning steps [Snow, 1979; 1982; Lawver and Snow, 1980]. By using IMC-F process, a concentrate of 31 % P 2 O 5 0.86 % MgO from feed of 2 % MgO with 83 % P 2 O 5 recovery can be obtained. High MgO Pebble Amine Recleaning phosphate Flotation Cleaning Phosphate Flotation Ro ugher Phosphate Flotation Conditioning 20-30 sec Dewatering 65-70% Silica Flotation Desliming 150 Mesh Screening 24-35 Mesh Rod Milling Phosphate Conc. Acetic acid/Amine Oversize -150 Mesh Fines Dolomite Rough er Tail Dolomite Cleaner T ail Frother Dolomite Tailings Silica Tailings Figure 1-4. Flowsheet for IMCF cationic flotation Nonconditioning Flotation A research contract between FIPR and Mineral Resources Institute (MRI) at the University of Alabama aimed to develop a selective flotation process (Figure 1-5) to separate dolomitic limestone from Florida phosphate ore [Hanna and Anazia 1990]. This process depends on the difference in adsorption rate of fatty acids on both phosphate and

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10 carbonates. Fatty acids adsorb more rapidly on carbonate surfaces than on phosphate surfaces. At slightly acidic pH (5.5-6.0), carbonates floated immediately on addition of collector and frother. After carbonate froth collection, the pulp is conditioned briefly to float phosphate thereafter with no more addition of collector. High MgO Pebble Flotation p H 4-7 Conditioning Dolomite Flotation Conditioning Desliming 325 Mesh Scrubbing 35 % solids Desliming 150 Mesh Screening 35 Mesh Rod Milling Phosphate Conc. Fatty acid/Pine oil +35 Mesh -150 Mesh Fines Dolomite Tail Sodium silicate/Fatty acid Silica Tailings Silica Tailings -325 Mesh Figure 1-5. University of Alabama pebble processing, simplified flowsheet

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11 Two-Stage Conditioning Process This process was investigated through FIRP university of Florida project, in 1983 [Moudgil, 1988]. The process involves conditioning the feed at pH 10, followed by reconditioning at a lower pH before flotation, Figure 1-6. Selective flotation of dolomite from apatite was observed for both single and mixed minerals, by reconditioning at pH 4. Basic pH Modifier/Fatty acid High MgO Pebble 65x150 Mesh Feed Frother Dolomite Flotation p H 4-5 Reconditioning Flotation P H 9-10 Further processing to remove silica Conditioning pH=10 H 2 SO 4 Silica (Sink) Float Dolomite Sink (Apatite & Fine Quartz) Figure 1-6. Flowsheet for University of Florida two conditioning stages To understand the mechanisms of observed selective flotation, further studies were conducted involving electrokinetic behavior, oleate adsorption, infrared spectroscopy,

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12 and solubility of the minerals. Selective flotation of dolomite, by reconditioning at pH 4, is attributed to the combined effect of higher oleate adsorption on dolomite and hydrolysis of the adsorbed oleate molecules to oleic acid at lower pH values. The method has been tested in the laboratory with several dolomite-apatite mixtures and natural magnesium phosphate samples from the Florida phosphate field. Reductions of the MgO content of the samples from 1.8-4.0 % MgO to below 1 % MgO at recoveries of about 90 % P 2 O 5 in the sink fraction have been obtained in bench-scale flotation tests. Reconditioning pH was determined to be one of the most important parameters in this process. The CLDRI Process In China, over 90 % of the phosphate resources are dolomitic, with MgO content ranging from 2 % to over 10 %. For economical and rational use of domestic phosphate resources, China Lianyungang Design and Research Institute (CLDRI) has conducted studies for many years and developed some flotation technologies for removing MgO impurity from phosphate ore. These flotation technologies have successful industrial applications [El-Shall et al., 1996]. Since 1997, CLDRI has conducted extensive studies on Florida high dolomitic pebble with the objective of using CLDRIs fine particle flotation technology to recover phosphate (Figure 1-7). In 2000, pilot scale testing (400 lb/h) was carried out jointly by CLDRI, Jacobs engineering group, and IMC phosphates company at Jacobs pilot plant facility. Preliminary economic and technical analysis by Jacobs engineering (based on pilot plant test results) showed that CLDRIs fine-particle flotation technology could be used economically and technically for processing Floridas dolomitic phosphate pebbles [Geo et al., 2002].

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13 Figure 1-7. Simplified flowsheet for CLDRI dolomite flotation

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14 The CLDRIs fine-particle flotation technology (Figure 1-7) utilized for processing Florida high-dolomitic phosphate pebbles has two steps. The first step is grinding for liberation and second nondesliming after grinding, which improves flotation recovery and use of Florida resources, and lowers production cost. Acid Leaching Strong and weak acids were used in the acid leaching process. In strong-acid leaching processes, sulfuric acid was used to completely dissolve the dolomite from phosphate ore. In the early 1970s, the USBM investigated magnesium impurity removal from phosphate concentrates by acid leaching [Rule, 1970]. The MgO level was reduced to less than 0.1 % by using dilute sulfuric acid, but the phosphate loss was about 6 % P 2 O 5 Weak-acid leaching, using weak organic acids, was also studied. Pilot plant studies [Abu El-shah, 1991] using 6.7 % acetic acid solution could remove more than 80 % MgO. The advantage of using weak organic acids is that (unlike strong acids), they do not attack other minerals. The overall disadvantage is that acid leaching, in general, needs fine particle sizes produced by crushing and grinding which means more expenses. Physical Separation Methods Heavy Media Separation The only commercial process to separate dolomite from phosphate is heavy media separation [Wiegel and Hwang, 1984]. Heavy media cyclones are used in IMCF mines for processing the high-dolomite portion of the ore. The concentrate with 1.2 % MgO was obtained from feed that has 3 % MgO.

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15 Sizing, Attrition Scrubbing, and Desliming The dolomite is more friable than phosphate rock. Thus, dolomite can be separated from phosphate by discarding the fine fraction (mainly dolomite) by scrubbing or sizing [El-Shall and Bogan, 1990]. Problem Statement The various beneficiating techniques discussed have various limitations or disadvantages. In acid leaching, strong acids can attack phosphate as well as dolomite and can be associated with environmental problems associated with this process. In flotation processes for high dolomitic phosphate, because they could not reduce the MgO % below 1 % are not applied commercially. In CLDRI fine flotation process, by which the MgO % could be reduced to less than 1 %, concerns are as follows: handling of fine concentrate (dewatering and transport), capital cost (grinding and multiple process steps), and operating cost: increasing the MgO % in the phosphate rock increases reagent consumption, and requires grinding, thus increasing energy consumption and plant operating cost. The only process with commercial application was heavy media separation (HMS), which also suffers from high MgO % (more than 1 %) in the concentrate in addition to about 50 % phosphate loss. Novelty and Scope of Study We sought a process that separates dolomite from phosphate pebbles resulting in a phosphate concentrate with less than 1 % MgO. Since the dolomite is mostly in the pebble fraction and not attached to phosphate, the idea came from well-known reaction between carbonates and acid producing carbon dioxide gas. Dolomite, as a carbonate

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16 mineral, generates CO 2 when exposed to a slightly acidic solution, as shown in the following chemical reaction: Dolomite + Acid salt + CO 2 Capturing the generated CO 2 at the dolomite particle surface, into bubbles using coating agent (which is a kind of surfactant or polymer) can selectively float dolomite, and separate it from phosphate rock. Since this process depends on chemical reaction between dolomite and acidic medium to form a stable bubble at the particle surface and then to float it, this process is called the Reactive Flotation (RF) process. The RF has the following requirements (1) presence of acidic medium at low percentage, and (2) Presence of surfactant that: attaches to the dolomite, is permeable by acid, allows formation of stable bubbles at the particle surface, is impermeable to CO2 gas, and is stable enough to float the particle to the surface. Goal of Study The goal of this study is to develop and to optimize a novel and an effective process to separate the dolomite from phosphate rock. This process will not only reduce the MgO % to less than 1 % but also increase the efficiency of the subsequent processes in phosphoric acid production such as filtration and consequently reduce the phosphate losses. In addition to develop this novel process, a fundamental study needs to be done to elucidate Mechanism(s) involved in this novel process.

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CHAPTER 2 MATERIALS AND METHODS To achieve the goals of this research different measurements and techniques are needed to elucidate polyvinyl alcohol (PVA)/ particle interactions, and bubbles formation and stability as well as its modeling the following strategy will be followed, Figure 2-1. Film thickness Work of Adhesion Acid Diffusion CO2formation rate Bubble formation model Elasticity (Dynamic surface tension) Time required to start particle flotation Density balance Density change Adsorption Isotherm FTIR Surface Tension Contact Angle Zeta Potential 12 Film thickness Work of Adhesion Acid Diffusion CO2formation rate Bubble formation model Elasticity (Dynamic surface tension) Time required to start particle flotation Density balance Density change Adsorption Isotherm FTIR Surface Tension Contact Angle Zeta Potential 12 Figure 2-1. Strategic plan to achieve research goals As it can be seen form Figure 2-1, the first block represents the required techniques and measurements to elucidate polyvinyl alcohol (PVA)/ particle interactions. On the other hand, the second block represents another part of our goal which is bubble formation and stability as well as its modeling. 17

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18 Flotation Study In this study, screening and central composite statistical experimental designs are used to determine the effect of various factors on the removal of MgO and its recovery. The Plackett-Burman design was used to screen out which of the 7 factors being considered were the most statistically significant. In other words, it is a tool that helps determine which factors made the greatest impact on the MgO removal. A central composite design was used to determine if there were any interactions between the three most significant factors determined from the Plackett-Burman design. Screening Design (Plackett-Burman Design) The variables examined in the screening stage were acid concentration (1% and 3 %), Polyvinyl alcohol concentration in the coating solution (1 % and 3 %), the PVA molecular weight (60,000 and 150,000), the degree of hydrolysis (88 %-99 %) of the PVA, particle size (-0.5 mm and 5-9 mm), and drying time of the coating (0 and 2 hrs). The levels were chosen according to the exploratory test results from phase I of this project. The Plackett-Burman design used for this study had 11 factors and 12 experimental runs (Table 2-1). MgO % was determined using chemical analysis. Chemical analyses were performed using wet chemical methods, acid attack (digestion) method as described below. Central Composite Design A central composite design was used to further investigate the three most significant factors (acid concentration, PVA concentration, and particle size) determined from the screening design. Five levels were used. The central composite experimental design had 17 experimental runs (Table 2-2 and Figure 2-2). For each run, the products are chemically analyzed as above-mentioned and the MgO % and MgO removal % were

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19 calculated for all the experimental runs. The computer program, Design expert (SAS Institute, Inc.), was used to perform the statistical analysis for the central composite design. The data was analyzed by fitting the response variables to a second-order polynomial model. Table 2-1. Experimental Plackett-Burman design for 11 variables Run No. Variable Levels 1 2 3 4 5 6 7 8 9 10 11 1 + + + + + + 2 + + + + + + 3 4 + + + + + + 5 + + + + + + 6 + + + + + + 7 + + + + + + 8 + + + + + + 9 + + + + + + 10 + + + + + + 11 + + + + + + 12 + + + + + + Plackett-Burman Variables Used in the Reactive Flotation Study Variables Low Level (-) High Level (+) 1) Acid conc 1 % 3 % 2) PVA conc 1 % 3 % 3) dummy 4) dummy 5) PVA M.W 60,000 150,000 6) Degree of hydrolysis 88 % 99 % 7) Time of drying 0 2 h 8) dummy 9) Particle size -0.5mm 5-9 mm 10) dummy 11) dummy dummy variables are used to calculate the variance of the experimental runs

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20 Y Z X Figure 2-2. Five-level, rotatable central composite design. The X, Y, and Z axes represent the 3 variables, sulfuric acid concentration, PVA concentration, and particle size. The circles represent each experimental run. Table 2-2. Rotatable central composite design with 5 levels and 3 variables Run No. Acid conc PVA % Particle Size 1 -1 -1 -1 2 -1 -1 +1 3 -1 +1 -1 4 -1 +1 +1 5 +1 -1 -1 6 +1 -1 +1 7 +1 +1 -1 8 +1 +1 +1 9 -1.68 0 0 10 +1.68 0 0 11 0 -1.68 0 12 0 +1.68 0 13 0 0 -1.68 14 0 0 +1.68 15 0 0 0 16 0 0 0 17 0 0 0 Levels Variables -1.68 -1 0 +1 +1.68 Acid conc. (%) 0.32 1 2 3 3.68 PVA, (lb/t) 0.6 2 4 6 7.4 Particle size, mm -0.5 0.5-1 1-2 2-5 5-9

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21 Flotation Procedures for Screening and CCD Designs Using 300 ml (3 % H 2 SO 4 ) in 400 ml beaker, particles were pre-coated by spraying 3 % PVA solution (using a mist delivery nozzle) then added to the acidic solution. The experiment was left for 5 min. Dolomite floats to the surface, which was separated by decantation on a screen. The products (floated and unfloated fractions) were dried, weighed, and chemically analyzed. Factorial Design for Conditioning with PVA before Flotation This design was used to study the factors affecting the conditioning step with PVA, which is a promising step for reducing PVA consumption. Table 2-3 shows the design and levels used. Table 2-3. Factorial design for conditioning with PVA Run No. PVA concentration, % Pulp density (S/L ratio) Conditioning time, min 1 -1 -1 -1 2 -1 -1 +1 3 -1 +1 -1 4 -1 +1 +1 5 +1 -1 -1 6 +1 -1 +1 7 +1 +1 -1 8 +1 +1 +1 9 0 0 0 10 0 0 0 11 0 0 0 Levels Variables -1 0 +1 PVA concentration, % 0.25 0.625 1 Pulp density 30 % 50 % 70 % Conditioning time, min 2 11 20 Flotation Procedure for Conditioning Statistical Designs 50 gm of ore were added to 1 % PVA solution in a 600 mL beaker according to specific solid/liquid ratio. The slurry was mixed for required time at 300 rpm (using 2.5

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22 cm magnetic bar). After the conditioning time is elapsed the solids were screened, the solids were used for flotation in acidic solution and the filtrate solution was taken to PVA analysis to determine the PVA residual concentration. Chemical analysis: About 0.5 gm of the dried and ground representative sample were digested in 50 ml of aqua regia by boiling on hotplate until the reaction complete. After cooling, this solution was filtered through a Whatman 42 filter paper into 1000 ml volumetric flask. The filter paper and residue were then washed at least five times to remove all the traces of dissolved salts and acid. The filtrate was diluted with distilled water and thoroughly mixed and the concentrations were measured using Inductively Coupled Plasma, ICP, emission spectrometer, (Perkin Elmer Optima 3200RL Optical Emission Spectroscopy, Norwalk, CT). ICP was calibrated using AFPC rock check No.22. Standard sample concentrations were measured from time to time in the course of the analyses to check the accuracy of the calibration curve. Five replicates were taken and averaged for each element. The following wavelengths were used: Element Wave lengths, nm Ca 315.887, 317.933, 393.366, and 396.847 Mg 279.077, 285.213, and 279.553 P 213.617, and 214.914 Fe 238.204, 239.562, 259.939, and 234.349 Al 308.215 Density and Surface Area Determination Densities of powders were measured using a Quanta Chrome ultrapycnometer. The specific surface area (m 2 /g) of dolomite and apatite particles was determined using Quanta Chrome NOVA 1200 instrument. (Quantachrome Corp., Boynton Beach, FL).

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23 The analysis was performed using a five-point BET (0.10, 0.15, 0.20, 0.25, 0.30) using Nitrogen gas. The particles were outgased at 60C for 24 hours before analysis. PVA Preparation PVA was kindly supplied by Celanese chemicals Co., USA. Different PVA types with various ranges of molecular weights and degree of hydrolysis are used in screening factorial design, namely: Type Average Molecular Wt. Degree of Hydrolysis, % Celvol 165 150000 99 Celvol 540 150000 88 Celvol 305 60000 99 Celvol 203 60000 88 In the rest of the study, PVA, Celvol 165, was used. PVA flakes were gradually dissolved in deionized water at 90 o C with continuous mixing by magnetic stirrer and heated at 90 C for 2 h to produce different PVA concentrations (0.5, 1, 2, 3, and 4 %). Spectrophotometric Determination of PVA PVA solution of certain concentration treated with 25 ml of 4 % boric acid solution and 2 ml of iodine solution (prepared from 1.27g of iodine and 25 g of KI/l), in that order. The resulting solution is diluted to 100 ml and kept at 25C and its absorbance measured at 690 nm against a blank solution containing the same amount of boric acid and iodine solution. Beers law applies in the concentration range of 0-40 mg of PVA/l of solution [Finch, 1973; 1992]. Absorbance spectra were taken using ultraviolet/visible spectrophotometer (UV-Vis spectrophotometer, Perkin-Elmer Lambda 800). All spectra were taken at room temperature.

