R. Kuma, et al.
Applied Catalysis A, General 595 (2020) 117496
Fig. 1. Catalytic dioxin decomposition process in municipal waste incineration plants.
(
EXAFS) spectroscopy. XANES spectroscopy provides information re-
fixed on double-sided carbon tape on an Al stub. The spectra were re-
−
6
garding the local geometry around the absorbing atom and its oxidation
state, whereas EXAFS spectroscopy is a powerful technique for ob-
taining direct structural information.
corded at 25 °C under a pressure of < 1.33 × 10
Pa using an AlKα
radiation source with a beam diameter of 100 μm and a pass energy of
140 eV. The binding energies were calibrated to the C1s peak.
The V K-edge XANES measurements were performed at the BL-9C
beamline of the Photon Factory (KEK-PF). The sample masses were
calculated to adjust the height of edge jump and mixed with boron
nitride (catalyst sample:boron nitride = 1:11) before being pressed into
an in situ cell to form a self-supporting disc with a diameter of 7 mm.
Nitrogen gas was fed into the in situ cell and the data were collected in
transmission mode using a Si(1 1 1) monochromator at ambient tem-
perature (25 °C) or at 200 °C. The XANES spectra were analyzed with
the ATHENA software.
2
. Experimental
2
.1. Catalyst preparation
TSM mixed oxides were prepared by a coprecipitation method, as
described in our previous report [17], using titanium sulfate solution
70 g/L TiO , Tayca Corp.), silica sol (30 % SiO , Nissan Chemical
Corp.), ammonium molybdate (Taiyo Koko Co., Ltd.). TiO –SiO (TS)
and TiO were prepared similarly. The SiO content in all TS and TSM
samples was fixed to 7 wt%.
For comparison, MoO /TS (Mo/TS) and MoO
were prepared by an incipient wetness method. Ammonium molybdate
1.36 g) was mixed with monoethanol amine (0.55 g, Nippon Shokubai)
and deionized water (5 g) at approximately 25 °C, and then the TS or
TiO powders (10 g) were impregnated with this molybdenum solution
(
2
2
2
2
The Mo K-edge XAFS measurements were carried out at the BL01B1
beamline of SPring-8 (Japan Synchrotron Radiation Research Institute)
in transmission mode. A double-crystal Si(1 1 1) monochromator was
used. The sample masses were calculated to adjust the height of edge
jump and mixed with boron nitride (catalyst sample:boron ni-
tride = 2:1). The Ti K-edge XAFS measurements were performed at the
BL-9C beamline of the KEK-PF using a Si(1 1 1) monochromator. The
samples were mixed with boron nitride at a sample:boron nitride ratio
of 1:3. For the Mo and Ti K-edge XAFS measurements, each samples
mixed with boron nitride was pressed to form a self-supporting disc
with a diameter of 10 mm, and the XAFS spectra were recorded at
ambient temperature (25 °C) and pressure. The Mo and Ti K-edge XAFS
data were analyzed using the REX2000 software (Rigaku Co.).
The V, Mo and Ti K-edge XANES spectra were normalized to the
edge jump, and the first derivative of the near-edge region was em-
2
2
3
3 2 2
/TiO (Mo/TiO )
(
2
and mixed well. The conditions and procedure for drying and calcina-
tion were the same as those employed for the TSM samples. The no-
menclature used for the various samples is “XMo/TiO
2
”, “XMo/TS”, and
“
XTSM”, where X represents the molybdenum content calculated as the
weight percentage of MoO
between 5 and to 30 wt%, and those in Mo/TS and Mo/TiO
3
3
. The molybdenum content in TSM ranged
were 10 or
0 wt%. Honeycomb-shaped vanadium catalysts were prepared in ac-
2
cordance with our previous report [17]. Ammonium metavanadate was
mixed with an aqueous solution of monoethanol amine and oxalic acid
at approximately 25 °C. The TSM powders and the vanadium solution
obtained above were mixed and kneaded under the continuous addition
of water. The resultant blend was fed into an extrusion molding device
and molded into a honeycomb monolith. After drying at 60 °C and then
calcining at 450 °C for 5 h in air, a honeycomb catalyst with an outer
diameter of 50 mm and a pitch of 3.2 mm was obtained.
3
ployed for determination of the edge absorption energy. The k -
weighted EXAFS oscillations of the Mo and Ti K-edges were extracted
3
using spline smoothing. Subsequently, the filtered k -weighted χ(k) was
−
1
Fourier transformed into R space (k range: 3–13 Å ) using a Hanning
function window [19].
2.3. Catalytic activity measurements
V
2
O
5
–MoO
V10Mo/TiO ) were also prepared by the same method, with ammo-
nium molybdate added to the mixed aqueous solution of ammonium
metavanadate, monoethanol amine, and oxalic acid. V /TiO –SiO
V/TS) was prepared by the same method as V10Mo/TS, except that no
ammonium molybdate was added. The loading amount of vanadium on
all the catalysts in the present study was fixed at 8 wt% V
3
/TiO
2
–SiO
2
(V10Mo/TS)
and
2 5 3 2
V O –MoO /TiO
(
2
Oxidative degradation tests using o-chlorotoluene were conducted
in a U-shaped tubular stainless-steel reactor with an inner diameter of
.8 cm. The honeycomb catalyst to be tested was cut into 25 cells and
loaded into the reactor. A reaction gas mixture consisting of 100 ppm o-
chlorotoluene, 10 % O , and 10 % H O by volume and balanced with N
was supplied to the reactor. o-Chlorotoluene and H O were supplied
using two glass saturators controlled at 31 °C for o-chlorotoluene and
2
O
5
2
2
3
(
2
2
2
2 5
O .
2
2
.2. Characterization of the catalysts
3
4
2
6 °C for H O. The reaction gas flow rate was 0.6 Nm /h and the gas
−1
hourly space velocity GHSV was 6000 h . The reaction was carried out
overnight (∼15 h) at each temperature, and the o-chlorotoluene con-
centrations before and after the reaction were analyzed by gas chro-
matography using a Shimadzu GC-14B instrument equipped with a
Chromosorb column controlled at 140 °C. The concentrations were
analyzed 3–5 times every 20 min, and after confirming the value to be
almost constant, the average value was used for decomposition rate
The X-ray diffraction (XRD) measurements of the support materials
and catalysts were carried out using a Rigaku SmartLab diffractometer
with a CuK radiation source under ambient conditions. The specific
surface areas of the samples were evaluated by the
Brunauer–Emmett–Teller (BET) method using a Mountech Macsorb
α
Model 1210 apparatus. The samples were degassed in flowing N
00 °C for 60 min.
X-ray photoelectron spectroscopy (XPS) spectra were obtained using
a ULVAC PHI Quantera SXM instrument. The sample powders were
2
at
2
calculations. The CO and CO
2
concentrations in the gas were measured
using a Horiba PG-250 gas analyzer.
2