radioanalytical separation and size-dependent ion exchange property of micelle-directed titanium...
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Radioanalytical separation and size-dependent ion exchangeproperty of micelle-directed titanium phosphate nanocomposites
Rajesh Chakraborty • Sriparna Chatterjee •
Pabitra Chattopadhyay
Received: 9 September 2013 / Published online: 8 November 2013
� Akademiai Kiado, Budapest, Hungary 2013
Abstract Nanocomposite titanium-phosphate (TiP) of
different sizes was synthesized using Triton X-100 (poly-
ethylene glycol-p-isooctylphenyl ether) surfactant. The
materials were characterized by FTIR and powdered X-ray
diffraction (XRD). The structural and morphological
details of the material were obtained by scanning electron
microscopy (SEM) and transmission electron microscopy.
The SEM study was followed by energy dispersive spec-
troscopic analysis for elemental analysis of the sample. The
important peaks of the XRD spectra were analyzed to
determine the probable composition of the material. The
average size distribution of the particles was determined by
dynamic light scattering method. Ion exchange capacity
was measured for different metal ions with sizes of the TiP
nanocomposite and size-dependent ion exchange property
of the material was investigated thoroughly. The nanoma-
terial of the smallest size of around 43 nm was employed to
separate carrier-free 137mBa from 137Cs in column chro-
matographic technique using 1.0 M HNO3 as eluting agent
at pH 5.
Keywords Nanocomposite � Triton X-100 � Ion
exchange capacity � Radioanalytical separation
Introduction
The salts of multivalent metalloacids are a class of widely
studied inorganic ion exchangers because of their excellent
stability, insolubility in common solvent within very wide
limits of pH, subsequent utilization in column separation
and of course selective sorption behavior towards different
metal ions. Metalloacid salts of such type are a large group
of ion exchangers, amongst which tetravalent cations Zr,
Th, Ti, Sn are most studied, followed by some trivalent
cations such as Al and Cr. The anions most extensively
employed include phosphate, arsenate, antimonate, vana-
date and molybdate [1–3]. Acid salts of these types have
gel or microcrystalline structure and their composition and
properties are easily modified by the conditions of syn-
thesis. Their composition is most likely non-stoichiometric
and the proportion of cations, anionic groups and water
vary widely affecting the ion exchange properties of the
material. The hydrogen atoms bound to the anionic groups
create the ion exchange properties, and the selectivity
depends on the size of the exchanging cations and cavities
and the distances between layers of the material. In par-
ticular, the hydration size and energy of the exchanging
cations has a great effect on the selectivity of tunnel- and
layer-structured materials. If the material has high charge
density it can strip or partly strip away the hydration shell
of cations, decreasing their size and enabling their access to
the inner structure of the material. Among all the metal-
loacids discussed so far Phosphate-based molecular sieves
[4–6] of Zr and Ti with mostly a neutral framework have
also attracted considerable attention of the academia and
industry. Titanium phosphates (TiPs) have been exten-
sively studied with respect to their diverse structures and
wide applications in some areas such as ion exchange [6, 7]
intercalation [8] proton conduction [9, 10] catalysis
Electronic supplementary material The online version of thisarticle (doi:10.1007/s10967-013-2815-1) contains supplementarymaterial, which is available to authorized users.
R. Chakraborty � P. Chattopadhyay (&)
Department of Chemistry, The University Burdwan, Golapbag,
Burdwan 713104, India
e-mail: [email protected]
S. Chatterjee
Department of Colloids and Material Chemistry, IMMT,
Bhubaneswar 751013, India
123
J Radioanal Nucl Chem (2014) 299:1565–1570
DOI 10.1007/s10967-013-2815-1
[11, 12] and so forth [13, 14]. TiPs with layered [14, 15]
and mesoporous [16] structures have already been prepared
by different methods. Furthermore, attempts have been
made to synthesize nanostructured-TiPs apart from that of
porous materials. Such as TiP nanotubes were successfully
synthesized via a microemulsion-based solvothermal route
by an amine extraction [17]. Core–shell TiP nanospheres
were synthesized by using docusate sodium salt as the
structure-directing agent [18]. Hollow TiP spheres were
successfully obtained using polystyrene particles as tem-
plates [19]. Thus, due to their potential applications in ion-
exchange and catalysis the design of novel porous TiP
nanocomposite with well-defined morphology and uniform
size distribution is a matter of great interest.