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24 Static (Equilibrium surface tension) Equilibrium surface tensions were measured for freshly prepared solutions by the Wilhelmy plate method at room temperature. The platinum plate was always cleaned and heated to a red/orange color with a Bunsen burner before use. Dynamic Surface Tension (DST) Maximum bubble pressure method The dynamic surface tension (DST) measurement is important in the dynamic interfacial processes where the equilibrium surface tension is hard to be achieved. The DST can be measured by different methods such as: the drop weight [Jho and Burke, 1983; Miller et al., 1993], oscillating jet [Thomas and Hall, 1975], capillary wave [Kelvin, 1871], growing drop technique [Macleod and Radke 1993], and the maximum bubble pressure method [Mysels, 1986; Ross et al., 1992]. The maximum bubble pressure (MBP) technique is the most commonly used technique for the measurement of DST, and has been applied to a variety of surfactant and polymer solutions [Fainerman et al., 1994; Tamura et al., 1995]. The physical principle behind the MBP measurement is the Laplace pressure; the pressure inside a curved liquid interface is higher than the ambient. This excess pressure (P) can be calculated from the Laplace equation [Adamson and Gast, 1997]. P = r 2 + gh Where is the surface tension, r is the radius of curvature of the bubble, is the liquid density, g is the gravitational constant and h is the depth of the bubble in the liquid. The first term expresses the Laplace pressure due to the curved gas/liquid interface, and the second term is the hydrostatic pressure due to the liquid height above the forming

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25 bubble. The first term will vary during the life cycle of the bubble, while the second term will remain constant. Figure 2-3 shows a typical cycle of a bubble and the resulting pressure within the capillary. After a bubble breaks off from the capillary tip, the pressure is the lowest. As more gas flows into the capillary, the pressure builds up as the gas is pushed out of the capillary and the radius of curvature at the tip decreases. During this expansion process, surfactant is populating the new interface and acting to lower the surface tension. At the point of minimum interface radius of curvature, where a hemisphere of gas is formed at the capillary tip, the pressure reaches maximum. Figure 2-3. Characteristic bubble-pressure vs. time curve in MBP. Both the minimum radius of curvature and the surface tension, as described by the Laplace equation, govern the maximum pressure experienced. On the incremental addition of gas, the bubble expands out of the capillary tip and the radius of curvature gradually increases. This results in a drop in the Laplace pressure, and a resulting rapid expansion of the bubble. At some point, the bubble breaks off from the capillary tip and the whole process starts again.

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26 Dynamic surface tension setup The maximum bubble pressure apparatus was constructed using a differential pressure transducer purchased from Omega Engineering, Inc. (Stanford, CT), with a sensitivity of 0 to 10 in. (25 cm) H 2 O (0 to 2500 Pa). A #23 steel needle was used as a capillary, with nominal 0.025 in. (0.64 mm) external diameter, 0.013 in (0.33mm) internal diameter, and a flush cut tip. The capillary diameter was chosen so that the various resistance of water to bubble growth could be ignored. Such internal and viscous effects are a potential source of error in these measurements that need to be taken into consideration [Garrett and Ward, 1989]. All measurements were conducted with the capillary tip 1 cm beneath the liquid surface. CO 2 gas was used as the bubbling gas to simulate the gas produced in the reaction of acid with dolomite and an oscilloscope connected to the pressure transducer was used to determine the bubble frequency and the dynamic surface tension (Figure 2-4). Rotamete r Polymer Solution Pressure Transducer Pressure Volta g e 1.0 cm de p th Bubble formation Oscillosco p e Air Flow Figure 2-4. Setup for the measurement of dynamic surface tension by maximum bubble pressure method. Contact Angle The angle formed at a point on the line of contact of three phases, of which at least two are condensed phases, by the tangents to the curves obtained by intersecting a plane

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27 perpendicular to the line of contact with each of three phases. One of the phases must be a liquid, another phase may be solid or liquid and the third phase may be gas or liquid. In other words, it is the angle included between the tangent plane to the surface of the liquid and the tangent plane to the surface of the solid, at any point along their line of contact. The surface tension of the solid will favor spreading of the liquid, but this is opposed by the solid-liquid interfacial tension and the vector of the surface tension of the liquid in the plane of the solid surface. s Solid Gas Liquid l Figure 2-5. Contact angle and its relation with surface tension Equilibrium wetting properties of liquids and solutions can be interpreted in terms of the balance of surface tensions (Figure 2-5). sg sl = lg cos Measurement of Contact Angle The contact angle goniometer, Figure 2-6, is a device mounted on the optical bench to examine a single liquid drop or gas bubble resting on the smooth, planar, solid substrate. The drop/bubble is illuminated from the rear to form a silhouette, which is viewed through a telescope connected to computer. The image of the drop/bubble appears on the computer monitor by which the brightness and contrast, focusing and amount of illumination can be adjusted. After adjusting the image the contact angle can be measured.

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28 Figure 2-6. Contact angle measuring apparatus Surface Characterization by FTIR The spectorometer used for FTIR was a Magna-IR760 spectrometer by Nicolet in transmission setting. As for the spectra recorded in transmission mode, KBr pellets were prepared for the background measurements. Another pellets were prepared by mixing about 1 mg of filtered powder with 50 mg of KBr. Transmission spectra were recorded using a DTGS detector, with 128 scans and 4 cm -1 resolution. Zeta Potential Measurements In the zeta potential measurement tests, 1 g of ground mineral samples was added into a 250 ml beaker in which 100 ml 0.003 M KNO 3 solutions were added. The suspension was conditioned for 3 min during which the pH was adjusted, followed by 5 min of conditioning after adding the polymer. It was then allowed to settle for 3 min, and about 10 ml of the supernatant was transferred into a standard cuvette for zeta potential measurement using a Brookhaven ZetaPlus Zeta Potential Analyzer. Solution temperature was maintained at 25 C. Ten measurements were taken and the average was reported as the measured zeta potential. Adsorption These studies were carried out at 25C using 0.5gm mineral sample in 50 ml solution having the desired PVA concentration and the ionic strength fixed at 3X10 -3 M

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29 using KNO 3 One set of experiments was performed first to determine the effect of conditioning time at a fixed pH (pH 7) and PVA concentration was 100 ppm (3.33X10 -8 M). Then set of experiments was also carried out as a function of pH at the same PVA concentration. Adsorption isotherm was also determined for PVA/dolomite, PVA/apatite, PVA/dolomite/apatite supernatant, PVA/apatite/dolomite supernatant systems at pH 7 and 3X10 -3 M KNO 3 as an ionic strength. After the conditioning step, the suspension was centrifuged at 3000 rpm for 5 min using an IEC-Medispin centrifuge (Model 120). Then a volume of the clear solution was withdrawn for measurement of the PVA residual concentration. In adsorption kinetic experiments, a 0.5 gm of dolomite or apatite were added to 100 ppm (3.33X10 -8 M) PVA solution a 30 ml screw-capped bottle and was shaken at room temperature using Wrist hand shaker for a given recorded time (0.05, 0.083, 0.0166, 0.25, 0.5, 1, 2, 4, 6, 8, 10, 16, 20, 24 h). After that the contents of each bottle were allowed to settle, followed by centrifugation step using an IEC-Medispin centrifuge (Model 120). The amount of PVA adsorbed was determined by difference between the initial and final concentrations measured spectrophotometrically with a Uv-vis spectrophotometer (UV-Vis spectrophotometer, Perkin-Elmer Lambda 800). These experiments were used to establish the equilibrium time for adsorption of PVA on dolomite and apatite. This equilibrium time was used as contact time in adsorption isotherm experiments. Dissolution Kinetic Experiments Dolomite specimens (1-2 mm and 0.2-0.3 mm), uncoated and coated with PVA, were added to 2000 ml aqueous medium (3 % H 2 SO 4 ) at 23 0.5C to carry out 120 min static dissolution tests. After a definite time interval, solution samples were collected

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30 periodically and concentrations of Mg 2+ and Ca 2+ were determined with ICP. The relations of concentration, C, with time, t was plotted to explore the dissolution kinetics of the dissolution process. Pilot Scale Experiments The Sluice The pre-conditioned material is introduced into a feed box, which contains 3 % sulfuric acid. The reaction of sulfuric acid with particles starts in the feed box forming bubbles around dolomite particles and creating the required density difference for the separation in that device. The particles soon enter the moving stream and, because of the bubbles on dolomite particles, they settle at lower rate and float to the surface when the enough bubbles formed and carried away till they reach the lip of the trough and discharged with liquid overflow. Since phosphate particles do not produce CO 2 and have no bubbles at their surfaces, they are collected at the bottom of the trough (Figure 2-7). Figure 2-7. Schematic diagram for separation of dolomite from phosphate in sluice Pre conditioned F eed Dolomite Phos p hate Inclination angle to horizontal Reject Trough angle Feed B o x 3 % Su lfuric acid C once n t r at e Sluice Experiments 250 gm of ore (a mixture of dolomite and phosphate), with particle size 1-2 mm, were conditioned in 1 % polyvinyl alcohol solution for 5 minutes, then screened to separate the solids from PVA solution. The screened solution was analyzed to determine the actual PVA consumption by depletion method. Or the material was sprayed with the

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31 equivalent amount of PVA and was tumbled to attain a good coating. After that, the coated solids were poured into sluice feed box which the sulfuric acid and the reaction starts to generate CO 2 bubbles. The particles move through the sluice at flow rate 125 ml/sec (2 GPM). The floated fraction, dolomite, was collected on 0.5 mm screen and the sink fraction, phosphate, was collected in the sluice trough. The floated and sink products were analyzed for MgO, P 2 O 5 CaO, and insoluble residue (I.R.).

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CHAPTER 3 TECHNICAL ASPECTS OF REACTIVE FLOTATION: PRELIMINARY TESTS Introduction The reactive flotation process, as mentioned earlier, requires certain conditions to give good results and separate dolomite from phosphate rock. The main requirements for RF to work properly are the acidic medium and surfactant or polymer, which attaches to the dolomite, to allow the acid to diffuse through but at the same time remain impermeable to the CO 2 gas produced by the reaction. Moreover, the formation of CO 2 will lead to stretching of the membrane-like surfactant layers, which requires an elastic behavior of that membrane. The elasticity of the membrane formed around the particle will then allow the formation of stable bubbles. The stable bubbles are the main criterion in RF to float the dolomite particles and separate them from others. At the starting point of this process, the most well behaved acids and surfactants, under RF conditions, were not known. Different acids and surfactants can be used but it was unknown which one would best fulfill the previously mentioned requirements for the RF process. For that reason, in the current study, preliminary tests were conducted using different acid types (sulfuric, hydrochloric, nitric, acetic) within a particular concentration range (0.5 4 % v/v) as well as different types of surfactants (anionic, cationic, and non-ionic), which were prepared as 1-2 % surfactant solution and used in two different ways: (1) surfactant was added to acidic solution and/or (2) surfactant was used to coat the particle before adding the particle to the acidic solution. Also, poly-vinyl32

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33 alcohol (PVA) was used in this study. Vegetable and corn oil were used at the acidic solution/ air interface and oil height was 0.5-0.6 cm. List of Potential Surfactants: Surfactants Screening A list of potential surfactants used in this study, are given in Table 3-1. The list contains different types of surfactants, (i.e., cationic, anionic, and non-ionic, as well as polymers). Table 3-1. Surface-active agents used in RF tests Surfactant Chemical Name Type Arquad 12-50 Dodecanaminium+isopropyl alcohol Cationic Lilamine N-3-aminopropyl-N-tallow alkyltrimethylenediCationic Armac HT Amines, hydrogenated tallow alkyl acetates Cationic Armid HT Amides Cationic Armeen 12 D dodecanamine Cationic Ethofat Tall Oil Anionic SDSO 3 Sodium dodecyl-sulphonate Anionic SDSO 4 Sodium dodecyl-sulphate Anionic Oleic acid Oleic acid Anionic Arlacel Sorbitan sesquioleate Non-ionic Span-20 Sorbitan monolautrate Non-ionic G-1096 Polyoxyethelene-sorbitol hexaoleate Non-ionic Brij-97 Polyoxyethelene oleyl ether Non-ionic Arlatone T Polyoxyethelene polyofatty acid ester Non-ionic Tween-21 Polyoxyethelene Sorbitan monolautrate Non-ionic Tween-85 Trioleate Non-ionic PVA Poly-Vinyl-Alcohol Non-ionic Initial Screening Tests A 100-pound sample of high-dolomitic phosphate oversize pebble was obtained from the IMC Four Corners mine. This is not normal high MgO rock, but the oversized high MgO rock that is removed from pebble. As such, neither the screen weight fractions nor the chemical analyses are representative of pebble. However, the rock is representative of the high-dolomitic rock that needs to be separated. The rock was screened, and each fraction is chemically analyzed in Tables 3-2 and 3-3.

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34 Table 3-2. Size analysis of the dolomitic phosphate sample Size, mesh Size, mm Wt. % % Cumulative (passed) % Cumulative (retained) + 3/8 in 3/8 in +3.5 3.5+6 6+9 9+16 16 + 9.5 9.5+5.6 5.6+3.36 3.36+2 2+1 1 11.62 65.36 18.14 2.05 1.6 1.23 100.00 88.38 23.02 4.88 2.83 1.23 11.62 76.98 95.12 97.17 98.77 100 100.00 Table 3-3. Chemical analyses of the dolomitic phosphate sample Size, mesh P 2 O 5 % CaO % MgO % Fe 2 O 3 % Al 2 O 3 % +3/8 in -3/8 in +3.5 -3.5+6 -6+9 -9+16 -16 19.86 21.25 17.09 24.32 20.42 13.62 32.23 36.34 27.92 38.90 28.71 22.75 4.02 3.43 2.34 2.75 2.12 2.44 0.93 1.15 1.32 1.08 1.27 1.13 0.52 0.84 0.86 1.17 1.07 0.95 Since most of the rock was relatively coarse, a portion of it was crushed and re-screened to obtain smaller fractions that could be used in the tests. Specific Tests The results of some preliminary testing are shown in the following paragraphs in terms of acid type and dosage, surfactant type and dosage, particle size, and using of oil layer at the water/acidic solution interface. Acid type Different acids (H 2 SO 4 HCl, HNO 3 and Acetic acid) were used. Inorganic acids: HCl, HNO 3 and H 2 SO 4 gave the same results at 2 % acid concentration. On the other hand, the acetic acid (RCOOH) formed a very small number of bubbles at 2 % acid concentration. Increasing the concentration of acetic acid to 5 % gave no significant variation in bubble formation, which means that the organic acids are weak acids. Consequently, a large amount of organic acids is needed relative to inorganic ones.

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35 Acid dosage Since all the inorganic acids behave in the same manner, sulfuric acid was used in the rest of the experiments. Table 3-4 shows the effect of acid concentration on the bubble formation rate, amount of bubbles formed, and particle floatability that were taken as a criterion to compare the results. The surfactant used for coating the dolomitic particle was dodycyl sulphonate (SDSO 3 ). Table 3-4. Effect of sulfuric acid concentration Sulfuric acid concentration, % 0 0.25 0.5 1 2 Bubble formation rate Very slow Slow Fast Rapid Amount of bubbles formed Very small number of bubbles (about 5 bubbles for 10 minutes then no bubbles formed) The interval between formation of two bubbles was about 30 seconds Increasing the rate and number of bubbles formed Continuous formation of bubbles but at rate higher than 0.5 % Continuous and quick formation of many bubbles Flotation of dolomite particle No flotation Float after 5-10 minutes Float after 1 minute From Table 3-4, we notice that the reaction between dolomite and acid to produce CO 2 decreases noticeably with decreasing acid concentration and the flotation of dolomite particle takes longer time (5-10 min) in 1 % acid than in 2 % acid. Consequently, the 2 % sulfuric acid concentration is the most suitable acid concentration for bubble formation in terms of both bubble formation rate and amount of bubble formed. Because of the wide gap between 1 % and 2 % acid concentration another set of experiments were conducted as shown in Table 3-5 to get the optimum acid concentration.

