172
C. Catrinescu et al. / Applied Catalysis A: General 489 (2015) 171–179
Table 1
ated corrosion and environmental challenges. Previous studies on
␣-pinene and limonene methoxylation have been principally per-
formed using zeolites [7] although clay-based catalysts can also
be used [8]. The alkoxylation of limonene over  zeolite and ion-
exchanged clays afforded good yields (around 85%) whereas the
methoxylation of pinene, over the same  zeolite, gave lower yields
also studied over acidic cation exchange resins [9] and sulphonic
acid-modified mesoporous silica [10]. However, more recent stud-
ies over poly(vinyl alcohol) containing sulfonic acid groups [11],
heteropolyacids immobilized on silica [12] and microporous and
mesoporous carbons [13] reported good selectivities, of ca. 60%, at
almost complete conversion.
Clay minerals, which are natural materials that cost significantly
less than the catalysts listed above, are versatile and environmen-
tally friendly catalysts that can be modified with relative ease to
promote a wide variety of organic reactions [14]. Beside the type of
clay, the nature, the locality and the extent of the isomorphic sub-
stitution strongly influences the layer charge of the clay and exerts
a major influence on the acidity and accessibility of the active sites.
These intrinsic characteristics of the clays, responsible for their
catalytic activity, can be readily improved using different meth-
Ni2+- and Al3+-exchanged montmorillonites, following appropri-
ate thermal activation procedures, are considered model Lewis and
Brønsted acids, respectively. The nature of the active sites has been
unequivocally determined using FT-IR spectra of adsorbed pyridine
[16] and verified by catalytic data.
Elemental composition for the purified host clays and for the Al3+ ion-exchanged
forms.
Clay
Chemical composition, % oxide
Na
Mg
Al
Si
K
Ca
Ti
Fe
SAz-1
AlSD
2.6
0.1
0.1
0.1
3.4
6.7
2.9
6.3
20.5
20.0
22.5
23.2
57.4
59.7
54.4
68.1
0.9
0.2
0.8
0.1
0.5
3.2
0.1
0.0
3.3
0.3
5.0
0.3
10.3
1.8
12.8
1.7
AlSAz-1
The nitrogen adsorption–desorption isotherms at −196 ◦C were
determined on an Autosorb iQ from Quantachrome Instruments,
equipped with turbomolecular pumps for high vacuum attain-
ment, using helium (for dead space calibration) and nitrogen of
99.999% purity. Prior to the adsorption measurements, all the sam-
ples were outgassed for 5 h at 200 ◦C, achieved using a heating rate
of 1 ◦C min−1
.
TG data were recorded on a Mettler TG50 thermobalance
equipped with a TC10A processor. Samples (∼10 mg) were trans-
ferred directly out of cyclohexylamine (CHA) vapour into the
thermobalance and the desorption traces were recorded at a
heating rate of 20 ◦C under a nitrogen flow of 25 cm3/min. Sam-
ples were conditioned for 15 min under flowing nitrogen to
reduce the amount of physisorbed CHA. Variable temperature dif-
fuse reflectance infrared Fourier transform spectra (VT-DRIFTS),
were recorded at room temperature, then at 25 ◦C increments
until 250 ◦C. Samples were held at a specific temperature for
15 min in a flow of dry nitrogen in a variable-temperature cell
(Graseby-Specac; maximum operating temperature 500 ◦C). The
spectrometer used was a Mattson Polaris operating at 4 cm−1 res-
olution and 256 scans.
In this work we report the synthesis of ␣-terpinyl methyl ether
via the methoxylation of ␣-pinene over clay catalysts. Based on
our recent results detailing the methoxylation of limonene [8], two
starting clays, with different compositions and properties, were
selected and these were activated by ion-exchange with Al3+ and
then thermally activated at 150 ◦C. This approach is known to afford
the maximum catalytic activity in Brønsted acid catalysed organic
reactions involving polar reagents.
2.3. Catalytic tests
␣-Pinene and n-decane (internal standard) received from Sigma
Aldrich were dried over anhydrous magnesium sulphate prior
to use. Anhydrous methanol was used as received from Sigma
Aldrich. The reactions were performed in a stirred 25 ml batch reac-
tor, equipped with a reflux condenser, under drying tube (CaCl2)
protection. Before the reaction, a known amount of catalyst was
thermally activated at 150 ◦C, in air, for 2 h in a vial. Before being
removed from the oven, the vials were stoppered and then placed in
a desiccator to cool and prevent rehydration. After being cooled at
room temperature (15 min) the catalyst powder was quickly trans-
ferred into the reaction vessel containing dry methanol, preheated
at the reaction temperature. The injection of pinene and n-decane
(internal standard) marked the start of the reaction. Samples were
taken periodically and the catalyst was removed by syringe filtra-
tion. The filter had no influence on the reaction products and no
further reaction took place during storage. The reaction products
were identified by GC–MS (Agilent 6890N/MSD GC–MS system) and
quantified by GC with FID, using a J&W Carbowax 20 M column and
n-decane as an internal standard.
In a separate test the effect of the larger amounts of water avail-
able in non-thermally activated clays was evaluated. These high
water content samples were stored in a desiccator over saturated
aqueous Ca(NO3)2 prior to their use as a catalyst.
Initial reaction rates were calculated utilizing the concentra-
tion versus time data collected during the first few minutes of
the reaction. During this initial time period, the concentration of
the reactants decreased almost linearly with time, and hence the
reaction rate i.e., the differential of the reactant concentration with
respect to time, was calculated from the slope of a linear fit to these
initial data.
2. Experimental
2.1. Catalyst preparation
in deionized water and the <2 m size fraction was collected by
centrifugation. The raw bentonite (SD) was collected from the Serra
de Dentro deposit (Porto Santo - Madeira Archipelago, Portugal)
and purified [17,18] to give the Na-exchanged form (NaSD). The
major impurities were removed by low speed centrifugation (6 min,
at 600 rpm), to obtain the <2 m size fraction, followed by the
removal of inorganic carbonates by incremental addition of a
0.5 M sodium acetate buffer until the clay suspension reached
pH 6.8. Then, the product was converted into the Na-exchanged
form using 1 M aqueous sodium chloride solution. Excess Cl− was
removed by dialysis and the solid clay was obtained after drying the
gel collected following centrifugation at 4500 rpm for 30 min.The
chemical composition for SAz-1 and NaSD is reported in Table 1.
SAz-1 and NaSD were treated three times with 0.3 M Al(NO3)3,
washed, dried and ground to give the AlSAz-1 and AlSD catalysts.
These samples were stored in a desiccator over saturated aqueous
Ca(NO3)2.
2.2. Characterization
The XRD patterns were recorded using a Shimadzu LabX
˚
XRD-6000 diffractometer with Cu K␣ radiation (ꢀ = 1.54184 A).