UNIVERSITI PUTRA MALAYSIA
SYNTHESIS OPTIMIZATION AND EXTRACTION OF RARE EARTH METAL IONS BY POLY (N - METHYlHYDROXAMIC ACID) RESIN
SECKIN BALCl
FSAS 1998 19
SYNTHESIS OPTIMIZATION AND EXTRACTION OF RARE EARTH METAL IONS BY POLY (N - METHYlHYDROXAMIC ACID) RESIN
By
SECKIN BALel
Thesis Submitted in Fulfi l lment of the Requirements for the Degree of Master of Science in the Faculty of Science & Environmental Studies
Universiti Putra Malaysia May, 1 998
ACKNOWLEDGEMENTS
I extend my deepest thanks to my supervisors Assoc. Prof. Dr. Md. Jelas
Haron and co-supervisor Assoc. Prof. Dr. W. M. Z. Wan Yunus and Dr. Mansor
Ahmad for their invaluable comments and contributions to this study to make it more
efficient, to Mr. Kamal Margona for h is endless support during the analysis with AAS,
Mrs. Choo Chai Syam for her incredible efforts and friendship for I .C .P. analysis and
to Un iversiti Putra Malaysia for its invaluable approach and concerns to create the
best environment for academicians and students.
The deepest thanks are also exlented to Ambassador of Turkish Embassy,
H .E. Ferhat Ataman and h is wife Ayse Ataman, to Commercial Counsellor Mr. Attil la
Gokhan Kizilarslan and his wife Sevda Kizilarslan , to M il itary Attache Captain Oguz
Orh un and h is wife Ayten Orh un for their ful l support and encouragement for me to
do better.
Furthermore, I am very grateful to my spouse dear Ali Balci for an oppertun ity
to l ive in Malaysia and to do Master of Science; and for h is patience and support
econom ically and also spiritually, through out my study. And I also thanks to my dear
mother Mrs. Refika Merder who really help me by taking care of my chi ld,
disregarding her health problems. F inally I would l ike to dedicate my thesis to my
lovely son Yigithan Balci and my spouse Al i SalcL
11
TABLE OF CONTENTS
Page
ACKNOWLEDGEMENTS . . . . . . . , . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . " . . . . ... . . . . . . . . . .. .... . . . . . . . . .. . . ... i i
LIST OF TABLES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . " . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . vi
LIST OF FIGURES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . vii
ABSTRACT . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ix
ABSTRAK . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . x
CHAPTER
INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
I I LITERATURE REViEW . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7
Ion Exchange and Chemistry . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7
Types of Ion Exchangers . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 0
Synthetic Resin Ion Exchangers . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 1
Cationic and Anionic Exchange Resin . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 1
Chelating Ion Exchangers . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 5
Preparation of Poly(Hydroxam ic Acid) Resin . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . 18
Synthesis of poly(N- Substitutedhydroxamic Acid) Resin . . . . . . . . . . . . . . . . . . . 25
iii
Classification of Ion Exchange Methods Used in Analytical Chem istry . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 26
Separation of Rare Earth Metal Ions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 29
III MATERIALS AND METHODS ....................................... ............ 34
Materials . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 34
Methods . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36
Preparation of Buffer Solution . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36
Copolymerization of Poly(Methyacrylate-Divinyl Benzene) . . . . . . 36
Preparation of Poly(Hydroxamic Acid) Resins . . . . . . . . . . . . . . . . . . . . . . . 37
Preparation of Poly(N-Methyl Hydroxam ic Acid) Resin . . . . . . . . . . . . 38
The Classical Visual Test . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 38
Infrared Spectroscopy . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 38
Hydrogen Ion Capacity . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 39
Hydroxamic Acid Group Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 39