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36 Table 3-5. Effect of sulfuric acid concentration on the bubble formation Sulfuric acid concentration, % 1 1.2 1.4 1.6 1.8 2 Bubble formation rate Increases Amount of bubbles formed Continuous and small No. of tiny bubbles Continuous & large No. of tiny bubbles Flotation of dolomite particle Takes 20 minutes to float, not stable (particle goes up and down) Floats and stays at water/oil (W/O) interface for 5 min. Then oscillates within 2 min intervals Floats and stays at (W/O) interface Table 3-5 shows that the flotation at 1 % & 1.2 % is not stable and flotation occurs after the particle loses part of its weight due to reaction with acid. Accordingly, this concentration deals with a small particles (smaller than 1mm) rather than large particles. The bubble formation rate is decreased with the acid percentage from 2 % to 1 %, but as the difference was narrower between 1.6-2 %, 1.6 % acid concentration was found to be optimal. The effect of acid concentration on the RF criterion was schematically summarized in Figure 3-1. Bubblformation e rate Number of bubbles formed Flotatin o A B C time Acid conc. Acid conc. Increases Increases Increases Acid conc. Figure 3-1. Effect of acid concentration on: A) Bubble formation rate, B) Number of bubbles formed, C) Flotation time. Surfactant type Table 3-6 shows the anionic, cationic and non-ionic surfactants used. According to RF criterion, the performance of Anionic surfactant was superior to Non-ionic, which was superior to Cationic. Anionic surfactants, especially SDSO 3 formed stable

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37 membranes that captured CO 2 and persisted for 10 minutes. This may be due to its ability to work at low pH. Therefore, SDSO 3 was used in the next experiments. Table 3-6. Preliminary tests of high dolomitic phosphate with different surfactants Surfactant Name Remarks Arquad 12-50 (1%) Lilamine (1%) Armac HT (1%) Armid HT (1%) Armeen 12 D (1%) stable bubbles for 20-30 sec, particle 2-3 mm can float less stable bubbles, stay 10 s, particle does not reach to surface of the solution (air-water interface) surfactant precipitated in the solution Ethofat (1%) SDSO 3 (1%) (2%) SDSO 4 (1%) (2%) Oleic acid Formation of bubbles on the particle surface then particle floats Bubbles form and go up to solution surface, but particle doesnt float Particle takes 2-3 sec to float Bubbles form and go up to solution surface, but particle doesnt float Flotation rate in case of SDSO 4 < Flot.rate in case of SDSO 3 Added as it is, particle stays at surface of the solution (air-water interface) with formation of many small bubbles. Arlacel Span-20 G-1096 Brij-97 Arlatone T Tween-21 Tween-85 Common observations for non-ionic surfactants: No significant change in behaviour of different non-ionic surfactants used The flotation of high dolomitic particle after 3-5 seconds and stay at the surface, while the low dolomitic does not float. Formation of stable bubbles on the floated particle surface Surfactant dosage The results of different dosages of surfactant sodium dedocyl sulfonate (SDS) are shown in Table 3-7 in terms of bare and coated particles. It is indicated from Table 3-7 that bare particles, without coating, form s bubbles quickly and in large quantity due to rapid dolomite/acid reaction but the bubbles are not stable at the interface where they can be collected.

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38 Table 3-7. Effect of surfactant concentration (SDSO 3 2%) SDSO 3 (2 %) 2 % 4 % 6 % Particle without coating Many bubbles formed Small particle (1-2 mm) floats Large particle (3-4 mm) goes up and down Many bubbles formed Particles (1-2 mm) and (3-4 mm) float Many bubbles formed Particles (1-2 mm) and (3-4 mm) float Particle coated with SDSO 3 Many bubbles formed -small particle floats-large particle does not float On the other hand, the coated particles take more time to float due to the diffusion of acid through the surfactant layer around each particle. Also, a greater number of bubbles are formed when no coating is used. Finally, when coating is not used each bubble forms as a separate bubble, while formation of bubbles clusters occurs when with a coating with SDS is used. Increasing the surfactant concentration increases the flotability of the particles and large particles (3-4 mm) can float at high surfactant concentrations of up to 4 %; after that, there is no noticeable change in floatability(i.e., 6 % is very much similar to 4 %). The oscillated motion of large particles (3-4 mm) for short period of time (3-5 sec) was noticed at 2 % surfactant concentration; however, the same size floats without oscillation at 4 % and 6 %. This means more surfactant is needed. Particle size The particle size effect on the RF process was studied for coated and uncoated particles. The observations of different size ranges were recorded in Table 3-8 which indicates that the coating affects the stability of the bubbles on the particle surface as well as the stability of the floated particle at the interface; however, even uncoated particles

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39 release many bubbles and float quickly for very short time due to their rapid reaction with acid. Table 3-8. Effect of particle size on the dolomitic particle floatability Particle Size, mm 0.5-1 1-2 2-4 4-6 Without treatment Particle floats and stays at water/air interface Particle floats for few seconds then oscillates No flotation -the particle oscillates without reaching the interface With treatment Floats and stays at interface Floats after 30 sec and stays at (w/a) interface Oscillates and finally stays at w/a interface Floats after 1 min then oscillates for 5 min This rapid rate of reaction causes rapid reduction in particle weight. In addition, it causes the production of many bubbles at a faster rate than bubbles-particle detachment, leading to presence of uncoated particle at the interface, although for shorter time than coated ones. But once the uncoated particle reaches the interface, the bubbles will not be stable anymore due to high surface tension, which is the reverse of coated particles. Large size particles need more bubbles; the bubbles formed were not enough to lift the particle causing the particle to oscillate up and down. On the contrary, the small particles 1-2 mm and smaller do not oscillate and float directly to the interface. To improve the stability of the floated particles at the interface, the reduction of the surface tension is required. Therefore, the oil layer was used at the interface for that purpose. Oil-Surfactant Experiments Addition of an oil layer, either vegetable or corn oil, to the acidic solution/ air interface was attempted with different types of surfactants to enhance the bubble stability at the interface, as shown in Table 3-9. The selected surfactants for this set of

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40 experiments were the best ones from Table 3-6. The particle was coated with the surfactant before its addition to acidic medium. Table 3-9. Effect of presence of surfactant and oil layer on particle flotation Surfactant Type Observations Arquad Lilamin Cationic Formation of bubbles due to dissolution of dolomite, but no flotation. 2 % sulfuric acid solution + oil layer Ethofat SDSO 3 SDSO 4 Anionic Bubble formation, Particle floats to water/oil interface for 10 min and then comes back to acidic solution. Arquad Lilamin Cationic Formation of cluster of bubbles on particle surface, but no flotation. 2 % sulfuric acid solution + 1 % surfactant Ethofat SDSO 3 SDSO 4 Anionic Bubble formation and particle oscillates and the bubble bursts at water/air interface. Arquad Lilamin Cationic The same as before Ethofat Bubbles form No flotation 2 % sulfuric acid solution + 1 % surfactant + oil layer SDSO 3 SDSO 4 Anionic Bubbles form on particle surface and particle floats to water/oil interface then to oil/air interface It is clear that, as can be seen in Table 3-9, the oil layer enhance the bubbles stability on the particle and at the interface. When the particle floats to the acidic medium/oil interface, the floated particle stays at the interface for up to 10 min. The presence of oil layer may add another layer, an oil layer, in addition to the surfactant layer on the particle surface, although this would depend on the adsorption of the surfactant to the particle as well as the type of the surfactant and its interaction with oil. From Table 3-9, it was observed that the presence of a low percentage of surfactant (1 %) in the acidic solution slightly increases the stability of bubbles in the absence of an oil layer. The presence of 1 % surfactant in the solution may reduce the fast detachment of surfactant molecules from the particle surface through reduction of the diffusion of surfactant molecule to bulk solution.

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41 By using acidic solution in combination with 1 % surfactant and an oil layer (Table 3-9), it was found that the oil layer causes more stable formation of bubbles on the particle when the particle floats to oil/air interface. The particle does not go back into the acid solution but stay at oil/ air interface. Consequently, large particles of up to 3 mm can float in the presence of the surfactant and oil layer. SDS is a good surfactant under these experimental conditions. However, Ethofat and cationic surfactants did not work well in the presence of surfactant mixed with acidic solution. This may be due to the interaction between the oil layer on the particle and those surfactants possibly causing the formation of a non-flexible surfactant layer, which cannot capture the CO 2 gas and cannot form the bubbles required for flotation. Poly-Vinyl-Alcohol (PVA) Testing PVA was used as a viscous polymer to coat and to float the dolomite particles. The effect of acid concentration, particle size, and different PVA concentration were studied. Effect of acid concentration PVA forms a membrane on the particle. This membrane needs a high acid concentration to penetrate it and to perform the reaction between the acid and particle surface. It was observed that there were a very small number of bubbles generated. However, most of the bubbles formed a cluster on the particle surface, which increased the volume of the bubbles at the surface and floated the particle. The floated particles were not stable at the beginning, going up and down at interface, but ultimately staying at the interface for long time (sometimes more than 2 days). On the other hand, PVA also floated the low dolomite-content particles, which were able to form bubbles. This observation is due to PVAs very low permeability by CO 2 which makes it the best among the surfactants used. By increasing the PVA

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42 concentration, longer time was taken to form a bubble and to float the particle, which requires high acid concentration, but in this case it became possible to float large particle sizes (up to 8 mm). Table 3-10. Effect of acid concentration Acid concentration, % 0.5 1 1.5 2 Particle coated with PVA Formation of cluster of bubbles Very low bubble formation rate No particle flotation (up and down at 1.5 %) Cluster of bubbles formed Low bubble formation rate Particle floats From Table 3-10, it is evident that the findings were that the PVA forms a membrane on the particle. This membrane needs a high acid concentration to penetrate it and to perform the reaction between the acid and particle surface to release the gas, which is responsible for floating the particle. No quick release of bubbles was observed at low acid concentrations, but rather only a very small number of bubbles at the beginning; furthermore, the rate of bubble formation and particle flotation was very slow. After a while, an increasing number of bubbles appeared and clustered on the particle surface, which then caused the particle to float. Moreover, at low acid concentrations, the floated particles were not stable, going up and down at the interface due to absence of surfactant. Even at high acid concentrations, the acid takes time to penetrate the PVA membrane and react with particle surface. For that reason, the bubble formation rate was low. But after the formation of bubbles began to cover the particle surface with clusters of bubbles, the particles started to float. The acid concentrations of less than 2 % were not effective due to the high viscosity of PVA membranes, which requires a high concentration difference to permeate

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43 the membrane and the reach the particles surface. Because the previous set indicated that the 2 % acid concentration was optimal, another set of experiments was conducted at higher acid concentration (> 2 %) under the premise that a concentration higher than 2 % would be even better. Therefore, additional experiments were conducted using 2.5-4 % acid concentrations. Table 3-11 shows the results of those experiments. Table 3-11. Effect of acid concentration above 2 % Sulfuric acid concentration, % 2.5 3 3.5 4 Bubble formation rate Increases with increasing acid conc. % Amount of bubbles formed Cluster of bubbles formed on the particle surface Rapid reaction no stable bubbles are seen on the surface (bubbles released in high rate from particle surface) Flotation of dolomite particle Particle Floats Is more stable than higher acid conc. Particle floats Less stable than 2.5-3 % Particle oscillates and finally goes down There was no flotation at acid concentrations above 3 % due to the high bubble formation rate and absence of stable bubbles that can attach to the surface of the particle and float it. The bubble formation rate increases with increasing acid concentration, 4 % > 3.5 % > 3 % > 2.5 %; however, 2.5-3 % resulted in the most stable bubbles. Different PVA concentrations (2 %, 3 %, and 4 %) were also used and the experiments indicated that 3-4 % concentration is most suitable for dolomite flotation. However, increasing PVA concentration increased the time it takes each particle to float. Effect of particle size Increasing the particle size increased the time needed to float the particle. This can be explained by variation of surface area to weight of the particle ratio, which decreases with increasing particle size. The results of these tests are shown in Figure 3-2.

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44 0102030-11-22-55-9+9Particle size, mmTime, min Figure 3-2. Effect of the particle size on the time needed to float the particle in 3 % H 2 SO 4 when the particle is pre-coated with 3 % PVA PVA with acid vs. PVA on the particle surface By using two beakers, one of them containing uncoated particles added to 3 % PVA + 3 % acid solution and the other containing PVA coated particles added to 3 % acidic solution, the comparison between the performance of different application of PVA was obtained. Table 3-12 shows the results in terms of bubble formation, rate of formation, and particle flotation. When uncoated particles were added to the PVA+acid solution, the acid attacked the particle surface. Consequently, the dissolution of dolomite is higher than in case of coating the particle with PVA before adding it to the acidic solution. Presence of micro-bubbles (cotton shape) at the particle surface indicated the dissolution of dolomite. Bubbles were vertically distributed rather than horizontally in first beaker, while the bubble distribution was horizontally uniform (spreading on the particle surface) in the second beaker. The bubble formation rate is higher in the first case than in the second.

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45 The flotation of the particles was better in the second case due to the presence of relatively large bubbles and uniform bubble distribution. Despite rapid dissolution of dolomite particles in the first case, flotation of the particles took a long time due to the small size of the bubbles. In both cases, the particles floated stay at interface for a long period of time (days). Table 3-12. Comparison between coating the particle before adding it to acidic solution and adding the particle to acid+PVA solution without coating First beaker Second beaker PVA + acidic solution in the beaker and the particle added without coating Particle was pre-coated with PVA before adding it to acidic solution Bubble formation rate Tiny bubbles were formed Relatively large bubbles were formed Amount of bubbles formed Cluster of the bubbles grows vertically and cover parts of the particle surface no uniform distribution of the bubbles on the particle surface. Cluster of the bubbles grows almost horizontally and uniformly distributed on the particle surface. Flotation of dolomite particle Takes long time (hours) to float Takes short time (min) to float Preliminary Testing Using PVA Coated Particles In the following preliminary tests, all particles were pre-coated with PVA Flotation of a Representative Sample Flotation of a representative sample, a mixture of phosphate and dolomite, was attempted in a one-liter beaker. The percentage of floated fraction by weight obtained after 6 hours was about 22 % and un-floated fraction was about 78 %. It was noticed that the smaller particle sizes (less than 1mm) floated immediately. It was then determined that using small size fractions of about 1 mm coated with PVA would reduce the flotation time with very low chance to dissolve the particle; it appears that good PVA coating

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46 prevented rapid acid-attack to the particle. On other hand, we should take into account that the PVA consumption will increase due to increased surface area. Fraction of Representative Sample (-4+1.19 mm) A bucket (11 in diameter and 15 in height) was filled with a solution of 15 liters of water containing 3 % sulfuric acid and 3 % PVA. The water height in the bucket was about 1 foot. Most of the particles were in monolayer form to avoid mechanical entrapment of the particles. After applying the finalized procedure, the MgO percentage in the representative sample was reduced to less than 1 % of the sink fraction; P 2 O 5 percentage was reduced to less than 4 % (Table 3-13). Table 3-13. Results of representative sample (4+1.19 mm particle size) Sample Chemical analysis, % Recovery, % Wt% MgO CaO P 2 O 5 I.R. MgO CaO P 2 O 5 I.R. Float Sink 14.55 85.45 13.21 0.75 32.56 34.83 2.71 19.35 6.89 10.55 75.1 24.9 13.73 86.27 2.33 97.67 10.01 89.99 Balance 100 2.56 34.50 16.93 10.02 100 100 100 100 Feed 100 2.6 34.78 16.84 10.32 100 100 100 100 Effect of Time on Weight Percentage of Floated Particles Two samples of 4+1.19 mm size were gathered at different flotation time (30 min and 60 min). The samples were immersed in a beaker containing a solution of 3 % PVA and mixed to ensure the coating of all particles with PVA before adding the sample to acidic water (3 % sulfuric acid). The same bucket as in the previous test was used and at the same conditions. Each experiment was observed for two days and the floated fraction was collected. Most of the particles (about 90 %) floated within 30 minutes and about 10 % in the remaining two days of the experiment. The results are shown in Table 3-14.