The present work deals with the synthesis, characteriza-
tion and successful employment of nanocomposite TiP in
radioanalytical separation of the carrier-free 137mBa from137Cs. 137mBa is a short-lived radionuclide 62 (t1/2 = 2.55 min)
and is in secular equilibrium with the long-lived parent, 137Cs
[T1/2 = 30.07 years, 63 b-decay to 137mBa (94.4 %) with
single photon emission (662 keV). Radiochemical analysis
is required not only for processing radioactive waste samples
in the laboratory, but also for at-site or in situ applications of
carrier-free radioactive nuclides produced in the nuclear
reactions for radio-labeling of the pharmaceuticals in view of
getting potent radiopharmaceuticals. Monitors for nuclear
waste processing operations represent an at-site application
where continuous unattended monitoring is required to
assure effective process radiochemical separations produc-
ing waste streams that qualify for conversion to stable waste
forms. In connection with the present work, 137Cs/137mBa
generator has great advantage because of fast growth of
radioactive 137mBa, safe and frequent in-site elution, better
image quality, applications in teletherapy and irradiation or
sterilization of materials and plants [12, 20, 21].
Experimental
Reagent and apparatus
The powder X-ray diffraction (XRD) data were recorded
from a PANalytical X’pert Pro diffractometer with Cu Karadiation. The morphology of the nanosized materials was
studied by using of a JEOL-2003 analstation scanning
electron microscope (SEM). IR spectra were obtained by
JASCO FT-IR model 420 using KBr disc. Radioactivity was
measured with a scintillation counter equipped with a well
type NaI(Tl) detector. Size distribution measurements of the
nanoparticles were made by dynamic light scattering
(Model DLS-nanoZS, Zetasizer, Nanoseries, Malvern
Instruments). Samples were filtered several times through a
0.22 mm millipore membrane filter prior to measurements.
The radiotracer 137Cs in equilibrium mixture of daughter137mBa was obtained from Board of Radiation Isotope and
Technology (BRIT), India. TiCl4 (AR grade) was purchased
from Merck (Mumbai, India). Triton X-100 was purchased
from Himedia (Mumbai, India). The reagents for the syn-
thesis of the ion-exchange material were obtained from
commercial sources and used without further purification.
Synthesis of TiP nanocomposites using TX-100
Nanocomposite TiP were prepared by adding one volume of
0.05 M TiCl4 solution to two volumes of a (1:1) mixture of
6.0 M H3PO4 and TX-100 solutions drop-wise with constant
stirring [22]. Solutions of TiCl4 were prepared in 0.5 M
Fig. 1 a SEM image of TiP1and b STEM image of TiP1 for
EDS analysis
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H2SO4 and those of Triton X-100 and 6.0 M solution of
phosphoric acid was prepared in demineralized water. The
resulting slurry, was stirred for 3 h at this temperature, fil-
tered and then washed with demineralized water for removal
of the adhering ions (chloride and sulphate) till pH \ 4
before drying at room temperature. It was then treated with
1 M HNO3 for 24 h and was finally washed with deminer-
alized water, dried inside oven at 50 �C. The size of the core
of the material has been controlled by changing water to
surfactant ratio [23]. The ratio metric variation of water and
Triton X-100 has been utilized to produce nanocomposite
TiP of different sizes. TiP1, TiP2, TiP3, TiP4 and TiP5
were prepared using 10-1, 10-2, 10-3, 10-4 and 10-5 M of
Triton X-100 as a micelle, respectively.
Determination of size-dependent ion exchange capacity
(IEC) of TiPs
Previously reported batch method [24] was followed to
determine the hydrogen ion capacity. An accurately
weighed (0.5 g) portion of the ion exchange materials, TiP
were treated with 2.0 M HCl and then filtered off, washed
with distilled water, and dried at 50 �C for 2–3 h to remove
free HCl. The acidic form of the material was equilibrated
with 20.0 mL of 0.1 M NaOH solution for 1 h at room
temperature with stirring, and then the excess alkali was
titrated with 0.1 M HCl solution to determine the total acidic
hydrogen content. The IEC of the ion exchangers for dif-
ferent alkali and alkaline-earth metal ions was determined
by the batch method. To a glass-stoppered centrifuge tube
(diameter 2.0 cm) containing 0.5 g of the dry solid ion
exchangers, 50.0 mL of 2.0 M solutions of different alkali
and alkaline-earth metal ions were added to the tube in each
case; then the mixture was shaken for 1 h. The ion
exchangers were subsequently filtered off and washed with
bi-distilled water to remove the adhering H? ions. The
exchange capacities for the metal ions were determined by
measuring the liberated acid by titration with a standard
alkali solution. The IEC of each metal ion was determined
repeatedly for each concentration of Triton X-100 and the
effect size on IEC was observed.