Water Content Determination . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 39
Capacities of Poly(Hydroxamic Acid) and POly(N-methyl hydroxam ic Acid) Resins for Copper( l l ) and I ron( l I l) Ions . . . . . . . 39
Optimum Conditions for Preparation of Poly(N-methyl hydroxam ic Acid) Resin . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .40
Stabil ity of the Resin . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 43
Sorption Kinetic of the Resin . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 44
Sorption Capacity Metal Ions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 44
iy
Separation of Copper( l l) and I ron( I I I ) . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 45
Separation and Elution of Rare Earth metal Ions . . . . . . . . . . . . . . . . . . . 46
IV RESULTS AND DiSCUSSiON . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 47
Confirmation of the Product . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 47
Comparison of POly(N-unsubstituted Hydroxamic Acid) Resin and Poly(N-methyl Hydroxamic Acid) Resin Metal Complexes . . . . . . . . . . 52
Stabil ity of the Resin . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 61
Sorption Kinetics . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . 62
Separation of Metal Ions by Poly(N-methylhydroxamic Acid) Resin . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 64
Separation of Copper( l l) and I ron( l l I ) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 64
Distribution Coefficient of the Resin for Rare Earth Metal Ions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 67
Elution of Lanthanum( l l I) and Cerium( I I I ) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 70
Separation of Mixture of Rare Earth Elements . . . . . . . . . . . . . . . . . . . . . 73
V CONCLUSiON . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . , ............... 80
BIBLIOGRAPHy . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . , ............... 82
APPENDiX . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 87
BIOGRAPHICAL DATA . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . 90
LIST OF PUBLICATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 91
LIST OF TABLES
Table Page
1 . Functional Groups of Some Commercial Ion Exchangers . . . . . . . . .. . . . . . . . . . . . . . . . 3
2. Rare Earth Content in Typical Xenotime ............................................... 31
3. Effect of N-Methylhydroxylam ine Hydrochloride Concentration on Preparation of N-Methyl Hydroxam ic Acid Resin ... . . ... . . . . . . . . . . . . . . . . . . . . . . . 41
4. Effect of Sodium Hydroxide Concentration on Preparation of N-Methyl Hydroxamic Acid Resin . . . . . . . . . .. . . . ... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ... 42
5. Effect of Amount of Poly(Methylacrylate-Divinyl Benzene) on Preparation of N-Methyl Hydroxamic Acid Resin . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . 43
6. The Water Contents of the Resins Prepared from Different Amount of N-Methylhydroxylamine . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 56
7. The Water Contents of the Resins Prepared from Different Amount of Copolymer . . . . , " . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . . . . , .. 56
8. Copper Sorption Capacity for Stabil ity Study ... . . . . . . . . .. . ... . . . . . ... . . . . . . ... . . . . . . . 61
9. The Highest Distribution Coefficient Values of Rare Earth Metal Ions and the Respective pH Values . . . . . . . ... . . . . . . . . . . . .. . . . . . . . . . .. . . . . . . . . . . . . . . . . . . ... . . . 69
vi
LIST OF FIGURES
Figure Page
1 . I R Spectrum of P .M.A . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . .. . .. . . . . .. . . . . . . . . . . . . . . . . . . .. . . .. . . . . 50
2. I R Spectrum of NMPHA R .. .. . . . . . . . . . . . .... . ... .. . . .. . . . ... . . . . . . . . . . . . . . . . . . .... . . ... ... 51
3. Sorption Capacity of Cu2+ Ions on Unsubstituted PHA Resin at Various pH .................................................................. 53
4. Sorption Capacity of Cu2+ Ions on PNMHA Resin at Various pH ................ 54