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47 Table 3-14. Effect of time on the flotation of 4+1.19 mm particle size Chemical Analysis Recovery Time, min Wt% MgO% CaO% P 2 O 5 % MgO% CaO% P 2 O 5 % Float Sink 16.75 83.25 13.62 0.78 24.25 31.12 0.76 18.89 77.84 22.16 13.55 86.45 0.8 99.2 Balance 100 2.93 29.97 15.73 100 100 100 30 Feed 100 3.03 30.38 15.76 100 100 100 Float Sink 17.44 82.56 13.6 0.81 26.17 30.8 0.94 19.06 78 22 15.22 84.78 1.03 98.97 Balance 100 3.04 29.99 15.90 100 100 100 60 Feed 100 3.03 30.38 15.76 100 100 100 The percentage of MgO was reduced to about 0.8 %; the percentage of P 2 O 5 was reduced to less than 1 % in the float fraction, which indicates that using PVA in a pre-coating solution is a promising process for separation of dolomite from phosphate pebbles. Effect of Size on the Flotation Two samples were crushed in a closed circuit to obtain the following sizes: 4+1.19 mm and -3.36 +1.19 mm. The conditions were the same as in the previous two tests. The results of these tests are shown in Table 3-15 within 5 minutes flotation time. The percentage of MgO was reduced to less than 1 % (0.6 % of the un-floated fraction in first experiment and 0.95 % in the second). Table 3-15. Effect of particle size on flotation Chemical analysis, % Recovery, % Size, mm Sample Wt% MgO CaO P 2 O 5 I.R. MgO CaO P 2 O 5 I.R. -4+1.19 Float Sink 20.5 79.5 12.13 0.6 30.34 30.24 3.31 19.13 8.1 9.6 83.9 16.1 20.55 79.45 4.27 95.73 17.87 82.13 Balance 100 2.96 30.26 15.89 9.29 100 100 100 100 Feed 100 3.03 30.38 15.76 9.46 100 100 100 100 -3.36+1.19 Float Sink 17.8 82.2 11.84 0.95 34.53 38.02 3.86 20.07 7.04 10.35 72.96 27.04 16.43 83.57 4 96 12.84 87.16 Balance 100 2.89 37.40 17.18 9.76 100 100 100 100 Feed 100 2.95 37.07 17.41 9.93 100 100 100 100

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48 Summarizing Remarks Separation of dolomite from apatite using CO 2 generated in the chemical reaction between dolomitic particles and slightly acidic media was explored by testing different parameters effecting this process, including: acid type and concentration, surfactant type and concentration, particle size, and use of polymer (PVA). The results were promising with anionic surfactants, especially SDSO 3 and Mr. Bubble solution with a concentration of 1.6 % sulfuric acid; however, low dolomite-content particles did not float. The most encouraging results were obtained with PVA, which floats the low dolomite-content particles, in addition to floatation of large particle sizes. Additional testing with a representative sample of ore mixture (phosphate and dolomite) showed the ability to reduce the MgO content to less than 1 % by using a PVA concentration of 3 % in an acidic medium concentration of 3 %. The next step will be the optimization of the RF process using PVA as well as performance of this process under dynamic conditions.

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CHAPTER 4 OPTIMIZATION OF THE REACTIVE FLOTATION PROCESS AND PILOT SCALE TESTING Introduction In previous chapter, it was demonstrated that when PVA coated high MgO phosphate rock is immersed in a 3 % sulfuric acid solution, effectively all the high MgO particles will float to the surface leaving a sink phosphate rock phase that is a low in MgO. In this chapter, the optimization of separation process using PVA as well as development of a separation continuous process is discussed. In this chapter, the RF is optimized using statistical designs (i.e., screening statistical design and central composite design (CCD)). Also, the reduction of PVA consumption was studied using statistical design, (i.e., factorial design). The tests show that as little as less than one pound of PVA per ton of feed rock can be effective in floating the dolomite. The tests also show that there is no significant adverse effect of having the sulfuric acid solution saturated with calcium sulfate. Furthermore, pilot scale testing of a simple sluice was carried out and demonstrated the effectiveness of this approach in giving a good separation between the phosphate and dolomite particles. Optimization of the RF Process Screening Statistical Design The MgO % removal in floated fraction, Table 4-1, was used as the response in calculating the statistical effect of variables. The effect of variables are calculated as follows: 49

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50 Table 4-1. The MgO % removal in floated fraction for Plackett-Burman design. Runs Response (MgO % removal) 1 3 2 3 3 3 4 3 5 86 6 90 7 3 8 12 9 3 10 20 11 3 12 3 6ReRe)()( sponsesponseEi (4.1) The variance is estimated by evaluating the effect of dummy variables and using this equation: nEVdeff22 (4.2) where Ed = effect of dummy variable and n = number of dummy variables = 5. The statistical significance of the effects is evaluated using the student t-test as calculated using: 2iEt (4.3) where the degrees of freedom = 5, confidence level = 95 % and t 5,0.05 = 2.015. Comparing the absolute t-values to 2.015 led to acceptance of variables with a higher t-value and rejecting the variables with lower t-values. In other words, the variables accepted were significant within 95 % confidence level. This comparison of the Plackett-Burman design is presented in Table 4-2. The PVA molecular weight t-value is 2.761,

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51 which is higher than 2.015. Nevertheless, the higher PVA molecular weight was used because of its significance. From the Plackett-Burman design, the most significant variables are acid concentration, PVA concentration, and particle size. From the screening design, a model relating the MgO % removal to the different variables could be represented by: y = -91.75 + 14.83X 1 +12X 2 3.2X 3 (4.4) where y represents MgO % removal and X 1 X 2 and X 3 represent acid concentration, PVA concentration, and particle size, respectively. All coefficients are statistically significant close to 95 % confidence level. The negative sign for particle size coefficient indicates that increase the particle size can lead to a decrease in the MgO % removal. On the other hand, the positive acid concentration and PVA concentration values indicate that an increase in both concentrations lead to higher MgO % removal. In order to further investigate the interaction among these three significant variables with respect to their effect on MgO % removal, a central composite design focusing on these three variables with five levels was used. Table 4-2. Plackett-Burman calculated t values for different variables. The decisions to accept or reject the significance of variables on the bases of comparing t-value to critical value at 95 % confidence level. Factors Effect on MgO % removal (t-value) Significant Variable Sulfuric acid concentration 2.69697 Accept PVA concentration 2.181818 Accept PVA Molecular Weight (MW) 2.969697 Accept PVA degree of hydrolysis (D.H.) 0.181818 Reject Particle size 2.45455 Accept Drying time 0.333333 Reject Statistically significant (95 % confidence level) (+ ve) sign indicates more MgO % removal (ve) sign indicates less MgO % removal

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52 Central Composite Design Central composite design (CDD) results of dolomite flotation experiments are given in Figures 4-1 and 4-2 in terms of MgO removal % in floated fraction and MgO % in sink (nonfloat) fraction respectively. The confidence interval is within 95 %. In other words, the effects are statistically significant at the 95 % level. The standard deviation and R-Squared for both of them are 13, 0.9287 and 0.36, 0.9287 respectively. It was indicated, from these figures, that the % MgO recovery and MgO % in concentrate are greatly and positively affected by increasing either acid concentration or PVA dosage, (i.e., % MgO recovery increases from 30 to more than 90 % and MgO % in the concentrate decreases from more than 2.1 to 0.6 respectively). However, particle size negatively affects the % MgO recovery and MgO % in concentrate. With increasing particle size the % MgO recovery decreases. At the maximum acid concentration and PVA dosage, it decreases from 90 to 75 % and % MgO concentration in the concentrate increases from 0.6 to 1.1 %. As it can be seen from these results that the PVA consumption is high (about 4.5 lb/t), which is economically unfeasible, to get a concentrate contains < 1 % MgO with high recovery > 90 %. Therefore, further study is needed to reduce that consumption, which is discussed in next section. Research to Reduce the PVA Consumption From the results obtained from the experimental designs following the screening the main factors, then studying the main factors, unfortunately, the PVA consumption was about 4-6 lb/t (calculated according to used amount of PVA to certain weight of rock including the losses on the coating device), which threaten the success of this process economically. At this point, it was necessary to find a method to reduce the consumption.

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MgO Removal (floated) %Acid concentration, %PVA dosage, lb/t 1.0 1.5 2.0 2.5 3.0 2 3 4 5 6 74 94 44 MgO Removal (floated) %Acid concentration, %PVA dosage, lb/t 1.0 1.5 2.0 2.5 3.0 2 3 4 5 6 73 43 93 A B MgO Removal (floated) %Acid concentration, %PVA dosage, lb/t 1.0 1.5 2.0 2.5 3.0 2 3 4 5 6 34 74 54 14 C Figure 4-1. Effect of PVA dosage and acid conc. on MgO recovery % in floated fraction at different particle size A) Particle size = -0.5 mm B) Particle size = 1-2 mm C) Particle size = 5-9 mm 53

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54 MgO% in unfloated fractionAcid concentration, %PVA dosage, lb/t 1.0 1.5 2.0 2.5 3.0 2 3 4 5 6 0.9 1.3 1.7 2.1 0.5 MgO% in unfloated fractionAcid concentration, %PVA dosage, lb/t 1.0 1.5 2.0 2.5 3.0 2 3 4 5 6 0.9 1.3 1.7 2.1 0.5 A B MgO% in unfloated fractionAcid concentration, %PVA dosage, lb/t 1.0 1.5 2.0 2.5 3.0 2 3 4 5 6 1.3 1.7 2.1 0.9 2.5 2.9 C Figure 4-2. Effect of PVA dosage and acid concentration on MgO % in Unfloated fraction at different particle size A) Particle size = -0.5 mm B) Particle size = 1-2 mm C) Particle size = 5-9 mm

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55 In this regard many tests were conducted among these tests were: Using compatible compounds with PVA like starch and cellulose. It was found that the presence of these compounds negatively affected the stability of the bubbles at the interface. Using fine particles (40 mesh) with different PVA (1, 2, 3 %) and acid conc.(1, 2, 3 %). It was found that the 3 % PVA and 3 % acid were needed which is the same condition as before and in addition the reaction was too fast due to the high surface area of the small particles. PVA + Drimax (spreading agent): to spread the PVA on the particle surface and then reduce the amount needed to cover the particles. The results of these experiments indicates that there is an interaction between the PVA and Drimax in such a way that prevented the formation of stable bubble at the particle / solution interface, probably by interfering with the crosslinking of the polymer layers that is necessary for the formation of a membrane and consequently stable bubbles. PVA + Boric acid: as it is in the literature [Finch, 1973; 1992], the boric acid and borax are used in PVA crosslinking. Using the boric acid (5 % of PVA) helps in reducing the PVA consumption due to polymer crosslinking but we did not go further in these experiments because of toxicity of boric acid and environmental reasons. PVA + Na 2 SO 4 : sulfate ions lead to coagulation of the PVA according to literature [Finch, 1973; 1992]. It was found that the coagulation is not enough to float the dolomite particle at low PVA concentration. Conditioning of the rock particles with PVA and screening it (or filtering it) to recover the excess PVA. Actually, this step was a most promising one in which the consumption of PVA was reduced to 1 lb/t instead of 4-6 lb/t in previous coating procedure. The conditioning step (with about 1 % PVA) in the same manner as a regular flotation is followed by a filtration step and calculation of the actual PVA consumption. On the other hand, it was found that the full coverage of the particle with PVA is not needed since the formation of some bubbles may be enough to create the density difference and by using sluice or spiral in which the dolomite particles will be lighter and follow the liquid stream. In this manner, the dolomite particle can be separated from the phosphate.

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56 Experimental Design of the PVA Conditioning Step Due to the high PVA consumption as indicated from experimental designs, different methods were tested as mentioned before, the conditioning step as in regular flotation circuits was tested since this step can reduce the consumption to one-fourth or more (The PVA consumption was reduced to 1-2 lb/t from 4-6 lb/t). For that reason statistical design with three factors, (i.e., conditioning time, PVA concentration, and pulp density) was used. It is indicated, from Figure 4-3, that the PVA concentration is the main factor and then the conditioning time while the pulp density (solid liquid ratio) has a very slightly effect on the % MgO in the concentrate and % MgO recovery in floated fraction. Cube GraphMgO recovery in floated fraction, % A: Conditioning time, minB: S/L ratioC: PVA Conc., %A-A+B-B+C-C+5.5046.835.1355.108.8820.509.3084.40Cube GraphMgO% in Concentrate A: Conditioning time, minB: S/L ratioC: PVA Conc., %A-A+B-B+C-C+2.91.852.91.62.821.12.80.7 Figure 4-3. Cube graph for MgO % and MgO recovery % Saturation Experiment The CaCO 3 was used to saturate the solution with calcium sulfate by adding CaCO 3 to 3 % sulfuric-acid solution. The formation of the precipitate of CaSO 4 indicated that the solution was saturated. It was found that 1.78gm/l of CaCO 3 would cause the precipitate to form. After the formation of the CaSO 4 precipitate, the flotation test was run as an indication of the acid performance after its saturation. Table 4-3 shows the results of these experiments before and after the saturation is reached.

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57 Table 4-3. Effect of saturated acid on the RF Before saturation After saturation Wt% MgO% P 2 O 5 % Wt% MgO% P 2 O 5 % Float Sink 22.1 77.9 11.1 00.8 04.2 21.1 21.3 78.7 10.95 00.85 4.15 21.2 Pilot Scale Testing: Sluice Results It was shown that the PVA consumption could be reduced to 1 lb/t on lab scale. Testing of the reactive flotation process using a simple sluice was conducted on pilot scale. Starting from the point that the formation of the bubbles on the dolomite surface creates a density difference between dolomite and phosphate particles. Therefore, the gravity separators are the promising techniques to do this separation. In that regard, two tests were run using the sluice under two different coating conditions. The first was spraying the particles with 3 % PVA solution before adding the particles to the sluice and the second was conditioning the particles in 1 % PVA solution and screening the particles to remove the excess PVA solution to reuse it (the PVA consumption is estimated to be 0.8 lb/t), then adding the particles to the sluice. The results of these two tests are given in Table 4-4. From these results, it can be seen that by applying the optimum conditions, the reactive flotation process can reduce the MgO % to less than 1 % with high recovery. In the rest of this work, the fundamental interpretations of what are observed experimentally were carried out. Table 4-4. Comparison of two different coating methods and their effects on MgO removal Coating Conditioning Sample Wt% MgO% P 2 O 5 % CaO% I.R% Wt% MgO% P 2 O 5 % CaO% I.R% Float Sink 20.74 79.26 12.3 00.65 02.9 22.3 32.82 38.33 09.8 11.22 20 80 12.41 00.68 02.85 21.90 33.55 37.93 10.01 11.14 Calc. Feed 100 03.06 18.27 37.19 10.97 100 03.03 18.09 37.05 10.93 Feed 100 3.04 18.13 37.45 11.05 100 3.04 18.13 37.45 11.05

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CHAPTER 5 FUNDAMENTAL STUDIES Polyvinyl alcohol-Particle Interaction Introduction Generally, adsorption of a polymer is utilized in many applications, such as: dispersion of particles, flotation, flocculation processes, treatment of surfaces, etc. If a solvent is a poor solvent (i.e., the interaction energy between the polymer segment and the solvent molecules is unfavorable when compared to polymer-polymer or solvent solvent molecular interaction energy), then the effective polymer surface interaction can be strongly attractive and the polymer will seek any opportunity to minimize the contact points with the solvent. Hence, in cases where a poor solvent is used, adsorption will increase on almost any surface, even the liquid-air interface. Adsorption is, therefore, always accentuated before precipitation will occur. The surfaces will act as a nucleation sites for polymer precipitation. This means, the poorer the solvent, the higher the adsorption and vice versa. In addition to the solvent quality, there are other factors that can affect the polymer adsorption and change its conformation, including: polymer molecular weight, polymer concentration, pH, and ionic strength. Previous studies of polymer adsorption suggest a number of qualitative trends that have been noticed in most polymer adsorption systems. The most important of them are as follows: many polymers adsorb on a variety of surfaces, Reach a plateau at few mg/m 2 a sharp isotherm sometimes is obtained, and molecular weight is a main factor, especially in a poor solvent. 58

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59 In this work, the polymer (PVA) is used as a membrane-forming agent to capture produced CO 2 gas on dolomite particles and makes them lighter than other particles leading to their flotation and separation from non-carbonate (apatite) particle. To understand this process and to elucidate the interaction mechanism between polyvinyl alcohol (PVA) and dolomite and apatite surfaces in the reactive flotation process, different techniques were used, such as: estimation of work of adhesion using surface tension and contact angle measurements, adsorption/desorption isotherms, Zeta potential, and surfaces characterization using Fourier Transform InfraRed (FTIR), etc.; the details of each one of these techniques are discussed in this chapter. The strength of adhesion to a solid surface can be estimated from the value of the thermodynamic work of adhesion or W a a concept first introduced by [Harkins, 1928]. In a simple system where a liquid L adheres to a solid S, Figure 5-1, the work of adhesion is defined as: slslaW .. (5.1) where s l and sl are the interfacial tensions of the solid/air, liquid/air and solid/liquid interfaces respectively. The problem with using Equation 5.1 is that, of the three interfacial tensions, only l can be measured with fluid phases, in this case the liquid and air. Those tensions involving the solid cannot be measured independently. Another approach, then, is to combine Equation 1 with the Young-Dupre equation (Equation 5.2), to provide a more useful expression for the work of adhesion [Adamson and Gast, 1997]: coslsls .. (5.2)

