M. Li, A.C. van Veen
AppliedCatalysisA,General550(2018)176–183
Fig. 1. Schematic diagram of experimental setup.
to high activity comparable to noble metals, but suffered rapid deac-
tivation because of Ni particle agglomeration and carbon deposition
[22]. MgO as basic support can enhance CO2 chemisorption [23]. In-
clusion of Al2O3 can increase surface area. Moreover, Ni supported on
Mg-Al mixed oxide have been shown to bear strong metal-support in-
teraction to suppress Ni sintering and exhibits enhanced catalytic sta-
bility in methane reforming reaction [24–26]. In this study, we for the
first time examine coupled reforming of methane with steam, carbon
dioxide and oxygen to produce syngas H2/CO = 2 at atmospheric
pressure over Mg-Al mixed oxide supported Ni catalyst and provide a
comparison of catalytic performance to bi-reforming. We also evaluate
carbon deposition in both reactions as one critical consideration for
catalyst stability.
plasma optical emission spectroscopy (ICP-OES, PerkinElmer 5300DV)
from the diluted extract in HNO3. Temperature programmed reduction
(TPR) was conducted in a quartz tube cell. The sample was heated in
84 cm3 min−1 5% v/v H2/Ar at 6 K min−1 to 1073 K and held for 1 h.
Hydrogen consumption was monitored by a thermal conductivity de-
tector (TCD). X-ray diffractograms (XRD) were recorded on a Bruker
D5005 X-ray diffractometer using Cu Kα radiation. Samples were
scanned at 0.02° step−1 over the range 30° ≤ 2θ ≤ 80° at ambient
temperature and the diffractograms identified against the JCPDS-ICDD
reference standards, i.e. Ni (04-0850), MgO (89-7746), γ-Al2O3 (10-
0425) and MgAl2O4 (77-1193). Nickel particle morphology (size and
shape) and carbon deposition was examined by Zeiss Supra 55VP field
emission scanning electron microscopy (SEM). Mean metal size (d) was
based on a count of up to 500 particles. Thermogravimetric-derivative
thermogravimetric analysis (TGA-DTG) of the samples post-reaction
was performed on a simultaneous thermal analyser (NETZSCH STA449)
by monitoring temporal mass with temperature. The samples (ca.
30 mg) were heated in 50 cm3 min−1 air to 1073 K (at 10 K min−1).
TPO-MS analysis of the spent catalysts was conducted in a quartz tube
by recording CO2 signal with time and temperature on a Pfeiffer
OMNIStar mass spectrometer. The samples (ca. 15 mg) were heated in
20 cm3 min−1 10% O2/Ar to 1073 K (at 5 K min−1).
2. Experimental
2.1. Materials and catalyst preparation
Mg-Al mixed oxide was prepared by co-precipitation of metal ni-
trates (Sigma Aldrich, > 98%) with aqueous ammonia (10% w/w,
Fisher) and ammonium carbonate (VWR Chemicals, 31.4% Assay NH3)
using flow synthesis. Aqueous nitrate salts (Mg2+ = 1.5 M, Mg/
Al = 3/1, 100 cm3) and a mixture (100 cm3) of ammonia (5 M) with
ammonium carbonate (0.25 M) was delivered separately via teflon line
2.3. Catalytic procedures
using
a
peristaltic pump (ISMATEC) at
a
fixed flow rate
(1.5 cm3 min−1), mixed in a tee (bore = 1.8 mm) and transported
continuously to 50 cm3 water. The suspension was stirred (500 rpm) at
353 K for 2 h. The solid obtained was separated by filtration, washed
with distilled water and dried at 393 K overnight. The dried sample was
calcined in air at 873 K (10 K min−1) for 4 h. Nickel (15% w/w) on Mg-
Al mixed oxide was prepared by deposition-precipitation using aqueous
ammonia. An aqueous solution of nickel nitrate (0.25 M, 100 cm3) and
ammonia (0.6 M, 100 cm3) was added to the support (8 g). The sus-
pension was stirred and heated to 353 K. The solid obtained was se-
parated by filtration, washed with distilled water and dried at 393 K
overnight. The catalyst precursor was sieved (ATM fine test sieves) to
60–200 mesh and activated at 10 K min−1 to 1073 K in
10 cm3 min−1 H2 (BOC, 99.99%) for characterisation.
Catalyst testing was conducted at atmospheric pressure
(973–1073 K), in situ after activation, in a continuous flow fixed bed
(alumina) tubular reactor (i.d. = 8 mm). The schematic diagram of the
reactor and gas analysis system is shown in Fig. 1. The catalyst
(5–30 mg) was mixed with ground quartz (60–200 mesh) and sand-
wiched between quartz wool. A layer of quartz particles was placed on
the top of quartz wool before the catalyst bed. Reaction temperature
was monitored by a thermocouple inserted in the catalyst bed. Water
was delivered to the reactor using a Shimadzu HPLC (LC-20AD) pump
and vaporized to steam in the upper part of the reactor. Reactant gases
(CH4, CO2 and/or O2, BOC, 99.99%), N2 (BOC, 99.99%) as internal
standard and Ar (BOC, 99.99%) as balance gas were introduced to re-
actor by Brooks mass flow controller (SLA5800 series) at (reactant) gas
hourly space velocity (GHSV) = 2 × 104–2 × 105 h−1. For all reac-
tions, the flow rate of methane was fixed at 9 cm3 min−1. The reactor
effluent was condensed in a gas sample cooler (Bühler) for subsequent
analysis using online gas chromatography (Shimadzu 2014) equipped
with a 0.5 cm3 sampling loop, thermal conductive detector (TCD) and
2.2. Catalyst characterisation
Nitrogen physisorption was performed on the Micromeritics ASAP
2020 system and total specific surface area (SSA) was calculated using
the standard BET method with pore volume obtained from BJH deso-
rption. Prior to analysis, samples were vacuumed and outgassed at
573 K for 1 h. Nickel content was measured by inductive coupled
flame ionization detector (FID), employing serial Hayesep
Q
(3.0 m × 2.1 mm i.d.) and Molecular Sieve 5A packed columns
(2.0 m × 2.1 mm i.d.). Data acquisition and manipulation were
177