5. Sorption Capacity of Copper(l l ) for the Resins Prepared Using Various Amount of NaOH . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 58
6. Sorption Capacity of Copper(I I ) for the Resins Prepared Using Various Amount of PMA .......................................................... 59
7. Sorption Capacity of Copper(l l ) for the Resins Prepared Using Various Amount of N-Methylhydroxylamine Hydrochloride .............. 60
8. Effect of Shaking Periods on the Copper( l I ) Sorption Capacity of the Poly(N-methylhydroxamic Acid) Resin ........................... 63
9. Sorption Capacities of Copper ( I I ) and I ron ( I I I) of PHA and P(N-methyIHA) Resins ............................................................. 65
1 0. Separation of Copper ( I I ) from I ron ( I I I ) by poly(N-methyl HA)R . . . . . . . . . .. . . . . . . . . .. . . . . . . . . . . . . . . ... . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . 66
1 1 . Distribution Coefficient for Rare Earth Metal Ions at Various pH . . . . . . . . . . . .. . . 68
1 2. Elution of La3+ at pH . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 71
1 3. Elution of Ce3+ at pH 1 ..................................................................... 72
1 4. Elution of y3+, Sm3+, La3+ and Nd3+ at pH 2 ............................................ 75
\"11
15. Elution of Gd3+, Vb3+ , Pr3+, Ce3+ and Dy3+ at pH 2 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 76
16. Separation of V3+ and Sm3+ at pH 2 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 77
17. Separation of V3+ and Nd3+ at pH 2 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ... 78
18. Separation of Sm3+ and La3+ at pH 2 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 79
,-iii
Abstract of thesis presented to the Senate of Universiti Putra Malaysia in fulfilment of the requirements for the degree of Master of Science.
SYNTHESIS OPTIMIZATION AND EXTRACTION OF RARE EARTH METAL IONS BY POLY (N-METHYLHYDROXAMIC ACID) RESIN
By
SECKIN BALCI
May 1 998
Chairman: Associate Professor Md Jelas Haron, Ph.D.
Faculty: Science and Environmental Studies
Poly(N-methyl hydroxamic acid) resin was synthesized from crosslinked
poly(methacrylate-d ivinyl benzene). The optimum amounts of N-
metylhydroxylam ine hydrochloride, NaOH, poly(methacrylate) were 2.2 g, 4 g and
and 4 g, respectively and 20 ml water-ethanol solution (75%) was used. The
reaction was completed at room temperature, for 24 hours. The abil ities of poly(N-
methylhydroxamic acid) resin and poly(N-unsubstituted hydroxamic acid) resin to
form complexes with Cu ion were compared. Kinetics study carried out indicated
that metal sorption process by the resin is fast and it is suitable to be used in
column technique. The resin showed good stabi l ity in buffer pH 4 and 1 M HCI
solution . Metal sorption capacities were determ ined for Cu, Fe, Y, La, Ce, Sm , Vb,
Nd, Pr, Dy and Gd. Separations of Cu / Fe, Y / Sm , Y / Nd, Sm / La have been
carried out.
ix
AOsual\ tesis yan9 dikemukakan kepada Senat Universiti Putra Malaysia sebagai memenuhi keparluan untuk ijazah Master Sa ins.
PENGOPTIMUMAN SINTESIS DAN PENGEKSTRAKAN ION LOGAM NADIR BUMI OLEH POLI(ASID N-METIL HIDROKSAMIK) RESIN
Oleh
SECKIN BALCI
May 1998
Pengerusi: Profesor Madya Md Jelas Haron, Ph.D.
Fakulti : Sains dan Pengajian Alam Sekitar
Resin poli (asid N-meti l h idroksamik) telah d isintesis daripada
poli (metakralik-divini l benzena) berangkai si lang. Jum lah optimum �
meti lh idroksi lamina h idroklorida, NaOH, poli(metakrilat) adalah masing - masing
2.2 g, 4 9 dan 4 9 dan 20 ml larutan air - etanol (75 %) digunakan. Tindak balas
d ilakukan pada suhu bi l ik selama 24 jam . Keupayaan resin poli(asid �
metilh idroksam ik) and poli(asid h idroksam ik) untuk membentuk kompleks dengan
ion Cu d ibandingkan . Kajian kinetik menunjukkan bahawa proses serapan logam
oleh resin adalah pantas dan sesuai untuk digunakan dalam teknik turus. Resin
menunjukkan kestabilan yang tinggi dalam larutan pen imbal pH 4 dan larutan 1 M
HCI . Muatan erapan logam ditentukan untuk Cu, Fe, Y, La, Ce, Sm, Vb, Nd, Pr,
Oy dan Gd. Pemisahan , Cu / Fe, Y / Sm, Y / Nd, Sm / La juga dilakukan.