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60 where is the contact angle that the liquid makes with the solid surface. Provided that l and can be measured experimentally, it is then possible to use Equation 5.3 to calculate the work of adhesion. )cos1( laW ......(5.3) Therefore, the measurements of surface tension and contact angle are essential towards the calculation of the work of adhesion of the polymer (PVA) with solid surfaces, which will be discussed in the following sections. Figure 5-1. Contact angle and interfacial surface tension at solid/liquid/gas interface urface Tension The equilibrium surface tension values of fully hydrolyzed PVA solutions (average w =150000) as a function of the initial bulk concentration at room temperature (23 C) re shown in Figure 5-3. The surface tension of PVA decreases with increasing oncentration of PVA until it reaches a region where the surface tension (59 60 yne/cm) no longer decreases with increasing the polymer concentration. The critical oncentration at which the surface tension starts to be constant is 1 % PVA in aqueous solution. These results coincide with the literature concerning the surface tension of fully hydrolyzed polyvinyl alcohol (PVA). The fully hydrolyzed polymer has less effect on Gas l Solid Liquid s sl S M a c d c

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61 surface tension than partly hydrolyzed PVA [Fbiehn and Erusberger, 1951; Kim aLuckham, 1991]. The chemical structure of both is shown in Figure 5-2. nd Figure 5-2. Structural formula for PVA: A) partially hydrolyzed; B) fully hydrolyzedIt is reported that the surface tension reaches a constant level at 1-3 % PVA depending on the PVA molecular w These results are similar to several findings reported in the literature regarding polymer systems; the stabilization of the surface tension of high-Mw PEO (> 100000) solutions was associated with the saturation of the air/water interface by the polymer chains [Zeno eight and degree of hydrolysis [Finch 1973; 1992]. et al., 2004]. 5055 6065Surface Teion, dyne/cm 7075012345PVA Concentration, %ns Figure 5-3. Equilibrium Surface tension for aqueous PVA solutions at 23 C A B

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62 An explanation of this phenomenon is that the surface activity of a polymer mainly relies on its conformation in the aqueous solution, whereas the conformation of macromolecule depends on its chemical structure and composition, etc. At low concentrations, the chains of macromolecule are stretched in the water due to the formation of hydrogen bonding with water molecules. These long chains lying on the liquid/air interface can dramatically decrease the surface tension of water, even though the adsorbed amount on the liquid/air interface is very small. With the increase of concentration, the polymers molecules that adsorb on the surface increase and a tight hen the polymer clusters; ay also in Figure 5-4. PVA crystal structure; the dotted lines indicate hydrogen bonds. macromolecular film is formed, which makes the surface tension decrease. W ers occupy all the surface of solution, the adsorption reaches a level of saturation corresponding to the lowest value of surface tension. As this concentration furthincreases, the polymers in the solution begin to aggregate and form micelle-like at this point, the surface tension shows no more changes. In the case of PVA, it mbe related to degree of crystallinity due to formation of hydrogen bonding as indicatedFigure 5-4 [Finch 1973]. OH OHOH CHCH 2 CH OHCH 2 CH CH 2 CH OHOHOH OH CH 2

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63 It is expected that the surface tension will have higher values in the presence ofthe acidic media since th e SO4-2 ions increases the surface tension, affects the polymer lubility, and enhances the formation of polymer aggregates at even a slightly high acid oncentration [Sun, 1994]. ontact Angle The phenomenon of wetting or non-wetting tter nderstood by studying cct ae, which is the most universally applied method of quantifying wettability. Contact angle methods have been developed extensively over the past four decades. The contact angles of dolomite and apatite surfaces with PVA can be to the surface by hydrogen bond. As the PVA reases, more and more hydrogen bonds form; as a result of hydrogen bondslt in a modified PVA end groups [Finch 1992]. so c C of a solid by a liquid is be u onta ngl aqueous solutions at different concentrations are shown in Figure 5-5. From the figure, it seen that the contact angle increases with the increase of PVA concentration for both minerals surfaces. This phenomenon can be explained by the structure of PVA in the solution shown in Figure 5-4. When a droplet of PVA placed on the surface of dolomite or apatite, the PVA adsorbs concentration inc among its molecules, the PVA begins to form clusters. These clusters resulocal viscosity increase, which controls the droplet shape as well as its tendency to spread. This, in turn, increases the contact angle accordingly. The dynamic behavior of the molecules, their conformation at solid-liquid interface, and diffusion of macromolecules will affect the adsorption of more molecules, with a subsequent increase in contact angle. The increase in contact angle is proposed toresult from polymer cluster formation and preferential coverage of the hydrophilic sites by polymer molecules. This phenomenon is observed for PVA and also for some

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64 3040 1020012345Co PVA concentration, %ntact angle, degree Dolomite Apatite Figure 5-5. Static contact angle variation with the PVA concentration All measurements shown in Figure 55 were conducted immediately after application of the drop. Evaporation of water caused the drop to contract and a consequent change in the contact angle. Work of Adhesion Figure 5-6 shows the dependence of work of adhesion, Wa, on the PVA concentration. The work of adhesion decreases with increasing PVA concentration (increase in G, where Wa = G [Lloyd, 1994]). The increase in G reflects the formation of polymer clusters and increase of its crystallinity. This is due to the formation of OH-group bonds between PVA molecules causing them to favor adhesion to a solid surface. Additionally, the polymers diffusivity decreases with higher With increasing PVA concentration, the PVA molecules not only adsorb to the surface but also form hydrogen bonds among themselves. This behavior affects the concentrations.

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65 conforation on stage 1-3 %, at which constant surface tension and ieved. rmation of the molecules at the solid-liquid interface till they reach the satustage, when the work of adhesion becomes constant. It appears that this saturatiis the same region of PVA concentration contact angle are ach 80PVA concentration, %W 100120140orkf Adhesin, dyne/c2 160012345 oom Dolomite Apatitesence of hydrogen bonding hypothesis and to establish an adsorption mechanism additional studies were conducted and their results are discussed in the paragraphs that follow. Adsorption study: Research grade samples were purchased from Wards Natural Science and used to conduct the adsorption study. These samples were chemically analyzed by the wet chemical method and the results are listed in Table 5-1. Figure 5-6. Work of adhesion as a function of PVA concentration on dolomite and apatite substrates Additional Studies To substantiate the pre

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66 Table 5-1. Chemical analysis of the samples used in adsorption tests MgO% P2O5% CaO% Al2O3% Fe2O3% I.R.% L.O.I. % Dolomite 20.39 0.58 31.6 0.97 0.10 2.52 42.6 Apatite 31.73 49.50 2.64 1.04 4.95 5.0 Specific surface area measurements (BET method): The specific surface area of dolomite and apatite particles was determined by the BET in order to be used in adsorption isotherm calculations (applied in the next section). Using nitrogen as the adsorbate, the measured surface areas for dolomite and apatite were 0.9 and 1.48 m2/g respectively. Pore size distribution: The results of cumulative pore size distribution for apatite er umulative pore area, 9 m/g, than the dolomite, 1.8 m2/g. Mean pore sizes for apatite and dolom and dolomite are shown in Figures 5-7 and 5-8. It is clear that the apatite has a high2 c ite are 28 A and 42.5Arespectively. o o 02 468Cumulative pore area, m 10000re der, A2igure 5-7. Cumulative pore size distribution for apatite sample /g 20 40 600 800 1000 Po iamet F

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67 00. 402004006008001000 0.81.21.6Cumulative pore area, m2/g 2Pore diameter, A Figure 5-8. Cumulative pore size distribution for dolomite sample Zeta Potential In order to obtain a more detailed description of the adsorption and electrical properties of the solidsolution interface, measurements of the zeta potential were taken. The tendency of zeta potential to vary with nonionic polymer adsorption may be caused by one of two different factors: 1) the shift of the position of the shear plane, or 2) the blocking of the active sites on the surface by adsorbing polymer chains. The participation of these effects was estimated by the determining the difference in the values of the zeta potential with no polymer and with polymer present. The use of a KNO3 solution (3X10-3 M) acted as a control in these experiments. olomite in 3X10-3 KNO3 solution as function of pH are presented in Figure 5-9. It can be seen that the iso-electric points (IEP) of apatite and dolomite are about 6.8 and 9, respectively. This is in agreement with the results reported in the literature [Amankonah and Somasundaran, 1985; Chander and Furestenau, 1982; Pugh and Stenius, 1985]. The results of measuring the zeta potential of apatite and d

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68 -60-50-40-30-20-100102030405002468101214pHZeta Potential, mV Dolomite Apatite3X10-3M KNO3 Figure 5-9. Zeta potential of dolomite and apatite samples lts of measuring the zeta potential in the presence of a PVA solution. It is evi Zeta potential in the presence of PVA was determined as well. Figures 5-10 and 511 show the resu dent that the presence of PVA does not change the IEP of the apatite or dolomite. It does, however, cause compression in the electrical double layer. -40 -20-10020405060Zeta Potential, mV -30pH 103002468101214 Dolomite Dolomite + PVA 3X10-3M KNO3 Figure 5-10. Zeta potential of dolomite in absence and presence of polymer

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69 -50-40-30-20-1001020304002468101214pHZeta Potential, mV Apatite Apatite + PVA3X10-3M KNO3 Figure 5-11. Zeta potential of dolomite in absence and presence of polymer sible to potential determining ions ( VA is not due to a decrease in charge and surface potential, but rather to a shift of the shear plane (Figure 5-12). er on the shear plane position, A) without polymer, B) after polymer adsorption The results indicate that the surface sites remain acces H + and OH ) and the IEP remains unchanged during PVA adsorption, thus implyingthat the polymer does not alter the surface potential. It can be considered, as other investigators asserted [Ottewill, 1967; Mpandou and Siffert, 1984;1987; Luckham et al., 1983] that the decrease in zeta potential relating to adsorption of P Figure 5-12. Effect of polym Distance from surface Shear p lane Stern p lane Zeta Potential Surface Potential Shear p lane Stern p lane Distance from surface Zeta potential before adsorptionZeta potential after adsorption Ions counter ions Polymer chain A B

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70 In short, the changes of the zeta potential produced by the adsorption of substances with high molecular weight, result from blocking of the active sites on the minerals surface and as well as from the shift of the shear plane. Zeta potential of minerals in supernatant solutions In natural ores, the dolomite and apatite form a mixture. Their presence together may affect the adsorption of the polymer on both of the minerals surfaces. Therefore, the adsorption on the dolomite in presence of apatite supernatant and apatite in presence of dolomite supernatant were studied. The effect of the supernatant of dolomite on the zeta potential of apatite is shown in Figure 5-13. The results show that the apatite surface becomes more positive over the entire pH range and that the IEP has shifted from 6.8 to 8.6. Both effects are hypothesized to be due to the presence of calcium and magnesium ions in the solution. -50-40-30-20-10 50 0 10 20304002468101214pHZeta Potential, mV Apatite A p atite in Dolomite3 e and apatite in dolomite supernatant 3X10-3M KNO Figure 5-13. Zeta potential of apatit

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71 SP shifts from 9 to 6.5. imilarly, the zeta potential of dolomite in an apatite supernatant was measured as a function of pH. The results, given in Figure 5-14, show the zeta potential of dolomite to be reduced drastically in presence of apatite supernatant. The IE 50 -30-20040101214Zeta Potential, mV 3X10-3M KNO3 -1010203002468 -50-40pH Dolomite Dolomite in Apatite supernatant Figure 5-14. Zeta potential of dolomite and dolomite in apatite supernatant Zeta potential in the presence of PVA Moreover, the zeta potential of dolomite in apatite supernatant in presence of PVA was determined. The results in Figure 5-15 indicate that the PVA deals with surface of dolomite, when suspended in an apatite supernatant, as an apatite surface. This is due to the faster diffusion of small ions and molecules from the solution to the dolomite surface, which converts it to surface similar to apatite. As can be expected, the movement and diffusion of these ions is quite faster than that of polymer molecules. Consequently, The polymers role is applied after the surface changing and the adsorption of the polymer appears as if it is on apatite surface. The same argument mentioned in the previous paragraph can be applied in the caseof PVA present with apatite in a dolomite supernatant. The results of the zeta potential of this system are shown in Figure 5-16.

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72 -60-50-40-30-20-1001020 3040 3X10-3M KNO3 02468101214pHZeta Potential, mV Dolomite in apatite supernatant + PVA Dolomite in Apatite supernatant Figure 5-15. Zeta potential of dolomite in apatite supernatant before and after PVA adsorption 50 40 -40-30-200102002468101214pH -1030Zeta Potential, mV Apatite in Dolomite supernatant + PVA Apatite in Dolomite supernatantFigure 5-16. Zeta potential of apatite in dolomite supernatant before and after PVA adsorption 3X10-3M KNO3 Infrared (FTIR) The FTIR spectra of the powders, both with and without polymer adsorbed to them, previous studies [Kiselev and Rygin, 1972; were compared in order to obtain the mechanism of adsorption of PVA on dolomite and apatite surfaces. This method was applied in

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73 Paradip and Moudgil, 1991; Howard, and McConnel, 1967; Behl and Moudgil, 1993; Bjelopavlic et al., 2000; Zaman et al., 2002; Mathur and Moudgil, 1997; Moudgil and Prakash, 1998] to explain polymersolid interactions. The major peaks for dolomite and apatite are identified according to Ince et al. [1991] and Farmer [1974]. FTIR spectroscopic studies were carried out on the dolomite and apatite and polymer samples both before and after adsorption. The assignments of the various bands and peaks made in this study are in reasonable agreement with those reported in the literature for similar functional groups [Finch, 1973; Chanchani, 1986; Ince, 1987]. The FTIR spectrum of PVA is shown in Figure 5-17. A broad-band, is displayed at e sharp band at 2930 cm-1 is attributed to strong C-H stretching. The band at 2860 cm-1 is attributed to shoulder C-H stretching. The transmission band at 1650 cm-1 is due to the presence of moisture in the sample. The band at 1460 cm-1 can be attributed to OH and C-H bending. These results are in good agreement with the spectra of PVA reported by other workers [Finch, 1973; 1992]. 3450 cm-1 which may be attributed to hydrogen-bonded surface hydroxyl groups. Th 40080012001600200024002800320036004000Wave number, cm-11110594Figure 5-17. Infrared transmittance spectra (FTIR) of poly vinyl alcohol (PVA) 3450293016501460862 2860

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74 The FTIR spectrum of the bare-dolomite sample as well as those that had previously interacted with PVA is shown in Figure 5-18. The isolated hydroxyl group peak is present in dolomite powder without polymer, but the spectra with polymer shows the disappearance of this peak. Moreover, the peak intensity of the hydrogen-bonded hydroxyl groups is smaller in case of the powder with the polymer than without. These observations indicate that the adsorption of PVA on dolomite occurs by hydrogen bonding involving OH groups of the polymer. This finding is in concurrence with earlier studies on silica-PEO [Rubio and Kitchener, 1976; Cheng, 1985] and silica-Polyacrylic acid PAA [Tadros, 1978], which showed that the presence of isolated OHgroups on the surface is responsible for the adsorption of polymer molecules by hydrogen bonding. 40080012001600200024002800320036004000Wave number, cm-1 Dolomite + PVA Dolomite8831460 72818202550264029103030345036407288831460182025502640291030303450 Figure 5-18. Infrared absorbance spectra (FTIR) of A) dolomite alone, and B) dolomite/PVA system. A B

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75 The FTIR spectrum of the apatite sample after having interacted with PVA is shown in Figure 5-19. However, unlike the case of dolomite, this figure indicates that the adsorption mechanism of the polymer on apatite is not clarified by using FTIRno change is shown in the bands intensities or positions, either for bare apatite or apatite with polymer adsorbed on it. This finding is in agreement with the current literature [Chanchani, 1986; Ince, 1987]. It is pertinent to mention that FTIR spectroscopic studies on the dolomitePVA and apatite-PVA systems revealed the presence of hydrogen bonding only. 40080012001600200024002800320036004 000 Wave number, cm-1 Apatite Apatite + PVA866146016503450 Figure 5-19. Infrared absorbance spectra of A) apatite alone, and B) apatite/PVA system. Adsorption Study An adsorption study was used for the purpose of determining PVA adsorption on termined colometrically. Figure 5-20 shows the calibration curve and its equation, which was used in this study to calculate the residual concentration of PVA in adsorption experiments. 6071050 A B both dolomite and apatite. The calibration curve for PVA concentration was de

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76 The l imitation of the PVA concentration to create this curve is 40 ppm [Finch, 1973;1992]. y = 0.0036x + 0.0030.020.040.060.080.10.120.140.16Absorbance 001020304050PVA Concentration, ppm Figure 5-20. Calibration curve for PVA concentration measurements Kinetics of adsorption A study of the kinetics of adsorption is mainly to determine the equilibrium time of adsorption. The rate by which equilibrium is established during adsorption depends on the chee polymer and its molecular weight, the solvent, and the type of adsorbent. In most cases, the kinetic curves indicate an increase in the amount of adsorbed polymer over time, with an asymptotic approximation of the equilibrium value of a polymer on solid surfaces occurs by a three-step mechanism [Dijit. mical nature of th [Lipatov and Sergeeva, 1974] The adsorption et al., 1990; Somasundaran and Ramachandran, 1988]. First, the polymer is diffused from the bulk to the interface. Second, adsorption of the polymer molecules occurs on the initially bare solid surface. Finally, polymer conformation and orientation changes in the surface layer to accommodate the adsorption of more polymer molecules

