126
G.D. Yadav, S.O. Katole / Catalysis Today 237 (2014) 125–135
Sigma Aldrich, Mumbai, India); dodecyl amine, chlorosulfonic acid
(Spectrochem Ltd., Mumbai, India).
Nomenclature
A
AS
B
BS
E
ES
W
CA, CB
reactant species A–ethylene glycol
chemisorbed A
reactant species B–methyl 2-naphthyl ketone
chemisorbed B
product, 2-methyl-2-naphthyl-1, 3-dioxolane
chemisorbed product
20% (w/w) Cs2.5H0.5PW12O40/K-10 (designated as Cs-DTP/K-10)
was prepared by incipient wetness technique developed in our lab
[19–21] including UDCaT-4 [23–25] and UDCaT-5 [25,26].
water
concentration of A and B (mol/cm3)
CA0, CB0 initial concentration of A and B (mol/cm3)
CAS, CBS concentration of A and B on solid catalyst surface
(mol/g-cat)
2.3. Catalyst characterization
X-ray powder diffraction (XRD) was performed using a Bruker
AXS powder diffractometer D8 instrument, with Cu-K␣ (1.54 A)
CES, CWS concentration of E and W at solid catalyst surface
(mol/g-cat)
˚
radiation, to analyze the crystallinity, textural patterns of the
catalyst and the phase purity of synthesized catalysts. The XRD
patterns were recorded by scanning the catalyst sample within
the 2ꢀ range of 10–80◦. The specific surface area, pore volume
and pore diameter of each sample were obtained from nitrogen
adsorption–desorption isotherms measured in Micromeritics ASAP
2010 automated instrument and specific surface area, pore vol-
ume and pore diameter of all prepared catalysts were calculated
by using the BET model. Fourier transform infrared (FTIR) spectra
in the range of 400–4000 cm−1 were collected on a Perkin Elmer
Spectrophotometer using a sample disk of 5% catalyst weight in
KBr powder. Surface morphology of the catalyst was captured by
SEM (SU 30 microscope, JEOL, Japan). The sample was dried and
mounted on specimen studs and sputter coated with a thin film
of platinum to make the surface conducting. Temperature pro-
grammed desorption (TPD) was performed by using ammonia as
a probe molecule in Micromeritics AutoChem 2920 instrument. It
was carried out by heating 0.2 g of the catalyst at 573 K in dry air for
1 h and then purging it with helium for 0.5 h. The temperature was
decreased to 398 K under the flow of helium and then 0.5 ml NH3
pulses were supplied to the sample until no more uptake of NH3
was observed. NH3 was then desorbed in helium flow by increasing
the temperature to 573 K, with a heating rate of 10 K/min, and NH3
CS
Ct
concentration of vacant sites (mol/g-cat)
total concentration of sites (mol/g-cat)
rate of disappearance of A (mol/cm3 s)
equilibrium constant for adsorption of A on catalyst
surface (cm3/mol)
−rA
KA
KB
k
equilibrium constant for adsorption of B on catalyst
surface (cm3/mol)
surface reaction rate constant for forward reaction
(cm6 mol−1 min−1 g-cat−1
)
KP
KW
equilibrium constant for adsorption of P on catalyst
surface (cm3/mol)
equilibrium constant for adsorption of W on catalyst
surface (cm3/mol)
vacant site
S
t
w
XA
time
glycol [3]. The commercial process for acetals is catalyzed by strong
orange fragrance. However, the process is normally carried out
using homogeneous acid catalysts which need to be replaced. The
use of heteropolyacids [13–17] and their modified forms with
in situ generation of nano-catalysts [18–21] including different
supports such clays [13–21] and hexagonal mesoporous silica [22],
their characterization and applications have been deliberated in
some of our publications.
The current investigation deals with efficacy of different solid
acid catalysts for acetalization of ethylene glycol with methyl 2-
napthyl ketone to synthesize 2-methyl-2-napthyl-1,3-dioxolane. A
variety of catalysts were evaluated for their activity and selectiv-
ity. Use of modified heteropolyacid supported on acid treated K-10
clay as the most active and selective catalyst is discussed. Reaction
mechanism and kinetics are established.
2.4. Reaction procedure and analytical methods
ethylene glycol was carried out in a 100-ml glass reactor (5 cm
diam.) fitted with a Dean-Stark apparatus for continuous removal
of water during reaction with overhead stirring and water con-
denser (Fig. 1). The reactor was charged with methyl napthyl ketone
(0.10 mol), ethylene glycol (0.20 mol), toluene as solvent, and n-
decane as internal standard. A known catalyst loading was used
(0.02 g/cm3) in control experiments. The reaction mixture was
vigorously stirred at different reaction temperatures. The reac-
tion was continued until maximum conversion was obtained. The
analysis of reaction products was carried out using GC (Chemito
1000) equipped with a BPX-50 capillary column (length: 30 m, ID:
0.25 mm) and with FID detector. Confirmation of reaction products
was achieved by GC–MS (Perkin Elmer, Clarus 500) using the same
capillary column.
2. Experimental
2.1. Chemicals and catalysts
The sources of various chemicals were as follows: dodeca-
tungstophosphoric acid (DTP), cesium chloride, methanol, n-
decane, zirconium oxychloride, aluminum nitrate, ammonium
persulfate, ethanol (M/s s.d. Fine Chem. Ltd., Mumbai, India);
montmorillonite K-10 clay, tetraethyl orthosilicate (M/s. Fluka
Chemicals, Germany);ethylene glycol, methyl 2-napthyl ketone,
benzophenone, acetophenone, propylene glycol, toluene (M/s.
3. Results and discussion
Preliminary experiments suggested that the best catalyst was
20% (w/w) Cs-DTP/K-10 and its characterization is briefly presented
here including the used catalyst.