x
CHAPTER I
INTRODUCTION
The phenomenon ion exchange which usually involves either inorganic or
organic ions in predom inantly aqueous solutions is a process involving the
reversible exchange of ions in solution with ions taken by a sol id ion - exchanging
material without perceptible permanent change in the structure of the solid.
Therefore, ion exchange can be any material that has the abil ity to uptake ionic
species from a solution with the simu ltaneous release of a chem ically equivalent
number of ions into solution .
The importance of the ion exchange however, is com ing from its widely
used area that provide the h ighest exchange capacity and is of greatest interest in
the laboratory as wel l as in industrial applications. They are used in many
chemical processes, including simple or chromatographic separations, catalysis
and analytical chem istry. Ion exchange processes are also employed in
hydrometallurgy and metal recoveries, the manufacture of sugar, in pharmacy and
medicine as wel l as in biochem istry and biotechnology, agricu lture and food
processing.
Within the framework of enrich ing economic and commercial activities
among the companies and countries, the current trend of these activities
2
influences the chemical industry and their researches. Scientists and researchers
have concentrated on some segments of chemical industry which are more
commercial as wel l as with scientific concerns. One of these segments is the
production of ion exchanger which is used in certain sectors such as nuclear
technology, electroplating industry, the sweetener industry, pharmacy, medicine,
biochem istry, biotechnology, analytical chem istry, homes, laboratories and small
industries, water treatment, treatment of drinking water and metal recovery.
Ion exchangers have been d istributed commercially under various trade
names: Allasion , Amberlite, Chempro, De-Acidite, Diaion, Dowex, Duolite, Imac,
lonac, Kastel, KatexlAnex, Lewatit, Liquonex, Mykion , Permutit, Purolite, Varion ,
Vionit, Wofatit, Zeo-Karb, Zerolit. Functional groups for some of these ion
exchangers are g iven in Table 1 (Dorfner, 1 99 1 ) .
Although hydroxamic acid ion exchange resin is sti l l not commercially
available today, many researches have been concentrated on th is type of resin,
especially on the various synthesis methods, within the last few years. A
successful experiment to produce hydroxamic acid resin was achieved in 1 965
where it was formed from a commercial carboxylic acid by esterification and then
treatment with hydroxylamine. The product was confirmed with visual tests
through the formation of complex by vanadium (V) and iron ( I I I ) ions. Furthermore,
infrared spectrometry also confirmed the presence of hydroxam ic acid groups in
the product. However, the conversion of carboxylic group to hydroxamic was
found to be very poor (only 3.9 %) (Petry et a I . , 1 965) .
Table 1 : Functional Groups of Some Commercial Ion Exchange Resins
Functional Group
Tertiary am ine
Quaternary ammonium
Amidoxime
Carboxylic acid
Mercaptane
Sulfonic acid
Amino-diacetic acid
Carboxymethyl
Diethylam inoethyl
Commercial Name
Duolite A 303, Lewatit AP 49, Lewatit M P 62
Duolite A 132, Duolite A 1 61 , Duolite A 1 62
Duolite ES 346
Duolite C 433, Duolite C 464, Duolite 468
Duolite ES 465
Duolite C 20, Duolite C 225, Duolite C 204 F
Dowex A 1 , Chelex 1 00, Amberlite IRC 71 8
Serva CM 23, Serva CM 32 Serva CM 52
Serva DEAE 23 SH, Serva Serva DEAE 23 SN, Serva DEAE 23 SS
3
4
Earlier two simi lar methods were used to synthesis this type of resin. I n one
method, carboxylic acid was first converted into the acid chloride and then used to
produce the (hydroxam ic acid) resin. The product was a bifunctional cation
exchanger with carboxylic acid and hydroxam ic acid (Cornaz et aI . , 1 957). In the
other method, a l inear hydroxamic acid resin was produced by hydroxylam inolysis
of poly (methyl acrylate) and hydroxylam ine in the presence of sodium methoxide
and benzene (Kern and Shulz, 1 957). These explorations of synthesis of
(hydroxamic acid) resin indicated that the synthesis method could be improved by
using a methacrylic acid - methylacrylate copolymer as this wou ld prevent the
formation of a hydride. A series of synthesis methods were studied by using
cross-linked polymer and commercial carboxyl ic acid as a starting material and
then used for the column operation. The resin synthesized sti l l contained
carboxylic acid groups because of the difficu lty in formation of the acid ch loride
intermediate (Vernon and Eccles, 1 975).