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77 To ascertain the time required for the adsorption equilibrium to be attained, kinetests we tic re carried out at a natural pH of 7 for a period of 24 hours; PVA concentration was 100 ppm (6.7X10-7 M). Figure 5-21 shows results on the adsorption of PVA onto dolomite and apatite as a function of time. It is evident that the equilibrium is attained at about one hour. The equilibrium values are 0.04X10-6 and 0.011X10-6 mole/m2 for dolomite and apatite respectively. In consideration of these findings, a 2-hour conditioning time was selected for the adsorption studies. It was observed that the adsorption followed a typical second-order adsorption process. The second-order model predicts the behavior over the whole range of adsorption and is in agreement with an adsorption mechanism being the rate-controlling step. The second-order rate expression [Ozacar, 2003] based on solid capacity is generally expressed as follows: 2)( d eqkOr, by integration dt... (5.4). eqeqtk1..(5.5) Where is adsorption density (mole/m) and t22sorption rate constant (hr-1), and t is time (hr). By fitting the exe eq X 10 mole/mK, hr eq is equilibrium adsorption density (mole/m 2 ), K is second-order ad perimental data to Equation 5.5, the parameters eq and K were determined. Thesare listed in Table 5-2. Table 5-2. Fitting parameters of second-order kinetic model -62-1 Dolomite 0.04 361.6 Apatite 0.011 200

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78 It can be seen that the eq values for dolomite and apatite match the experimental values. The higher eq value of dolomite indicates the presence of more sites available fPVA adsorption than on apatite. Moreover, the K or ad for dolomite is higher than the K ad for apatite, which indicates the higher adsorption rate on dolomite. However, the plateau was reached almost at the same time for both minerals. 0.E+00 5.E-02 1.E-024.E-02PVA Adsortion density, 10-6mole/m 2.E-023.E-020152025Time, hr2 Dolomite Apatite Dolomite-2nd order model Apatite2nd order model 510 Figure 5-21. Kinomite and Apatite (Initial PVA conX10 -3 M KNO3 and 23C). Explanation of the higher adsorption rate on dolomite: The higher adsorption ll either be flat on the solid surfacegreater tendency for ttach to each other, (2) The neutrality of apatite (pH 7) while having an IEP of 6.8, whns less ions in the lution are available to act as additional driving force for PVA to adsorb on the apatite etics of PVA adsorption on dolcentration 6.7X10 -7 M, pH 7, 2 rate on dolomite may be explained by: (1) The higher solubility of dolomite and production of more ions in the solution, which affects the solutions property as a solvent(effectively converting it to poorer solvent). This property also affects the polymers conformation, which wi molecules of polymer to be adsorbed on the solid surface or a ich mea so

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79 surfacn ed with FTIR spectra measurement. Adsorption isotherm Most isotherms of the adsorption of polymers from dilute solutions can be visually represented as curves that reach saturation at specific concentrations [Lipatov and Sergeeva, 1974]. It is important to note that polymers may adsorb on surfaces in various conformations depending on bulk (solvent) and surface chemical properties of the substrate, as well as other physical conditions of the system [Hong et al., 2001]. At low concentrations, the polymer chain behaves like isolated coil. If the concentration of the polymer in the solution is raised, the chains become close to each influence the motion e point of chain-overlapping concentration, which is thill is e. This is especially significant as there is high competition between the interactioof PVA with water molecules and interaction of PVA with the apatite surface, and (3) OH-groups on dolomite surface (isolated and hydrogen-bonded hydroxyls) are greater than those on apatite surface (hydrogen-bonded hydroxyls). In other words, the isolated OH is exclusive to the dolomite surface, which is confirm other, which allows polymer-polymer intermolecular interactions to of the polymer chains. The effects may be expected to be cumulative until th e close packing of the polymer coils in solution. Once the overlapping concentration has been reached, the polymer motion wbe dominated by the presence of direct polymer-polymer interaction. As polymer concentration is increased, the polymer diffusivity decreases. If the concentration increases even further, a pseudo-matrix-gel will be formed. The resulting viscositygoverned mainly by intermolecular interaction, which is related to polymer chains overlap [Izmailova et al., 1975; Gotze and Sonntag, 1987; Andreyeva et al, 1973; Babayevskii et al., 1986; Koopal et al., 1988].

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80 For PVA, OH is the only functional group [Koopal and Lyklema, 1979; Chibowski and Paszkiewicz, 1995; Chibowski et al., 2000]. Increasing the degree of hydrolysis reduces acetate groups, which usually show preferential adsorption. Thus, thconformation of the polymer chain at the solidpolymer solution interface will depend onthe number of acetate groups in a PVA macromolecule. The lower the degree ofhydrolysis, the fl e atter the polymer chains; conversely, at high degree of hydrolysis, the be oriented perpendicularly to the surface [Santhiya et al., 1999; Sjbeon the with ental resultlly -6 ite d polymer chains should rg et al., 1999; Bajpai and Vishwakarma, 2003; Koopal and Lyklema, 1979]. This conformation of the PVA macromolecule will favor the adsorption of the polymer surfaces of dolomite and apatite, which is shown in Figures 5-22 and 5-23. Chibowski [2000] reported that the adsorption of PVA on alumina increases an increase in the degree of hydrolysis. This is also confirmed by previous experim s and polymer screening experiments. In this work, it was found that the fuhydrolysed PVA was the best among different degrees of hydrolysis PVAs (Chapter 3 in this thesis). The adsorption density (mol/m2) of fully hydrolyzed PVA (acetate groups < 1 %) on the minerals surface as a function of the initial polymer concentration (0 to 4X10mole) was determined at 23 Celsius and a pH 7 for dolomite and apatite. The results obtained are presented in an adsorption isotherm plot (Figures 5-22 and 5-23 for dolomand apatite, respectively). The analysis of these adsorption isotherms shows formation of a plateau for both apatite and dolomite. Such behavior of the macromolecules comes from a different adsorption affinity towards different surfaces. This result suggests that the observe

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81 increahe s his, in r dsorption isothe se in PVA adsorption is mainly caused by the change in conformation of tpolymer chain at the minerals surface. Following this change, a number of active siteon the surface become available for further adsorption of polymer molecules. As mentioned previously, the greater porosity of apatite leads to high number of adsorption sites available and the horizontal stretching of the polymer to cover these sites. Tturn, explains the lower adsorption layer thickness and higher parking area of apatite. The shape of the adsorption isotherms shown in Figures 5-22 and 5-23 is typical fophysical adsorption and is an acceptable shape for that range of polymer molecular weight. [Adamson and Gast, 1997]. The measurements were repeated three times and error bars were plotted on each graph. From the figures we can see that the a rm is S-shaped, which suggests a physical adsorption of PVA onto the dolomite andapatite surfaces. 0.00.51.0Equilibrium PVA conc., 10-7 moleAdsotion nsity,Figure 5-22. Adsorption iso 1.52.00.00.40.81.21.62.0rpde X 10-7 mo2 therm of PVA on dolomite at 23C 2.5le/mDolomite

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82 0.0Equilibrium PVA Conc., 10-7moleFigure 5-23. Adsorption isotherm of PVA on apatite at 23C Calculation of PVA adsorption and parking area The amount of PVA adsorption was calculated using the following formula: 0.51.52.0Adsorption density, 10 mole/m2 1.00.00.40.81.21.62.0-7Apatite SA* m V*) C-(Ci r (5.6) Where, is the amount of PVA adsorption (mole/m2), (Ci-Cr) is PVA concentration on the particle (mole/ml), Ci is initial PVA concentration, Cr is residual PVA concentration, V is the volume of solution (ml), m is the mass of dolomite or apatite particles (g), and SA is the specific surface area of particles (dolomite 0.9 and apatite 1.48 m2/g). The parking area of PVA molecules was calculated using the following formula: Parking area = Av 10118Mw Where MW = 150,000 g/mole, Av is Avogadros number (6.023 x 1023 #/mol) and parking area is nm2/#. The calculated parking areas for dolomite and apatite at the first plateau are (23.72 nm2) and (75.47 nm2) respectively. Taking into account that the (5.7)

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83 Dolomite / Apatite Dolomite / Apatite Dolomite / Apatite Dolomite / Apatite Dolomite / Apatite Dolomite / Apatite A B parking area per stretched molecule is 0.2 nm2 [Koopal and Lyklema, 1979], it was observed that PVA-molecule forms a wavy or zigzag shape on the solid particles with the higher thickness on the dolomite particles. Moreover, this conformation on dolomite appears at lower relative concentration range. It is worth noting that in the case of dolomite the adsorption isotherm is both steeper and reaches a plateau at lower concentrations than in case of apatite. The observed results may be explained based on the following hypothesis, which is Schematically illustrated in Figure 5-24: macromolecules are generally more tightly e figure shows the r several chains (5-24B). It may be conclfavorable and with inter Figure 5-24. Polymer-conformation changes with increase the concentration: A) molecule. bound to surfaces due to the multiple points of attachment. Th conformation of single polymer chain (5-24A) and/ o uded that without intermolecular H-bonds, spiral conformations of PVA are molecular H-bonds, zigzag conformations is expected. conformation of a single molecule, B) conformation of more than one

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84 Adsorbed layer thickness The thickness of PVA layer adsorbed on dolomite and/or apatite can be calculated from the adsorption isotherm by using the following relationship: h2 (5.8) Where, h is the adsorbed layer thickness, m; is adsorption density, g/m, and is PVA density, g/m3. Using this relationship, the thickness of the adsorbed layer was found to be 27 nm on dolomite and 9 nm on apatite, which indicates that the vertical polymer chains are stretched three times longer in the case of the dolomite than in the case of the apatite. This explains the greater adsorption on dolomite; since, according to their conformation, the polymer chains occupy smaller number of sites. In addition, more sites are available on dolomite than on apatite. Note: The length of the PVA molecule of this molecular weight is about 600 nm, hich indicates that the polymer conformation would be like Figure 24B. EffIonic sites at the surface generally control the surface charges, on salt-type minerals such as apatite and dolomite. Specifically, for dolomite are: Mg++, Ca++, CO3--, HCO3-, OH-++, Mg(OH)2, CaHCO++2 and for apatite are: a++, HPO4--, CaOH+, Ca(OH)2, H2PO4-, CaH2PO4+. The nature of the mineral surface, adsorption behavior. Previous studies on different minerals (i.e., alumina, silica, kaolin, clays) showed that the OH group of PVA is mainly responsible for adsorption on the w ects of pH MgHCO 3 MgOH 3 CaOH, Ca(OH) C pH, the presence of solutes, and the functional group of the polymer all affect the

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85 surface of a mineral [Santhiy a et al., 1999; Sjberg et al., 1999; Bajpai and Vishwakarma, 2003]studied range of 2 to 12. The effect of pH on the adsorption of PVA onto dolomite and apatite is shown in Figure 5-25. It can be seen that adsorption is pH-dependent in the 0.0E+001.0E-022.0E-023.0E-024.0E-02135791113Adsorption density, 10 5.0E-026.0E-02 mole/m pH-62 Apatite Dolomite Figure 5-25. Effect of pH on adsoStudying the adsorption of PVA on both minerals gives evidence that, due to fluctuations in pH, the adsorption is due to formation of hydrogen bonding between the tite surface from one side and OHpolymer functional group from anoth It is or rption of PVA on apatite and dolomite dolomite or apa er side. Effects of pH on Apatite: It is evident from Figure 5-25 that the adsorption density decreases with an increase of pH. The decrease in the adsorption density as a function of pH may be explained by taking into consideration the surface charge of the apatite particles as well as the surface species, both of which are dependent on pH.interesting to note that the decrease of CaH 2 PO 4 + and H 2 PO 4 species, according to the apatite activity chart [Attia and Fuerstenau, 1989] in entire pH range, are responsible f

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86 formation of hydrogen bonding. In addition, there is a presence of about 5 % silica in this sample, which also leads to decrease in adsorption with increasing pH. Moreover, it has been reported, as in the case of silica, that adsorption behaves thesame way as pH due to a reduction in the number of undissociated silanol groups [Rachas et al., 2000]. On the other hand, the reaction of Ca+2 or Mg+2 ions with four OH groups occurs at pH > 7 and is accompanied by compacting of the macromolecules. The degree of crystallization of the film sharply decreased (evidently because of water) after formation of a calcium or magnesium complex. ption ding capacity. It was noticed that the increase of OHspecies and formathis CH2 CH2 H2C O H O H OH2OH2 M Where M is Ca +2 or Mg +2 ions Effects of pH on dolomite: It can also be seen in Figure 5-25, that the adsordensity of dolomite increases with an increase of pH. This increase of adsorption with pH can be attributed to the hydroxylation of dolomites surface, which enhances itshydrogen-bon tion of metal (Ca and Mg) hydroxides with increasing pH are responsible for increase in adsorption. Additionally, it has been reported in some cases that, at acidic pH, the decrease in PVA adsorption, can be caused by some or all of the following factors: loss of the most active binding sites for PVA bonding, reduction of the affinity for nonionic compounds by a salting-out effect, the screening effect of hydrated counterions, or preferential adsorption of water molecules at those ionized sites [Barker and

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87 Garvey, 1980; Bonekamp et al., 1989; Platonov et al., 1979; Zhang et al, 1996; Hidber al., 1995; Santhiya et al, 1998]. The adsorption of PVA on both minerals giv et es evidence that th supernatants ensity lymer aggregation. The increase in dolomite, on e other hand, is due to the presence of more sites, as mentioned previously. After aching certain concentrations, both a curve become parallel, which means the same mount of the polymer has adsorbed on both surfaces. e adsorption is due to formation of hydrogen bonding between the dolomite or apatite surface from one side and OHpolymer functional group from another side. Adsorption in The results of adsorption of PVA on apatite in dolomite supernatant solution and dolomite in apatite supernatant solution are given in Figure 5-26. The adsorption dis lower than when the medium was just water, possibly due to the presence of several ionic species, which may affect the po th re a 01 5 23400.050.10.150.20.25-6Adsorption density, 109 mole Equilibrium PVA Conc., 10 moleApatite in dolomite supernatant Dolomite in apatite supernatant Figure 5-26. Adsorption isotherm of apatite in dolomite supernatant solution, and dolomite in apatite supernatant solution This can be attributed to adsorption of the newly introduced polymer to the polymer already adsorbed to the surface and the ensuing formation of an aggregate at 3*10-3 M KNO 3 the solid/liquid interface.

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88 Desorption To ascertain whether the adsorption process is reversible, desorption tests were carried out by interacting the sample containing the adsorbed polymer with distilled wfor a specified period and analyzing the supernatant solution for residual polymer ater in Figures 5-27 and 5-28. From Figures 5-27 and 5-28 it is evif content. The results are shown dent that, in the case of PVA, desorption characteristics follow a trend in reverse othe adsorption behavior. However, only about 20 % of the polymer could be desorbed, confirming the relatively weaker nature of this particular interaction with dolomite and apatite. 00.040.08 0.12-6/m 0.1600.050.10.150.2Equilibrium PVA Conc., 10-6 molePVA adsorption density, 10 mole2 Adsorption Desorption Figure 5-27. Desorption of PVA from apatite surface

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89 00.05 0.10.150.25A Asorpion dnsit 10-6 molem2 0.200.050.10.150.2Equilibrium PVA Conc., 10-6 molePVdtey,/ Adsorption Desorption Figure 5-28. Desorption of PVA from dolomite surface Desorption in Acidic Solution Since the RF process requires adding PVA coated particles to an acidic media, desorption of PVA in an acidic solution was studied to simulate the RF process. Desorption tests show almost no desorption in both the cases of dolomite and apatite. This behavior confirms that the formation of polymer cluster at the particle/ solution interface is due to the presence of SO4-2 ions, which is one of the most ionic species leading to cross-linking of the polymer chains [Finch, 1992; Garba et al., 1996]. Consequently, this increases the viscosity of the polymer-coated layer in addition to strengthening the adhesion forces among polymer molecules thus affecting its viscoelastic properties, its hydrodynamic volume, and its stretching when CO2 gas is produced as a result of the acid-carbonate reaction. Moreover, it is mentioned in the literature that even H2SO4, a strong acid, does not lead to salting out of the PVA; rather, its effect is extremely weak [Finch 1973; 1992].