Fig. 2 EDS spectrum of TiP1
Fig. 3 a TEM of TiP 4 with 100 nm scale. b SAED pattern of TiP
J Radioanal Nucl Chem (2014) 299:1565–1570 1567
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Studies on radio analytical separation by the TiP1
Separation of 137mBa from 137Cs radionuclide was per-
formed by column chromatographic technique following
the earlier reports [25–28]. In the column method, a glass
column of 5.0 cm length and 1.0 cm inner diameter was
packed with the 1.0 g of the material. The column bed was
preconditioned with a 10-5 M (pH 5) HCl solution. A
2.0 mL solution sample containing the measured amount of
cesium and barium radionuclides, where 137Cs is in secular
equilibrium with its daughter nuclide 137mBa was passed
through the column at a flow rate of 1.0 mL min-1. After
absorption of the mixture, 10.0 mL of a 10-5 M HCl
solution was passed through the column to ensure the total
absorption of the mixture. Finally, the daughter fraction
was eluted with 2 mL 1 M nitric acid, which was followed
40 60 80 100 120 1400
5
10
15
20
25
30
35
TIP 1N
umbe
r de
nsity
Particle size (nm)
40 60 80 100 120 1400
5
10
15
20
25
30
35
TIP 2
Num
ber
dens
ity
Particle size (nm)
40 60 80 100 120 1400
5
10
15
20
25
30
35
TIP 3
Num
ber
dens
ity
Particle size (nm)40 60 80 100 120 140
0
5
10
15
20
25
30
35TIP 4
Num
ber
dens
ity
Particle size (nm)
40 60 80 100 120 1400
5
10
15
20
25
30
35
TIP 5
Num
ber
dens
ity
Particle size (nm)
Fig. 4 DLS study for the
measurement of average size
distribution of nanoparticles of
TiP1, TiP2, TiP3, TiP4 and
TiP5 using 10-1, 10-2, 10-3,
10-4 and 10-5 M of Triton
X-100 as a micelle, respectively
1568 J Radioanal Nucl Chem (2014) 299:1565–1570
123
by collecting the effluent in ten successive counting tubes
(1.0 mL each). The c-activity in each tube was measured
with a NaI (Tl) c-ray spectrometer several times with a
time gap of 30 s.
Results and discussion
Characacterization of TiPs
The FTIR spectrum of TiP (Fig. S1) exhibits a broad band
in the region *3,410 cm-1 which is attributed to asym-
metric and symmetric hydroxy –OH stretches. A sharp
medium band at *1,640 cm-1 is attributed to aqua (H–O–
H) bending. A band in the region *1,050 cm-1 is attrib-
uted to P=O stretching. All the prominent peaks in the
XRD spectra (Fig. S2) for the materials have been analyzed
to determine the composition and probable molecular for-
mula of the material. The analyses of the prominent peaks
at 41.26, 58.04 and 73.20 (in 2h unit) confirm the material
as titanium phosphate with molecular formula TiP2O7
(Card no. JCPDF 38-1468).
Figure 1a, b show the SEM and STEM images of the
nanostructured material. Sample does not have unique
morphology. Magnified image shown in Fig. 1a clearly
indicates the size range of the individual flakes in nano-
meter region. EDS analysis (viz. Fig. 2) ensures the pre-
sence of P, Ti and O as dominant chemical elements in the
samples. The transmission electron microscopy (TEM)
image of TiP4 in Fig. 3a in 100 nm scale bar indicates the
flake-like morphology of the material. Further the SAED
pattern corresponding to this TEM image turns out to be
several partial rings, as shown in the Fig. 3b. The texture of
TiPs featured by diffraction pattern can be regarded as
polycrystalline with D spacing to be 3.2, 2.7 and 1.6 nm.