Mandez and Pil lai (1 990) prepared the resin from styrene maleic acid
copolymer via the four step reactions through the formation of carboxylic acid and
acid ch loride.
The (hydroxam ic acid) resin was also synthesized by a one-step reaction
by Wan Yunus (1 980). The resin , which was in microporous microbead particles,
was shown to be effective in the kinetics of metal sorption. The same method of
one step reaction was also exam ined with different starting chern icals were
poly(ethyl acrylate-divinyl benzene} (Wan Yunus et aI., 1 988 and Lee and Hong,
1 994) and poly(methyl acrylate-divinyl benzene) (Haron et a I . , 1 994).
5
The resins were used to separate n ickel from cobalt and for iron ( I I I )
-copper-cobalt separation (Haron et a I . , 1 994). gold from silver (Vernon and Wan
Yunus, 1 981 ) . zinc from cadmium and, cobalt from copper and n ickel (Shah and
Devi, 1 987) and uranium from neodymium (Mohammed, 1 987). The resins had
also been successful ly used for the recovery and separation of uranium and iron
from the simulated synthetic and real sea water (Vernon and Shah , 1 983; Vernon
and Eccles, 1 976b) .
Three different hydroxam ic acid resins which are N-methyl, N-phenyl and
N-unsubtituted were prepared from a commercial poly(styrene-divinyl benzene)
Amberlite (XAD-4) and their properties were compared (Phi l l ips and Fritz,
1 982).The resins showed good stabil ity and the capacities were not affected by
treatment with 2 M hydroch loric acid or 1 M ammonium hydroxide. (N
methylhydroxamic acid) resin was synthesized by substituting N
methylhydroxylammonium chloride via a four step reaction . The (N
methylhydroxam ic acid) resin was found to have the h ighest metal capacity and
formed the most stable complexes with copper, alum inum , and thorium metal
ions. The extractions of nineteen metal ions including rare earth such as europium
and lanthanum were studied by using (N-methylhydroxamic acid) resin. The
results showed, the resin extracted 50 % of the ions at d ifferent pH values. This
indicate that the poly(N-methyl hydroxamic acid) resin can be used to separate
rare earth metal ions. However, the product sti l l contained carboxylic acid (Ph il l ips
and Fritz, 1 982) .
6
Wan Yunus et al. ( 1 986) described an alternative method of preparing the
poly(N-methyl hydroxamic acid) resin by hydrolysing poly(carboxylic acid-d ivinyl
benzene) . The preparation reaction was completed in 2 steps. In this study.
poly(methacrylate) was used as a starting polymer to prepare poly(N-Methyl
hydroxamic acid) resin. It was reported that the h ighest hydroxamic acid capacity
was obtained from poly(methacrylate) . Thus capabil ity of (N-methyl hydroxamic
acid) resin to sorb metal ions cou Id have been increased by appropriate method
and starting polymer.