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90 Bubble Formation and Stability The reactive flotation (RF) process, as mentioned earlier, includes two main steps: (1) the coating step, which is discussed in detail in the previous chapter and (2) the reaction step. In the second step, the sulfuric acid penetrates the polyvinyl alcohol (PVA) membrane and reacts with the dolomite surface. CO2 gas is one of the reaction products according to the following reaction: Ca Mg (CO3)2 +2H2SO4 CaSO4+MgSO4 +2CO2+2H2OBecause PVA is known for its very low permeability by gases (Finch, 1992), especially CO2, the CO2 will accumulate between the particle and membrane creating a density difference between the dolomite and phosphate rocks (i.e., lowering the dolomite tration of the mechanism of bubble formation during the reof the acid f ts to predict the membrane elasticity at particle density). A schematic illus action and how the particle density changes is given in Figure 5-29. Figure 5-29. The bubble formation mechanism To predict the required amount of CO 2 to float the particle, the modeling reaction with the dolomite surface and bubble formation was essential. In this chapter,different modeling efforts are discussed and the CO 2 production rate and the amount oCO 2 required to float the particle are calculated. Furthermore, the results are correlated with dynamic surface tension (DST) measuremen Acid diffusion Acid diffusion CO2 Dolomite Dolomite Dolomite CO 2BubbleCO2 Dolomite Dolomite Dolomite CO 2BubbleCO2 Dolomite Dolomite Dolomite CO 2Bubble

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91 a certain CO2 flowrate. Figu of the requirements to achie re 5-30 shows a schematic diagram ve flotation by RF process. CO2 re quired to float the particle Dolomite particle density changes Membrane elasticity CO2 production rate Dissolved Species (Ca and/or Mg) Dolomite-Acid reaction Figure 5-30. Schematic diagram of reaction kinetics of the RF Chemical Analysis of Samples Used in Kinetic Study: The experiments were carried out with two particle sizes (0.2 0.3, and 1-2 mm). The chemical analyses of these two fractions are given in Table 5-3. able 5-3. Chemical analysis of the samples used in kinetic tests Size, mm MgO% P2O5% CaO% Al2O3% Fe2O3% I.R.% L.O.I. % T -2+1 14.48 2.8232.61.021.5611.2 32.12 -0.3+0.2 15.36 2.45 31.47 34.37 0.99 1.34 10.95 It can be seen from the Table 5-3 that the analysis of the two samples are approximately the same. It is expected that the very small differences, as shown in the tic tests results. Effec. analysis, will have a negligible effect on the kine t of Particle Size Different particle sizes were tested in 3 % sulfuric acid, H 2 SO 4 solution (0.33 M)The results of reacting uncoated particles with acid at room temperature (23 1C), are shown in Figures 5-31 and 5-32 in terms of Ca and Mg dissolved, respectively. In all of the experiments, the solid loading in the reactor was 10 %.

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92 In the course of each dissolution process, concentrations of both the calcium and magnesium ions were determined as a function of time following the reaction between the dolomite and the sulfuric acid. The dissolution process of dolomite in aqueous sulfuric acid was found to depend on the solution acidity, as indicated in statistical design study (Chapter 4). It was also indicated in the literature that the reaction of calcite with sulfuric acid follows first-order kinetics and it depends only on acid concentration at pH< 5 [Booth et al, 1997]. Generally, calcium and magnesium ion concentration in the liquid phase first nderwent an exponential increase and then slowly approached an asymptotic value. rapidly due to the higher surface area available for H ions after which the dissolution reached a plateau ace area and did not reach equilibrium even u For the small particles, 0.2-0.3 mm, the reaction began very +(equilibrium) after 30 minutes. In the case of large particles, 1-2 mm, the reaction increased gradually as a result of lower surf after 2 hours. 00.0050.01 0.025 0.0150.02Ca dissolved, M Large particles 1-2 mm 020406080100120140Time, min Small particles 0.2-0.3 mm % sulfuric acid solution at 23C. Figure 5-31. Dissolution kinetic of different particle sizes in terms of calcium ions in 3

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93 00.0050.01 0.015Dissolved Mg, M 0.020.025020406080100120140Time, min Small particle (0.2-0.3 mm) Large particle (1-2 mm) Figurns in 3 % sulfuric acid solution at 23C. Formation of an insulating layer: The H+ transport is perturbed by the presence of the reaction products and since the H+ has a higher diffusivity, the reaction continued until it reached the point of equilibrium. At this point, the H+ can no longer reach the surface due to the formation of an insulating layer of reaction products, most probably gypsum, CaSO.2HO and/or a CO2 gas layer around the particle. This was especially true in the case of coated particles. To confirm the formation of a passivation layer of gypsum, a picture of a particle both before and after the reaction was taken (Figure 5-33). The variation of the particle color from yellowish to white is an indication of the formation of the gypsum layer at the surface of the particle. Figure 5-33. Dolomite particle (1-2 mm) before and after the reaction with 3 % H2SO4 e 5-32. Dissolution kinetic of different particle sizes in terms of magnesium io 4 2 After reaction Before reaction

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94 In the rest of this chapter, the Mg concentration will be taken as the dissolution kinetic indicator since both the calcium and magnesium follow the same trend. Effect of PVA Coating The reaction was tested with the particles having been coated with PVA. Figure 5-34 shows the results of both coated and uncoated particles. The curve is steeper in the case of uncoated particles and the curves for both coated and uncoated reach a plateau after 30 and 40 minutes respectively (Figure 5-34). This can be explained by the and then to the bulk solution. In addition, formation of the products occurs in a confined place (between the membrane and the particle surface), which also leads to a decrease in the saturation point and helps in rapid nucleation and growth of hydrated calcium sulfate, 22423ion of CO2 works as a diffusion barrier as well. presence of a polymer, which controls the transfer of ions to and from the boundary layer gypsum, (CaSO.2HO). Such a possibility exists in the case of a calcite-sulfuric acid system, providing that the solubility products are 2.5 x10-5 M2 for (CaSO.2HO) [Culberson et al., 1978] and 4.8 x 10-9 M2 for (CaCO) [Stark and Wallace, 1982]. Moreover, the accumulat 00.0050.01 0.0150.020.025 080100120140Time, minMg Dissolved, M uncoated coated 204060 igure 5-34. Dissolution kinetics of coated and uncoated 0.2-0.3 mm dolomite particle in F 3 % sulfuric acid solution at 23C.

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95 Bubble formation and growth: Figure 5-35 (a-e) shows the growth of bubbleon the dolomite particle surface with time. The reaction starts immediately after s adding solution. The bubbles then grow as a result of the evolution of CO2, id the particles to the acidic the impermeability of the PVA membrane, and the stretching of that membrane. If this membrane is not flexible enough, it will rupture and CO 2 gas will be released, leaving the particle without causing any flotation. It is also interesting to notice the rapgrowth of bubbles within a few seconds. 2s 5s 10s 15s 20s Figure 5-35. Growth of the bubbles with time on the dolomite particle surface, 50 X

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96 A echanism(s) controlling the dissolution process. The two mechanismge of acid and b) depletion of the active sites. Moreo empirical models are given fitted to experimental data. Those empirical models depend on reaching the saturation concentration in the bulk solution and the depletion of acid as the reaction products are formed. The main purpose of these models is to predict the amount of CO2 evolved and the consequent density changes of the dolomite particles, which leads to its separation. The details of each model are explained in the following paragraphs. Blockage of the Acid Model In this model, the reaction depends on the transfer of the acid to the particle surface; the products of the reaction then diffuse out to the bulk solution. The formation of the reaction products, (i.e., Ca-sulfate and/or CO2 gas), prevents the acids accessibility to the surface and stops the reaction. For simplicity of calculations, the sphericity of the particle, homogeneity of the coating around the particle, and presence of a barrier to CO2 gas transfer are assumed. lso, Figure 5-35 illustrates that presence of certain sites that can be considered asactive sites for reaction to form CO 2 bubbles. In other words, if the entire surface is reacting, the polymer will form a uniform and homogeneous membrane around the particle. Modeling of Bubble Formation and Dolomite-Particle Separation In the present study, two models were developed to explain the phenomena associated with the RF process. These models depend on the m s studied are a) blocka over, tw and The equations of this model are: )(momimairmiCCAKACKdt dC (5.9)

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97 airaiACKdt)(aiaoaCCAK dC (5.10) )(momimmoCCAK dtdC (5.11) aiAC (5.12) mdtdK aiaACdt (5.13) Where: C dKCmo : concentration of Mg in the bulk, M -2-1Ka : transfer coefficient, cm.min mi : concentration of Mg at the surface, M C ai : concentration of acid at the surface, M A : surface area, cm 2 K r : reaction rate coefficient, cm.min-2-1K m : transfer coefficient, cm -2 .min -1 and : coefficients, M -1 cm -4 min -2 : ratio between the boundary layer volume and total solution volume (Vi/Vo)37 for Large Small Fitting of this model to the experimental data is given in Figures 5-36 and 5-both size fractions. The fitting parameters are given in Table 5-4. Table 5-4. Acid-blockage model parameters Uncoated Coated Uncoated Coated *P-1 3 3 8.99 8.99 0.37 0.46 8.3 8.32 *10.1 3.29 9.27 9.26 0.67 0.67 9 9 0.00038 0.00085 0.0012 0.002 K m 5.97 5.97 10.04 K a 3.29 P-1 = Kr A Km= Km A Ka= Ka A

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98 0 0.0050.010.0150.020.02580100120140160Time, minMg Dissolved, M 0204060 Data-uncoated Model-uncoated Model-coated Data-coated1-2 mm experimental data Figure 5-36. Acid blockage model fitting to 00.005 0.025 0.02 0.015 0.01 001140Time, minMg Dissolved, M Data-uncoated Model-uncoat ed Model-coated 2040 6 80 00120 160 Data-coated ure 5-37. Acid model fi.25-0.35 rimental This model shows no difference in all its factors between coated and uncoated particlee can be explained by the swelling of the membrane due to the formation of CO2 gas, which Fig block age tting to 0 mm e xpe data s except which increases in the case of coated particles. The increas

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99 increases the internal boundary layer volume at constant external volume. The increase in P-1 for small particles is due to the increase in the number of sites that the acid can react with. Disappearance of Active Sites Model In this model, the reaction depends on the availability of the active sites at the particle surface. The depletion and disappearance of these sites will lead to cessation of the reaction. The disappearance of active sites may be due to formation of a passive layer from the reaction products, (i.e., Ca-sulfate and/or CO2 gas). In this way the acid is available to react, but there are no active sites to react with. arrier, constancy of acid concentration, homogeneity of the coating around the particle, and presence of a barrier to CO2 gas transfer are assumed. For simplicity of calculations, the sphericity of the particle, absence of an acid b )(mimomaormiCCAKACKdtdC (5.14) )(momimmoCCAKdtdC (5.15) aorACKdtdA (5.16) Where: Cmi : concentration of Mg at the surface, M Cao : concentration of acid in the bulk, M (assuming Ci=Co) A : surface area, cm2 concentration of Mg at the surface, M Km : t-2-1Kr : reaction rate coefficient, cm.min C mo : concentration in the bulk, M ransfer coefficient, cm.min-2-1 : ratio of volume of boundary layer to the volume of the bulk (Vi/Vo)

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100 Fitting of this model to the experimental data is given in Figures 5-38 and 5-39 for both size fractions. The fitting parameters are given in Table 5-5. 00.0050.01020406080100120Mg Dissolved, M 0.0150.020.025140160 Data-uncoa ted Model-uncoated Model-coat Time, min ed Data-coatedFigure 5-38. Active sites disappearance model fitting to 1-2 mm data 00.0050.010.0150.02 0.025 020406080100120140160Time, minMg Dissolved, M Data-uncoated Model-uncoated Model-coated Data-coated l fitting to 0.25-0.35 mm data Figure 5-39. Active sites disappearance mode Table 5-5. Active sites disappearance parameters Large Small Uncoated Coated Uncoated Coated 3 8.99 8.99 P-1 3 0.00038 0.00085 0.0012 0.002 7 10.04 10.1 9.26 K m 5.97 5.9 Acini 3.29 3.29 9.27 P-1 = KA K= KA rmm

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101 This model shows no difference in P-1, K m and K a between coated and uncoated particles. The only difference is in the value of which increases in the case of coated particles. The reason behind this increase is the constant external volume and increase of the internal volume since the polymer does not permeate the CO2. The increase in P-1 in for small particles is due to the increase in the number of sites that acid can react with. Empirical Models There are many models that can fit empirically to experimental data. The Two models chosen to fit the experimental data in this study were widely used in the literature for calcite dissolution [Sjoberg and Rickard, 1984; Sjoberg, 1978; Lund et al., 1973]. ndent model. However, these models do not reflect the physics associated with RF process First-order kinetic model For the phase of the study involving treatment with Sulfuric acid, a kinetic model [Cameselle et al., 1997; Froment and Bischo, 1979; Blancarte et al., 1987] was employed, the equation of which would be: These models are the First Order kinetic and Acid Concentration Depe )(CCeqkdtdc (5.17) Where: C : dissolved Mg concentration, M ; : treatment timBy integrating Equation 5.17, the value of the kinetic constant can be deduced: q (5.1 k : kinetic coefficient, min -1 ; C eq : Equilibrium concentration M t e, min. )1(kte CeC 8)

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102 Figures 5-40 and 5-41 show the fitting to this model to the results from experimenwith 3 % (0.33 M) sulfuric acid for two different particle sizes. The reaction rate constants are given in Table 5-6. The reaction rate constant, K, is 2.5X10 ts m reaching the surface and/or covering the active sites. -2 min -1 The variation in the equilibrium concentration at which the curves are leveling off is the presence of CO 2 as well as the development of a gypsum passivation layer, which prevents the acid fro 0 0.020.03 dissold, M 0.01M 020406080100120140 Time, mingve model coated data coated data uncoated model uncoatedFigure 5-40. First-order model fit ting for data of 0.25-0.35 mm particle size 0.0050.020.02 5 0 0.01g diss 0.015olved, M M 020406080100120140Time, min data uncoated model uncoated model coated data coated igure 5-41. First-order model fitting for data of 1-2 mm particle size F

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103 Table K Ceq 5-6. Reaction rate constants of first-order model Large particles Uncoated 0.025 0.02 (1-2 mm) Coated 0.0115 Small particles Uncoated 0.25 0.02 (0.25-0.35 mm) Coated 0.0115 Acid concentration dependence model Chemical reaction rate equations are used to define a conversion of the material or change in concentration due to dissolution and involve both a rate constant and a reaction order. However, a third parameter is also included in this model based on fact that the reaction product forms a barrier to acid diffusion. The circumstances under which this barrier is created are as follows: First, the acid concentration decreases with time as an evolution of reaction products. The reaction products then form a barrier between the acid and the particle surface. The thickness of this barrier increases with time until it reaches a certain stage where no acid can diffuse through and/ or the saturation stage is reached. Compton [1989] found that under very acidic (pH < 4) conditions, dissolution control passed from H+ diffusion control to a first-order heterogeneous reaction of H+ at the surface. This model can be presented by the following equation mAKCd t dc .(5.19) But the acid concentration changes with increasing the product concentrations according to the following relationship: (5.20) al form, which is: iAoAnCCC By plugging Equation 5.19 into Equation 5.20, we arrive at a differenti

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104 mnCCKdc)( iAdt5.21) By integrating.21, the ression will b .( Equation 5 final exp e: n CKtmmA1)1( nCCAi1][Wher m(5.22) 1 e, C A : acid concentration, M C AO : initial acid concentration, M C i : ions concentration, M n : number of ions evolved as reaction products K : reaction rate constant, min -1 t : time, min m: reaction order Figures 5-42 and 5-43 show the fitting of this model to experimental data. Its parameters are listed in Table 5-7. 00.01 0.03 0.02ed, M 0204060801001201 40Time, minMg dissolv model coated data coat ed data uncoated model uncoated Figur e 5-42. Model fitting for data of 0.25-0.35 mm particle size

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105 0 0.0050.010.0150.02508Time, minMg dissolved, 0.02 M 020406 0100120140 data uncoated model uncoated model coated data coated p Figure 5-43. Model fitting for data of 1-2 mm article size Table 5-7. Acid concentration dependence parameters Size, mm K n m 1-2 Coated Uncoated 1.65X10-21.65X10-211.9 11.9 3.97 2.85 0.25-0.35 Coated Uncoated 1.65X10-21.65X10-229.0 16.7 1.79 1.68 The reaction rate constant, K, is 1.65X10-2 min-1. For the small particles, the number of ions, n, in the case of coated particles is higher than uncoated because of a lesser volume around each particle in the presence of the polymer. This is not the situation in the case of the large particlesbecause of the lower surface area, the generation of ions is less and there is no competition among ions to diffuse out. Therefore, the n is the same, 11.9, in both cases. The order of the reaction, m, is primarily used to express the availability of acid. he acid, wile for oated particles, the polymer causes the formation of a barrier and limits both the accessibility of acid as well as the outgoing transfer of reaction products. Consequently, a higher m is needed to keep the reaction going at a constant rate. For uncoated particles m is smaller because there is no barrier for t h c