DLS measurement of TiP and sorption behavior
of the metal ions
The DLS study for measurement of average size distribu-
tion of TiP is shown in the Fig. 4. Variation of size of the
nanomaterial with varying water to surfactant (different
concentration of TX-100) ratio is listed in Table 1.
Exchange capacity for different metal ions increases with
decreasing size of TiP. This is simply because of the fact
that as the size of the particles becomes smaller, the
number of atoms on the surface of the exchanger increases.
Consequently small-sized particles show better sorption
behavior than the larger ones. Again the alkali metals show
a decreasing trend of the IEC (Cs? [ K? [ Na?) while the
alkaline earth metal ions follow the order Ba2? [ Ca2?.
The size and charge of the exchanging ions affect the IEC
of exchanger. This sequence is in accordance with the
hydrated radii of the exchanging ions. Ions with the smaller
hydrated radii easily enter the pores of the exchanger,
which results in higher adsorption.
Radio analytical separation
Separation of 137mBa from 137Cs radionuclide is ensured by
elution with a 1 M nitric acid solution. In presence of nitric
acid solution, Ba(II) forms very stable water-soluble
compound Ba(NO3)2 and hence it is eluted out of the
column matrix, whereas Cs(I) remains absorbed on the
column. The eluted sample was collected and counts of the
same fraction were taken at different time intervals to plot
the decay curve (Fig. 5). From the decay curve it is found
that the half-life of the daughter is 2.63 min which in very
much proximity to the actual the half-life of 137mBa (T1/
2 = 2.55 min). The radioactivity measured 1 h later is
equal to the background level which indicates that the
eluate does not contain observable amounts of the parent137Cs. As Ba(II) forms a stable and water soluble
Table 1 Exchange capacities of ZTPs of different particle sizes
towards metal ions
IEC in meq/g onto TiPs of different particle sizesa
Ions TiP 1 TiP 2 TiP 3 TiP 4 TiP 5
Na? 1.906 1.880 1.857 1.832 1.811
K? 2.116 2.09 2.067 2.046 2.021
Cs? 2.285 2.264 2.240 2.196 2.171
Ca2? 3.072 3.048 3.025 3.001 2.976
Ba2? 3.326 3.305 3.284 3.259 3.234
a Average size of TiPs (in nm):TiP1, 43.82; TiP2, 68.06; TiP3,
91.28; TiP4, 122.4; TiP5, 141.8
0 1 2 3 4 5 6 7 8 9
7.0
7.5
8.0
8.5
9.0
ln (
coun
ts)
Time (min)
Fig. 5 Decay curve of 137mBa eluted from TiP1 ion exchanger
(R = 0.99876 for eight points)
J Radioanal Nucl Chem (2014) 299:1565–1570 1569
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compound with HNO3, only 2.0 mL of 1 M HNO3 solution
was sufficient to remove 137mBa completely at a given
moment. When all the 137mBa was eluted from the 137Cs-
loaded generator, the 137mBa was allowed to grow until
secular equilibrium was established, so that the subsequent
fractions of the daughter nuclide could be recovered from
the parent nuclide adsorbed on the column by repeated
elution with a 1 M HNO3 solution. Thus the overall system
can be considered as a radionuclide generator. Fig. 5 shows
the decay curve of 137mBa eluted from TiP1 ion exchanger.
Conclusion
The designing of the conventional exchanger in nanoscale
range and its characterization has demonstrated its appli-
cability towards attaining a novel separation and confine-
ment of long-lived 137mBa from the long lived 137Cs of137Cs-137mBa radioactive equilibrated mixtures with
enhanced efficiency. It is of interest and importance to
fulfill the increasing demand for the radioactive waste
management for environmental protection and studies
related to nuclear medicines. The synthesis of the TiP
nanomaterial was attempted in a green chemical approach
without using any hazardous solvent or chemical.
Acknowledgments Financial assistance from UGC-DAE Center for
Scientific Research, Kolkata is gratefully acknowledged. The authors
are obliged to Dr. Suresh Valiyaveettil, Associate Professor, Materials
Research Laboratory (S5-01-03), Department of Chemistry, National
University of Singapore for his technical support in performing SEM
and EDS experiments. The authors are indented to Dr. P. Mitra,
Department of Physics, and B.U. for his cooperation in XRD analysis
and Dr. K. Bhattacharaya, BARC, Mumbai for TEM experiments.
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