The aims of this study are to synthesis a chelating polymer containing
(N-methylhydroxam ic acid) as a functional group from cross-linked
poly(methylacrylate--divinyl benzene). to compare the performance of (N
unsubstituted hydroxam ic) and (N-substituted hydroxam ic acid) ion exchange
resins, to determine the abil ity of the resin to sorb rare earth metal ions which are
great econom ic important and copper and iron which are contained in the natural
or industrial sources and to separate several rare earth metal ions. and copper
from iron by the resin.
CHAPTER II
LITERATURE REVIEW
Ion Exchange and Chemistry
Ion exchangers is the name given to insoluble electrolytes containing labi le
ions that easily exchange with other ions in the surrounding medium without any
major physical change occurring in the electrolytes' own structure. The process
taking place is usual ly cal led the ion exchange reaction and the labile ions in the
ion exchangers exchange reversibly. The ion exchanging electrolyte is in general
of a macromolecule of complex nature. Since after d issociation, al l electrolytes
exist only as either cations or anions, the ionic sites present in a macromolecu lar
matrix in the case of ion exchangers can also only be either cationic or anion ic.
Thus the different matrices consisting of repeating units in the macromolecules,
such as inorganic materials, highly complex organic materials of natural origin,
and the comparatively simple·structured synthetic resins, carry an electrostatic
charge in the form of a surplus charge or a fixed ion which is neutralized by the
charge of the labile ion . These counter ions are cations in a cation exchanger and
an ions in an an ion exchanger.
7
8
The term ion exchange has often been closely related to or even used
synonymously with adsorption and absorption. Exchange-adsorption was used
instead of ion exchange during the transition in understanding from base
exchange to modern cation exchange or anion exchange. It is important first to
d istinguish between absorption and adsorption before one can identify ion
exchange.
Absorption refers to a uniform penetration of the component of a system
into the solid absorbing material following the old chemical rule of "similia
similibus solvuntur " ( l ike l ikes l ike) and with no change in concentration.
Absorption is thus a process in which the solid engulfs another substance by
d istributing it very even ly throughout its own entire structure. The term adsorption
on the other hand refers to the interaction of a solute with a sol id adsorbent
through physical forces associated with the solid, resulting in a change in
concentration of, e.g. , a particular dissolved component of a system which occurs
mainly at the surface of the solid. Adsorption is thus characterized by an increase
in concentration, which takes place at the interface of the l iquid carrying the solute
and the solid adsorbent. Adsorption and absorption can be denoted as sorption
processes. Here, although the term adsorption for an ion exchange process may
appear strange, phenomena associated with ion exchange have involved
mechanisms other than the ion ic exchange of ions.
Today, the term ion exchangers denotes insoluble polymeric or
macromolecu lar substances with fixed ions. The reactive groups are dissociable
and either present by nature in a natural ly occuring exchange material or have
9
later been incorporated during the manufacture of a synthetic ion exchanger. Ion
exchangers are therefore reactive polymers or reactive macromolecules, but this
term does not include macro-ions. In the case of ion exchangers as reactive
polymers, the reactive groups are not functional, neither in the sense of the
definition of functional groups in organic chemistry nor as defined in polymer
chemistry. It is by reactions of polymers that ion exchangers can usually easily be
obtained, and these are then cal led reactive polymers. The fixed ions or reactive
ionic groups of ion exchangers have the ability of undergoing ion ic exchange
reactions, but they are also able to store ionic species as counter- ions.
Ion exchange is a phenomenon or process involving the reversible
exchange of ions in solution with ions held by a solid ion-exchanging material , in
which there is no directly perceptible permanent change in the structure of the
solid. An ion exchanger can be any material that has the abil ity to uptake ionic
species from a solution with the simultaneous release of a chemical ly equivalent
number of ions into this solution . These materials include cellu lose, dextran and
agarose derivatives, clays and clay minerals, materials based on coal and other
organ ic natural products, synthetic l iquid ion exchangers and ion exchange
membranes. While all the types just mentioned are of greater or lesser uti l ity, in
special applications, in this text by 'ion exchanger' is meant synthetic ion
exchange resin, if not otherwise stated.