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106 Estimation of CO2 Required to Float the Dolomite Particle Simple calculations were used to predict the size of the particle with its surrounding envelope of gas and to estimate the relation between the radius of the particle before and after the formation of the gas bubbles around the particles. For simplicity, the following conditions were assumed: spherical particle, uniform gas layer around the particle, and at equilibrium condition: The part of the particle dissolved in the reaction was also neglected in the calculations. s to float when the density of nsity of acidic solution. The w As a starting point, we assumed that the particle start the particle and the gas layer around it is less than the de calcu lations are as follo s: Coating a g ent CO2 g asDolomite p article r rM 1Where: M : mass of CO gas Vd : volume of particle Vw : volume of water R1 : total radius (particle + gas) e area of the d : mass of dolomite particle g2M w : mass of water V g : volume of CO 2 gas R: particle radius S d : surfac p article r 1.4 r3434 2.9)r-(r34 r34 r 34 2.9VV MVVV1133133333wgd r )r 2.9(r r 0) (M gm/cm M M(solution) (acidicdensity Omide1gddg3 1w ) M gd gas) 2 Cte (Dolonsity

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107 In addition, the ratio between gas volume and particle vol ume and the ratio between the ga From the previous calculations, we can deduce that: The total radius is 140 % of the original radius of the particle (without taking the dissolved part of the particle and the pores volume into account). Also, the volume of gas around the particle is approximately twice the original particle radius. A larger particle needs more volume of gas to float due to its lower surface area. Change in Density: The density change can be calculated according to the sequence in Figure 5-44. The model will be used to calculate the number of moles of Mg, ntly will give the number of moles of CO2 through the equation of hemical reaction. Using thety, the volume olumgenated in certain pee can then beerage owr ofO2 as it evolvee used to calculate the change in the ensity awell as to correlate that change to membranelow rates. s volume and particle surface area were calculated as follows: which conseque c CO 2 densi e of CO ga 2 s can be calculated. Th v e ate er C riod of tim used to calculate the av fl s. This flowrate can b d s elasticity at different f rr58.0)1((1.4) V3rS3V3g2d1g rrareasurfaceparticlevolumeGas)r((1.4) Vr4)(r4 S:333g233d 3Sd dg31.75V V75.11(1.4) dgg1g VV]r[(1.4)V3Vr 3333d1333dr V1.4r rr34)(r4 V:andrvolumeparticlevolumeGas

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108 igure 5-44. Sequence of calculating the particle density and membrane elasticity Figure 5-45 shows the change in dolomite particle density as a function of reaction time. It is very rapid due to the CO2 build up in the RF process. The density of the dolomite particles changes rapidly due to intense reaction in the first 20-30 seconds; after that the rate of change decreases dramatically (Figure 5-45). The change is sharper in the case of the smaller particles due to their higher surface area and greater amount of CO2 generated. The density can be calculated by: ure 5-44. Sequence of calculating the particle density and membrane elasticity Figure 5-45 shows the change in dolomite particle density as a function of reaction time. It is very rapid due to the CO2 build up in the RF process. The density of the dolomite particles changes rapidly due to intense reaction in the first 20-30 seconds; after that the rate of change decreases dramatically (Figure 5-45). The change is sharper in the case of the smaller particles due to their higher surface area and greater amount of CO2 generated. The density can be calculated by: Model Mg Moles CO2 Moles Density CO2 flowrate DST Elasticity F gp ppfVV V (5.23) Where: : floated particle density, g/cm fp 3 p : particle density, g/cm 3 V: particle volume, cm3, and V g : gas volume, cm 3

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109 0.01.02.03.0051015Time, minDensity, gm/cm3 0.2-03 mm 1-2 mm 2-5 mm 5-9 mm Figure 5-45. Density changes for different particle sizes Bubbles Stability As the reaction transpires at the dolomite particle surface, the CO2 gas produced affects the growing bubbles in terms of their stability, (i.e., the stretching and elasticity of the polymer due to gas-pressure on the adsorbed polymer layer). Presence of the surfactant or polymer adsorbed at either the gasliquid or liquidliquid interface leads to the viscoelastic properties of that interface. They may be characterized by a surface dilatational modulus, which is defineaccorg to Gibbss equation [Johnson and Stebe, nkenheimer et al., 1996; Pikhitsa and Tsargorodskaya, 2000]: d din 1 996; Lu AdE dln (5.24)ic surface tension (DST), and A is the geometric area of the surface. For that reason, the Dynamic Surface Tension (DST) measurements using the Maximum Bubble Pressure Technique were determined at different gas flow rates: 0.23, Where is the dynam

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110 0.47, 0.78, and 1.55 cm3/min. In Figure 5-46, the experimental data of DST for PVA solutions of different concentrations are given. These results show the change in Dynamic Surface Tension as a function of the increase in polymer concentration. Clearly, at PVA polymer concentrations of up to 1 %, the surface tension significantly decreases as compared to the surface tension of water. Over the concentration range from to 1 % to 3 %, the surface tension decreases gradually but at greater concentration levels the surface tension remains nearly constant. The decrease in surface tension can be described, according to the Ward and Tordai model [Pefferkorn et al., 1985; Nahringbauer, 1995; Fainerman and Miller, 1996], as a orption process. For a short time scale (from milliseconds to seconds) the equation can be written as diffusion-controlled ads 21)(2)(Dtcto (5.25) surface concentration at any time, (g m Where, Co bulk concentration, (g m), : commonly used value ore pronounced at lower flow ratesthe greate the variation in This can be referred to as the time needed for the polymer to get onto the newly formetes, the bubbles surfaces remain almos an active agent at the interfacial region will be lese 2 ), 2D monomer diffusion coefficient, (m 2 s 1 ). t: time, (s) It is interesting to note that these decreases in surface tension are m r the increase in the flowrate, the smaller the DST d interfacial region. Therefore, at high flow ra t clean and the effect of the polymer as s because the polymer molecules do not have enough time to adsorb onto it. Th

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111 lower the flow rate, the higher the chance for the polymer molecules to adsorb onto thinterface of the generated bubbles. e 60 66687072DST,cm 6264012345 74PVA conc, % dyne/ Flowrate, cm3/min 1.55 0.78 0.47 0.23Figure 5-46. Dynamic surface tension of PVA concentration at different CO2 flowrate Figure 5-47icity in terms of PVA concentration at a different CO2 gas flowrate. It is interesting to note that This is due to formation of a membrane ration, which is able to resist the pressure he CO2 gas generated. However, the higher the bubble formation rate (flow shows the results of using Gibbs equation to determine the elast the elasticity increases with PVA concentration as a result of increasing the polymer concent exerted by t rate), the lower the elasticity. This can be referred to as the lower diffusivity of the polymer to the bubble surface and, consequently, DST at high bubble formation rates. The flow rate of CO 2 generation was found to be very low due to the reaction, which is closer to equilibrium conditions. This also indicates higher membrane elasticity.

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112 024681012 14 16012345PVA conc, %Elasticity, dyne/cm2 1.55 Flowrate, cm3/min 0.78 0.47 0.23 Figure 5-47. Elasticity of PVA membrane in terms of PVA concentration at different CO2 flowrate. -39). and 5-49 for both two different fractions. The fitting parameters are given in Table 5-8. It should be noted that these parameters are different from the dolomite system due to differences in the number of active sites on both cases. Examining the data in Figures 5Validation of the Model Using a Different Carbonate Mineral The calcite was used as another carbonate material to validate the developed models. The calcite dissolution tests were conducted for coated and uncoated calcite particles in 3 % sulfuric acid solution at room temperature. Figures 5-48 and 5-49 show the results of both coated and uncoated particles. As expected, the curves show similartrends as that obtained in the dolomite dissolution experiments (Figures 5-38 and 5In other words, lower dissolution is obtained in presence of polymer coating. Once again this may be explained on the basis of the presence of a polymer, which controls the transfer of ions to and from the boundary layer and then to the bulk solution. Fitting of active site model to this experimental data is given in Figures 5-48

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113 48 and 5-49 indicate an excellent fit of the model to the calcite system, which is a good verification for the model. Table 5-8. Active sites disappearance parameters for dissolution of calcite Large Small Uncoated Coated Uncoated Coated *P-1 0.016 0.008 0.06 0.06 0.0051 0.0075 0.0013 0.0026 *Km5.97 5.97 10 10 Acini 5.9 2.5 30 9.3 P-1 = KrA Km= KmA 0.01Ca dissolve 00.020.025 .015d, M 00.005020406080100120140160Time, Min. Model-uncoated Exp-uncoated Model-coated Exp-coated Figure 5-48. Calcite dissolution: model vs. experimental data 0.25-0.35 mm particle size 00.005Time, Min.Ca 0.01020406080100120140160 die 0.0150.020.025ssolvd, M Model-uncoated Exp-uncoated Model-coated Exp-coated Figure 5-49. Calcite dissolution: model vs. experimental data for 1-2 mm particle size

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114 Summarizing Remarks It was found that wor k of adhesion decreases with increasing PVA concentration. ill create om for bubbles increaA membranes ability to expand. On the isolated hyite, which can be used evidence that the adsorption o interaction o with dolomigen bonding. However, the FTIR did not give a clear explanation for the adsorption of PVA on apatite. As a physical adsorption confirmation, zeta potential measurements indicated that the PVA does not change the IEP for either apatite or dolomite. Also, the adsorption of PVA in the presence of supernatants indicates that the PVA adsorption is not affected by the supernatants even though the PVA may tend to form aggregates in highly ionic strength (as reported in literature). Moreover, The adsorption isotherm is S-Shaped, which means adsorption is physical on both minerals. The adsorption on dolomite is more stretched than on apatite. Also, the parking area of PVA on dolomite is less than on apatite. Furthermore the adsorbed layer thickness is higher in the case of dolomite than apatite, desorption tests indicated that the process of PVA adsorption on the minerals surfaces (dolomite and apatite) is a slowly reversible process, and the PVA membrane elasticity was determined using dynamic surface tension. The elasticity modulus increases with PVA concentration and decreases with increasing CO2 flowrate. More Low work of adhesion is favorable for the reactive flotation processthis w ro to form and se the PV other hand, FTIR shows that the presence of droxy l groups is exclusive for dolom r f PV A te depends mainly on hydro higher than the adsorption on apatite and the conformation of the polymer on dolomite is

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115 interestingly, the rate of CO2 evoce is very low which keeps the membcalcite system, which is a good verifi lution at the particle surfa rane at its higher elasticity. From modeling point of view, two models were developed to predict the CO 2 formation rate and these models agreed well with the experimental data. The density change of the particle was predicted and verified by single particle beaker tests. As another carbonate mineral, calcite was used. Calcite dissolution tests showed similar trends as that obtained in the dolomite dissolution experiments. Moreover, the model showed an excellent fit to experimental data of the cation for the model.

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116 rolling factors were screened using the Placket Burman design and three factors were determined to be significant within a 95 % confidence vel. These factors were PVA concentration, acid concentration, and particle size. To urther explore the effect of these factors, Central Composite Design (CCD) was used. he surface responses of CCD for different particle sizes indicated that the percentage of gO could be lowered to less than 1 % with recovery increasing with decreasing the article size. Additionally, it was noticed that the PVA consumption in the original RF process as about four to six pounds per ton, which is very high and unfeasible. Many attempts decrease the PVA consumption were conducted and it was found that using a spray to re-condition the rock can decrease the consumption to as little as one pound per ton. his was determined by running a factorial design in terms of particle size, conditioning me, and PVA. The optimized results were applied for process enhancement using a sluice, a ravity concentrator, which separates particles depending on the differences in the gravity CHAPTER 6 CONCLUSIONS AND RECOMMENDATIONS FOR FUTURE WORK Conclusions In this study, the reactive flotation (RF) process was developed with a high potential to separate dolomite from phosphate rock at high recoveries. The optimization of this process was carried out using screening and central composite designs. The cont le f T M p w to p T ti g 116

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117 o f individual particles. The results were very encouraging and similar to the data obtained in beaker tests. With the RF process developed and optimized, the next step was understood the mechanismerms of dolomite/PVA and phosphate/PVA well as bubble formation and stabilstudied using severth sion VA ease in surface tension indicates that PVA is a surface-active molecule, whicheen ydroxyl (OH) is the functional group in PVA molecules, this polymer (PVA s involved in this process. the process was explored in t Consequently, interactions as ity. The interactions of both dolomite and phosphate with PVA were al techniques in order to elucidate the mechanism of adsorption of PVA on bominerals. Work of adhesion was determined by measuring the equilibrium surface tenand contact angle. It was found that the work of adhesion decreases with increasing Pconcentration, which indicates film formation on both Dolomite and Phosphate particlesThis decrease is due to the decrease in surface tension and increase in contact angle (making the cosine of the contact angle smaller). The final result is an overall decrease in the work of adhesion. The decr satisfies the water molecules at the water/air interface. Moreover, the surface tension remains at a constant value after 1 % PVA concentration is reached. This indicates the formation of a tight molecular film at the interface, which, consequently, increases the viscosity and contact angle due to the formation of hydrogen bonds betwPVA molecules. Since the h ) was expected to adhere to surfaces by hydrogen bonding. To confirm this hypothesis, the FTIR was used to characterize the surface of both minerals. Results of the

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118 FTIR indicated the presence of isolated OH groups on dolomite only and hydrogen bonded OH grou ps on both minerals. adsorption isotherms were determined for both minerals as well. Isotherms were s s: The adsorption on dolomite is higher than on apatite O2 bubbles will burst. Accordingly, the low flow rate is required to keep ce ound rmation rate to be very slow relative to the data measured by DST. rticle Secondary evidence, indicating the physical nature of PVA adsorption on Dolomite and/ or Apatite particles, was also considered. By using zeta potential measurements, results indicated no shift in the isoelectric point of PVA. The studied as a function of the equilibrium time, which was determined from previouadsorption kinetic studies to be 2 hours. Characteristics of the isotherms were as followThe isotherms were S-shaped The adsorption process resulted in the formation of multiple layers on dolomite. The thickness of the adsorbed layer on dolomite was calculated to be about 3 times thicker than apatite. The importance of the thickness of adsorbed layer lies in its resistance to the C formation rate. If the CO 2 formation rate is very high the stability of the PVA membrane will be affected and the the bubbles at maximum stability. The previously discussed finding was revealed using measuring dynamic surfatension (DST) maximum bubble pressure method at different flow rates. It was fthat increasing the PVA concentration increases the elasticity modulus. However, increasing the flowrate decreases the elasticity modulus. The actual experimental results showed the CO 2 fo In the kinetic study, the CO 2 rate was calculated in terms of Mg +2 ions dissolved. From the reaction equation, the CO 2 was determined stoichiometrically for two pasize fractions. The results of the kinetics experiments revealed that bare (uncoated)

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119 particles dissolved faster than coated ones. However, both of them reached a constanlevel of Mg t period of time. These observations were lubility than uncoated particles. In addticle. The second is the disappearance of tiveill continprodule densitythe smaller the particle size, the shBuild a new sluice design capable of continuous operation performance in terms of grade and recovery +2 dissolved concentration after certain attributed to the formation of product layers such as CO 2 or gypsum, which act as barriers. I was noted that the coated particles had a higher so ition, both types of particles reached a plateau of solubility after a certain period of time. This distinct behavior of the particles was explained by two controlling mechanisms. The first is the acid blockage mechanism in which CO 2 formation prevents the acid from reaching the surface of a par ac sites to which the magnesium carbonate can adsorb. In both cases, the reaction w ue until all active sites have been used or the sites are covered with reaction cts. The modeling of these two mechanisms were carried out and fitted to experimental data, to which they conformed well. The same models used to predict the CO 2 formation rate were used to predict the decrease of partic arper the change in the density. To validate this model, the predicted values for several size fractions were compared with experimental beaker tests. These showed a good agreement as well. Recommendations for Future Work There are several suggestions for future work: Investigate a lower polymer dosage with fine fractions Test a lower molecular PVA polymer Extend the model derived in this work for prediction of gravity separator

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BIOG RAPHICAL SKETCH a ning engineering at Cairo University. He completed masters degree in May ), researcher assistant in 1993. In 2001, he came to the University of ch assistant and performed research on minerals Ayman El-Midany was born in Cairo, Egypt, in February 1969. He attended the College of Engineering at Cairo University from 1986 to 1991. He completed bachelors degree in mining engineering in 1991. In 1992, he enrolled for graduate studies in mi 1997. He Joined Central Metallurgical Research and Development Institute (CMRDICairo, Egypt, as Florida to pursue a Ph.D degree in materials science and engineering. He worked with Professor Hassan El-Shall as a resear separation and particle science technology. 129