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F.J. Urbano et al. / Journal of Catalysis 268 (2009) 79–88
However, a recent study revealed that the catalytic activity in
trimethylborate) or alkaline-earth metal precursor (N for the
nitrate).
the MPV reaction decreases with increasing calcination tempera-
ture (i.e. with increasing loss of surface hydroxyl groups) in hy-
drous zirconia; this underlines the significance of proton
(Bronsted) sites in the process [11,10]. In any case, the presence
of very strong acid sites appears to reduce the selectivity via side
reactions [10,11]. In this respect, surface-modifying MgO with
chloroform has been found to seemingly block the Lewis acid sites
leading to poisoning of the catalyst and producing acid enough sur-
face OH groups (viz. Bronsted acid sites) for the reaction [19–21].
The loss of selectivity by effect of the reduction of the C@C dou-
2.2. Catalyst characterization
Gels were subjected to thermogravimetric and differential ther-
mal analysis on a Setaram Setsys 12 system, using Air at 40 mL/min
as carrier gas,
a-Al2O3 as reference material and a Pt/Pt–Rh(10%)
thermocouple. The heating rate was 10 °C/min and the tempera-
ture range 30–800 °C. The amount of gel used in each test was
ca. 17 mg.
ble bond has been ascribed to adsorption of the
carbonyl compound via the above-mentioned double bond fa-
voured by the presence of strong Lewis acids [8].
a
,b-unsaturated
The elemental analysis of the catalysts was performed on a Per-
kin–Elmer ELAN DRC-e ICP-MS instrument following digestion of
the samples in a 1:1:1 mixture of HF, HNO3 and H2O, and dilution
in 3% HNO3. Calibration samples were prepared from appropriate
atomic spectroscopy standards (PE Pure Plus, Perkin–Elmer) in
HNO3 (10 lg/mL of each metal). Calibration curves were con-
structed over the concentration range 1–100 ppb and the results
were included for a blank.
The textural properties of the solids were determined from
nitrogen adsorption–desorption isotherms obtained at liquid nitro-
gen temperature on a Micromeritics ASAP-2010 instrument. All
samples were degassed to 0.1 Pa at 110 °C prior to measurement.
Surface areas were calculated by using the Brunauer–Emmett–
Teller (BET) method [38], while pore size distribution (PSD), mean
pore diameter (DBJH) and cumulative pore volume (VBJH) were all
determined with the Barrett–Joyner–Halenda (BJH) method [39];
the adsorption branch, the amount of cylindrical pores open on
one end only and the adsorbed layer thickness were calculated
using the Halsey method.
Zirconia has proved a highly effective choice among heteroge-
neous catalysts used in the MPV reaction [11]. Zirconium oxide is
a solid with a high thermal stability and corrosion resistance in
addition to a strong amphoteric character [22]. Its textural and
acid–base properties depend largely on its synthetic procedure
and calcination temperature. Adjusting its acid–base properties is
possible by modifying its surface with sulphate ions [23–25], phos-
phate ions [26] and mixtures of other oxides; this has proved a
highly effective method for tailoring the activity of zirconia to-
wards many organic processes. Boron oxide is one of the most
widely used compounds for altering the textural and acid–base
properties of metal oxides such as Al2O3 [27], AlPO4 [28], TiO2
[29], ZrO2 [30,31] and MgO [32], which have their acid sites grown
at the expense of basic sites. On the other hand, the presence of
alkaline-earth metals in metal oxides and mixed oxides has been
found to endow the final catalyst with a basic character [33–37].
This piece of research deals with the selective reduction of cin-
namaldehyde by hydrogen transfer from 2-propanol in the pres-
ence of various solids consisting of ZrO2 in pure form or modified
to alter its acid (ZrO2–B2O3) or basic properties (ZrO2–alkaline-
earth metal). Altering the surface chemical properties of the start-
ing ZrO2 allowed us to examine the influence of acid (Bronsted vs.