10
Types of Ion Exchangers
Ion exchange was first investigated with inorganic materials and found
some industrial use, but were almost completely displaced by synthetic ion
exchange resins. The demand for ion exchange materials that wou ld satisfy the
most diverse requirements led to the development of new products, which must
be considered as separate ion exchanger types according to their special
properties.
Among the available types, synthetic ion exchange resins are of the
greatest importance. But inorganic ion exchangers should not be neglected, since
these have once again aroused interest because of their mechanical, thermal and
chemical properties and because, in l ight of their m ineralogical parallels, they offer
information about numerous processes in soil science. The cel lu lose ion
exchangers represent a separate type with their own characteristics related most
closely to another group. Both types have been rapidly accepted in ion exchange
chromatography where they have become indispensable for analytical as well as
preparative work. I n addition, ion exchangers based on carbon have been
produced and, together with a number of other materials with ion exchanging
properties, have been investigated for their appl icabi l ity. Liquid ion exchangers, as
another type, probably are important primarily because of the technological
possibil ities they offer.
11
Synthetic Resin Ion Exchangers
For the description of properties of synthetic ion exchange resins, three
factors are decisive: The raw material which is used for the construction of the
skeleton or the matrix, bridging agents for crosslinking and insolubil ization , and
the type and number of the ionogenic groups. Synthetic ion exchange resins
chemically are insoluble poly-electrlytes with a h igh but not unl imited moisture
regain capacity. With regard to their function one speaks of cation exchangers,
anion exchangers, and chelating ion exchanger types.
I n principle, polymerization and polycondensation can in principle be used
as the synthesis routes to form the matrix. At the present time, polymerization
resins have become more important than polycondensation resins, as they have a
h igher chemical and thermal stabil ity.
Cationic and Anionic Ion Exchange Resin
One of the most starting material is styrene which is polymerized with itself
and with d ivinylbenzene into a polymeric molecule:
-CH - CH - CH - CH - CH - CH -2 2 2
CH - CH -
I 2
- CH - CH - CH - CH -2 2
12
Incorporation of functional groups such as -S03H , -COOH and -P03H into
the pendant benzene rings in the matrix produce a cationic ion exchange resin.
Where else anionic exchange resin is produced when functional groups such as -
NCH30H, -N H (CH2)2 0H or -NH3
0H is incorporated into the benzene rings.
Another important starting materials for ion exchanger are acrylic
compounds such as acrylic acid, methacrylic acid, acrylic acid ester or
acrrylonitrile. For example acrylic ion exchange resins was made by suspension
polymerization of methacrylic acid and divinyl benzene according to the following
equation (Dorfner, 1 991 ) :
CHa I C=CH2 + I COOH
CHa I
- C - CH - CH - CH -2 2
I COOH
- CH - CH -2
13
A simi lar ion exchanger can also be synthesized from an acrylic ester
fol lowed by hydrolysis of the copolymer (Dorfner, 1 991 )
H I C- CH
b�o� + Polymerization
.
Hydrolysis
14
f CH - CH2-+------ CH - CH2 -
L booH n
- CH - CH -2
A resin prepared from an acrylic molecu le eleminates same interaction of
an aromatic matrix, as in the resin prepared from styrene, especially with the
sample contain ing an aromatic components.
The degree of homogeneity of ion exchange structures depends on the
purity, nature and properties of the starting materials used for their production, as
well as on optimum conditions of polymer synthesis. In spite of irregu lar structure
of the matrix it is possible to produce ion exchangers with a uniform distribution of
the ionic groups. The ever-increasing experimental data of recent years suggests
that the heterogeneity of ion exchangers is sti l l a d ifferent nature, and at the
molecular level of polymer chem istry it is basically associated with the structure of
in itial copolymer.
Cross-linking naturally depends first of al l on the quantity of d ivinylbenzene
used as the cross-linking agent in production. Commercial ion exchangers of the
gel type contain nominally between 2 and 1 2% divinylbenzene (Dorfner, 1 991 ) .