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A. Hamza et al. / Chinese Journal of Catalysis 36 (2015) 209–215
O
O
O
MAlP
O
2-n-pentyl-2-n-nonenal
Benzaldehyde
n-Heptanal
Jasminaldehyde
Scheme 1. Condensation reaction of n‐heptanal and benzaldehyde to form jasminaldehyde.
caustic liquid as the catalyst is not eco‐friendly due to envi‐
ronmental pollution and also has many other drawbacks such
as separation difficulties, corrosion of reactor lining and diffi‐
cult reagent handling. These drawbacks and difficulties can be
overcome by the use of fine‐tuned solid catalysts with good
efficiency. There have been reports on the use of solid catalysts
such as Mg‐Al mixed oxide [11], magnesium organo‐silicates
[12] and silica‐alumina [13] for this reaction. Climent et al. [14]
reported the superior activity of solid acid molecular sieves in
aldol and Knoevenagel condensation reactions, and found that
MCM‐41 was a better catalyst than microporous aluminosili‐
cates. Sudheesh et al. [15] investigated the application of a bi‐
opolymer chitosan as a solid catalyst for the condensation of
heptanal and benzaldehyde at 140 °C. Corma’s group [16]
studied the catalytic activity of various basic solids and com‐
pared their activity with that of amorphous AlP and ammo‐
nia‐treated AlP for the aldol condensation of n‐heptanal and
benzaldehyde. They reported the high activity of amorphous
AlP characterized by the presence of weak acidic sites along
with very weak basic sites. In their investigation, the catalyst
was prepared by the Lindblad method [17] in which ammoni‐
um phosphate was used as the phosphorous source instead of
phosphoric acid. In this method, the authors generated basic
sites on AlP by using ammonia. However, some of the catalyti‐
cally active acid sites may also be lost. As aldol condensation is
catalyzed by both acidic and basic materials, it would be inter‐
esting to evaluate the catalytic influence of these sites on aldol
condensation, and this was selected for the present study.
In the present work, we prepared AlP and MAlPs using
phosphoric acid as a phosphorous source and ammonium hy‐
droxide as precipitating agent. Precipitation was carried at ice
temperature to obtain particles with a smaller size and high
surface area, by Von Weimarn precipitation under relatively
super saturated conditions [18]. These materials were tested
for their catalytic activity in the synthesis of jasminaldehyde by
the condensation of n‐heptanal and benzaldehyde under reflux
conditions. An attempt was made to evaluate the struc‐
ture‐activity relationship of these catalysts.
dropwise addition of the ammonia solution for 20 min in order
to obtain particles with high surface areas. For example, pure
AlP was prepared by mixing Al(NO3)3·9H2O and 85% of H3PO4
in the desired molar ratio in 500 mL of de‐ionized water at ice
temperature to get a homogeneous solution. To the above clear
solution, 28% liquid ammonia was added dropwise from a bu‐
rette until the pH reached 7.5. The AlP gel thus obtained was
filtered, washed thoroughly with distilled water and dried at
120 °C in an air oven for 10 h. The dried samples were pow‐
dered and further calcined at 350 °C for 5 h.
The MAlPs were prepared by mixing Al(NO3)3·9H2O and the
metal salt in 500 mL of de‐ionized water followed by 85% of
H3PO4 in the desired molar ratio at ice temperature to get a
homogeneous solution. To the above clear solution, 28% liquid
ammonia was added dropwise from a burette until the pH
reached 7.5. The resulting precipitate was processed in a simi‐
lar procedure to that used for the AlP preparation. In the prep‐
aration of the MAlPs, the metal precursors used were the ni‐
trates of Cu, Zn, Cr, and Fe, and ceric ammonium nitrate and
zirconyl oxychloride for Ce and Zr. The phosphorous to total
metal molar ratio was kept 1:1 in all the catalysts with 2.5
mol% of the metal.
2.2. Material characterization
N2 adsorption‐desorption isotherms were determined using
a Micromeritics Tristar 3000 instrument. In a typical meas‐
urement, 0.2 g of the material (40–60 mesh) was degassed at
250 °C for 2 h in N2 flow. After cooling to room temperature,
the catalyst was loaded in the instrument for adsorption study
using N2 as adsorbate. The X‐ray diffraction (XRD) patterns of
the materials were analyzed using a Rigaku instrument (Japan)
with Cu Kα radiation. Fourier transform infrared (FT‐IR) spec‐
tra were recorded using a Thermo‐Scientific Nicolet IR‐380
instrument and the KBr pellet technique. Temperature‐pro‐
grammed desorption of ammonia (NH3‐TPD) experiments
were performed on a pulse Chemisorb instrument (Mi‐
cromeritics). In a typical experiment, 0.15 g of sieved particles
(40–60 mesh) was pretreated at 250 °C for 1 h in He flow,
cooled to room temperature and then 5% NH3/N2 gas was
passed through the bed for 30 min. After purging with He for
10 min to remove excess ammonia present on the surface,
NH3‐TPD was performed in the temperature range of 35–800
°C at a heating rate of 10 °C/min. The TCD signals were meas‐
ured after reaching 100 °C and a waiting time of 15 min to re‐
move physisorbed ammonia. The CO2‐TPD experiments were
carried out on the same instrument with a similar procedure as
described above using CO2 as the adsorbate.
2. Experimental
2.1. Material preparation
The pure and metal‐loaded AlPs were prepared by an earli‐
er reported co‐precipitation method [3] from the correspond‐
ing metal salts using 85% of H3PO4 as the phosphorous source
and 28% ammonia solution as the precipitating agent. All the
materials were prepared at ice temperature and with the