Lewis) sites and basic sites on activity and selectivity in the selec-
X-ray diffraction patterns were obtained on a Siemens D5000
diffractometer equipped with a graphite monochromator and
using Cu K radiation. The 2h angle was scanned from 5° to 85°
a
with a step size of 0.02°. The average diameter of the zirconia crys-
tallites, d, was calculated from the full width at half maximum
(FWHM) of the X-ray reflection at 2h = 30.3 (tetragonal phase),
using the Scherrer equation.
tive reduction of
gen transfer from 2-propanol.
a
,b-unsaturated carbonyl compounds by hydro-
FT-Raman spectra were obtained on a Perkin–Elmer 2000 NIR
FT-Raman system equipped with a diode-pumped NdYAG laser
(9394.69 cmꢀ1) that was operated at 300 mW laser power and a
resolution of 4 cmꢀ1 throughout the 3500–200 cmꢀ1 range in order
to gather 64 scans.
2. Experimental
Surface acidity in the catalysts was determined from the FT-Ra-
man spectra for chemisorbed pyridine. The most sensitive Raman
2.1. Catalyst synthesis
vibration of pyridine is its symmetric ring breathing (mCCN) (vs,
The catalysts were obtained by thermal treatment of a hydroxy-
gel prepared by alkaline hydrolysis of the corresponding zirconium
precursors: zirconyl chloride (Merck) and zirconium propoxide
(Fluka); boron (boric acid and trimethylborate from Fluka); and
the alkaline-earth metals (magnesium, calcium, strontium and bar-
ium carbonates from Merck). The proportions of each other were
calculated for an atomic ratio Zr/B = 10 or Zr/alkaline-earth = 13
in the final catalyst.
v1, A1), which appears at 991 cmꢀ1 in liquid pyridine. The interac-
tion of pyridine with acid sites induces a shift of this band to a
higher wavenumber. Therefore, the position of the skeletal vibra-
tion band can be used to detect interactions between pyridine
and protonic weak acid sites through hydrogen bonds (996–
1008 cmꢀ1
) or its chemisorption at strong Bronsted (1007–
1015 cmꢀ1) and/or Lewis acid sites (1018–1028 cmꢀ1) on a solid
surface [40–42].
Gels were obtained by adding 5 M ammonia to a solution of
each precursor in 250 mL of milliQ water up to pH 10 under vigor-
ous stirring. The mixture was then refluxed for 24 h, vacuum-fil-
tered and washed with milliQ water to remove all chloride ions
as checked with the AgNO3 test. The solid residue was air-dried
for 24 h, suspended in isopropanol, rotated for 5 h and the solvent
removed by vacuum evaporation at 50 °C. The final texture of solid
thus obtained was a fine dust instead of a rock type solid. The
resulting hydroxygels were vacuum-calcined at 400 °C for 5 h to
obtain the final catalysts.
Chemisorbed pyridine FT-Raman measurements were made in
a Ventacon H4 environmental cell coupled to the FT-Raman instru-
ment. A nitrogen stream at 50 mL/min was saturated with pyridine
at room temperature and then flowed through a catalytic bed at
50 °C for 1 h. Then, physisorbed pyridine was removed by flowing
nitrogen at 40 mL/min until complete disappearance of the peak
for physisorbed pyridine at 991 cmꢀ1. Spectra were recorded using
a resolution of 4 cmꢀ1, a laser power of 300 mW and 64 accumula-
tions. The spectra obtained after clean-up were subsequently pro-
cessed with the software PeakFit v. 4.11 in order to determine the
components for physisorbed and chemisorbed pyridine in their
three variants (hydrogen-bonding interactions, Bronsted sites and
Lewis sites).
The name of each catalyst includes the elements forming the so-
lid and information about the zirconium precursor (O for Zr oxy-
chloride and P for Zr propoxide), boron (A for boric acid and T for