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A. Nau et al. / Applied Catalysis A: General 397 (2011) 103–111
The application of innovative carbon materials in this content is
The mass balance is checked for each analytical result obtained.
All results discussed below feature a deviation of less than 3%.
The modified residence time of MTBE was varied between 0.02
and 0.2 h gKat g−1 in order to visualize the catalytic performance
constant.
In order to classify the activated carbon vs. industrially available
catalysts for MTBE cleavage, the performance of a commercially
available amorphous alumina–silica (AAS) prepared according to
[13], was used. AAS is already applied for MTBE cleavage in indus-
trial scale.
In order to study the time-on-stream behavior of the catalyst
samples, a fixed bed reactor (L = 600 mm, di = 11 mm) divided into
the vaporizer zone (330 mm), the reaction zone (40 mm) and the
outlet (230 mm) was designed. 2.25 g of the catalyst sample was
diluted (1:1) with granular quartz. Again, MTBE was fed as a liq-
uid by a mass flow controller and the residence time was varied
between 0.2 and 0.04 h gKat g−1. The reaction was carried out at
498 K and 6 bar(g). The off-gas of the reactor was analyzed as
described above.
a new approach to improve the process performance and to better
understand the complex reaction system of MTBE cleavage. Carbon
materials have been used for decades in heterogeneous catalytic
reactions. They help to increase the rate and to control the selectiv-
ity of many chemical reactions [11]. Oxidative surface modification
of activated carbon allows the generation of new functional acidic
groups on the carbon surface, e.g., carboxyl, quinone or phenol
groups, in order to adjust the surface chemistry properties. The
functional groups can participate in redox reactions such as the oxi-
dation of SO2 to SO3 (SO2 removal from flue gas). Activated carbon
can also be used as catalyst for the synthesis of phosgene from CO
is superior suited as catalyst support for the industrial synthesis of
products like vinyl acetate than other oxidic supports because the
undesired polymerization of the vinyl monomers does not occur
[12].
It was the aim of the present study, to generate new catalyti-
cally active materials by oxidation of activated carbon shaped as
spheres by ozone, and apply those as catalysts for MTBE cleavage
into isobutene and methanol. In the following, the results about
the catalytic performance of the activated carbon materials are
presented.
2.3. Characterization methods
Structural properties of the catalysts applied for MTBE cleavage
in the present study are reported in Table 1. The amount of acid
sites was determined by NH3–TPD, the total surface area and the
average pore size were calculated applying the BET-method; the
external surface area and the total pore volume were determined
by the t-plot method.
Scanning electron microscopy (SEM) micrographs were
obtained using a Zeiss 962 microscope operating at 30 and 25 kV,
respectively.
2. Experimental
2.1. Oxidative treatment of the activated carbon
Ozone was used as oxidizing agent to modify the surface of a
commercial, spherical activated carbon (SAC) with an internal sur-
face area of 1306 m2 g−1 and a particle size of 0.5–0.6 mm (received
from CarboTechAC GmbH, Essen). Oxidation was carried out in a
stainless steel fixed bed reactor (45 mm × 60 mm × 60 mm) con-
nected with an IR spectrometer (FTS 175 C, BIORAD) to analyze
the gas phase (CO, CO2, O3, and H2O). The fixed bed reactor was
equipped with four heating cartridges (per 200 W) and a thermo-
couple. For the oxidation, the reactor was filled ten times with
550 mgof theactivated carbonSAC. Thesamplewas treated at333 K
with 4000 ppm (L L−1) ozone in a N2/O2 (1:1.3) stream for 60 min
(sample herein after called SAC60). Ozone was received from an
ozonizer (COM-SD-30, Anseros, Tuebingen).
Diffuse reflectance FT-IR spectra (DRIFTS, optical resolution
4 cm−1) were collected at room temperature with a FT-IR spectrom-
eter (FTS 175 C, BIORAD) equipped with a DRIFTS cell [14]. During
the spectra collection the DRIFT cell was flushed with 165 mL min−1
nitrogen. The untreated activated carbon (SAC) was used as ref-
erence material to highlight the changes due to the oxidation of
the material and to receive a straight baseline for the subsequent
simulation of the spectra. The characteristic IR absorptions of the
oxygen surface groups overlap in the IR spectrum. To differentiate
between the functional oxygen groups on the activated carbon the
ex situ DRIFT spectra were simulated with single Gauss functions in
the region between 1700 and 1850 cm−1. The simulated spectrum
results from the superposition of the used four single Gauss func-
tions. The fit is optimized by varying the parameters half-width,
peak position and integral value of each single Gauss function and
thereby minimizing the sum of least squares.
The temperature programmed desorption experiments (TPDs)
were carried out in the reactor mentioned above. 250 mg of each
sample (SAC, SAC60, SACar and SAC60ar, whereas ‘ar’ indicates the
sample after the use as catalyst for MTBE cleavage in the paralleled
tube reactor experiments) were heated up to 773 K in a N2 flow
(165 mL min−1) at a heating rate of 10 K min−1. The end tempera-
ture was held for half an hour. The evolved gases were analyzed by
an attached IR gas cell. The elemental analysis of the carbon mate-
rial for C and H was carried out with a VarioEL analyzer, O was
calculated as difference to 100%.
2.2. Catalytic performance
The catalytic tests were carried out in a fully automated appara-
tus with paralleled tube reactors (L = 80 mm, di = 8 mm) at 498 K
and 6 bar(g). 0.2 g of catalyst was loaded to a reactor. The cat-
alyst samples were diluted (1:5) with granular quartz in order
to ensure an isothermal temperature distribution in the catalyst
bed. In one test series, two reactors were always loaded with
the same catalyst sample. The redundant use of the catalyst sam-
ples allows the verification of the reproducibility of the catalyst
performance.
MTBE was dosed as a liquid by a mass flow controller and was
vaporized in a tubular reactor (L = 200 mm, di = 24 mm) consisting
of 2 mm glass beads. Subsequently, the outlet gas was divided into
identical parallel streams, which were led into the paralleled tube
reactors, respectively. Via a selecting valve, the off-gas of one reac-
tor was led to a gas chromatograph that was connected online
(HP 6890). The streams of the other reactors were collected and
disposed of according to the safety regulations.
3. Results and discussion
The gas chromatograph was equipped with a flame ionization
detector and in series connected columns HP-1 methylsiloxane and
LowOx, which allow the separation of all known products of the
MTBE cleavage in 15 min.
3.1. Catalytic performance
Isobutene and methanol are the main products of the MTBE
cleavage over all tested catalysts. For AAS the selectivity towards