J. He et al. / Journal of Catalysis 309 (2014) 362–375
363
Water comprises typically 30 wt.% of raw bio-oil and is a suit-
able solvent for an upgrading process. Methanol has been success-
fully used for lignocellulose conversion especially for lignin
liquefaction [8], and nonpolar solvents such as hexadecane and tol-
uene have been employed for related hydrotreating of synthetic
crude coal and oil shale [9,10]. The solvent for hydrodeoxygenation
should, therefore, (i) be stable with respect to the process temper-
ature, pressure, and catalyst, (ii) hold reactants and intermediates
in solution; (iii) dissolve and transport H2, and (iv) dissipate the
heat of the highly exothermic reactions.
isotherm to zero H2 pressure, and this value was used to calculate
the dispersion of metal on supports.
2.3.3. Transmission electron microscopy (TEM)
TEM images were measured on a JEM-2010 Jeol transmission
electron microscope operating at 120 kV. Prior to the measure-
ments, catalyst was ground, suspended in ethanol, and dispersed
by ultrasonic treatment. The dispersion was dropped on a copper
grid-supported carbon film. The average cluster size was calculated
by counting 300 Pd particles.
In this contribution, we report the detailed kinetics of individual
steps for phenol hydrodeoxygenation with Pd/C or HZSM-5 in
water, methanol, and hexadecane. The turnover frequencies (TOFs)
and apparent activation energies for individual steps are explored.
The relationships between the chemical nature of the solvents and
the interactions at the gas–liquid–solid interfaces are investigated
in order to understand the fundamental differences between the
reactions occurring in media with differing properties. The sol-
vent–catalyst, solvent–reactant, and reactant–catalyst interactions
and their influence on the activity are discussed in this work as
well. In situ liquid-phase IR spectroscopy is employed to monitor
the concentrations of the reactants and products during individual
reaction steps in water to obtain kinetic information.
2.3.4. Temperature-programmed desorption (TPD)
HZSM-5 was activated in flowing He at 623 K for 1 h using a
heating rate of 5 K minꢁ1 from room temperature to 623 K. NH3
was adsorbed by adding 10 vol.% to the He carrier gas (total flow
30 mL minꢁ1) at 423 K. The sample was purged with He for 2 h
to remove physisorbed molecules. For TPD, the sample was heated
in He at a rate of 10 K minꢁ1 from 373 K to 1033 K for NH3 desorp-
tion. The species desorbing was monitored by mass spectrometry
(Balzers QME 200). For quantification, a reference material with
known acid site concentration (HZSM-5 with Si/Al = 45) was used.
2.3.5. IR spectra of adsorbed pyridine
IR spectroscopy with pyridine as probe molecule was used to
determine the acid site concentrations and distributions. The IR
spectra were measured with a PerkinElmer 2000 spectrometer
operated at a resolution of 4 cmꢁ1. The sample was activated at
723 K for 2 h in vacuum, and a background spectrum was recorded
after the temperature decreased to 423 K. The activated sample
was exposed to pyridine vapor (1.0 ꢀ 10ꢁ5 MPa) at 423 K for
0.5 h. After removing physisorbed pyridine by outgassing at
423 K for 0.5 h, the spectra were recorded.
2. Experimental section
2.1. Chemicals
All chemicals were provided from commercial suppliers: phenol
(Sigma–Aldrich, 99% GC assay), cyclohexene (Sigma–Aldrich, 99%
GC assay), cyclohexanol (Sigma–Aldrich, 99% GC assay), cyclohex-
anone (Sigma–Aldrich, P99.5%, GC assay), ethyl acetate (Sigma–
Aldrich, P99.5%, GC assay), methanol (Sigma–Aldrich, P99.93%,
GC assay), hexadecane (Merck, >99%, GC assay), toluene (Sigma–
Aldrich, P99.5%, GC assay), hydrogen (Westfalen AG,
99.999 vol.%), nitrogen (Westfalen AG, 99.999 vol.%), synthetic air
(Westfalen AG, 99.999 vol.%), and ultra water system (EASYpure
2.3.6. Atomic absorption spectroscopy (AAS)
A UNICAM 939 AA-Spectrometer was used to determine the
concentration of noble metals in the carbon supported catalyst. Be-
fore measurement, 20–40 mg of the sample was dissolved in a
mixture of 1.0 mL of 37 wt.% hydrochloric acid and 1.0 mL of
65 wt.% nitric acid at the boiling point of the mixture.
II, Resistivity: 18.2 MX cm).
2.2. Catalysts
2.4. Measurement of catalytic reactions
The Pd/C was obtained from Sigma–Aldrich (Sigma–Aldrich,
1 wt.% Pd), and HZSM-5 (Si/Al = 45) was supplied by Clariant AG.
They were used without further treatment.
2.4.1. Individual steps of phenol hydrodeoxygenation with Pd/C and
HZSM-5 catalysts
The hydrodeoxygenation of phenol to cyclohexane includes four
steps: Step 1: phenol hydrogenation to cyclohexanone on Pd/C, Step
2: cyclohexanone hydrogenation to cyclohexanol on Pd/C, Step 3:
cyclohexanol dehydration to cyclohexene on HZSM-5, and Step 4:
cyclohexene hydrogenation to cyclohexane on Pd/C. Exploration of
reaction rates was carried out at 473 K in three solvents (water,
methanol, and hexadecane). Apparent activation energies were
calculated from rates measured at 433, 453, 473, and 493 K.
The turnover frequencies (TOFs) defining initial reaction rates
were expressed as per mole of converted reactant on per mole of
surface Pd atom (or per mole of Brönsted acid site) per hour at con-
versions lower than 15% (except for the very fast cyclohexene
hydrogenation) at 473 K in the presence of 4 MPa H2. To control
conversions in this range, the ratios of reactant to catalyst have
been manipulated (Figs. 2, 4, 5, 7). H2 gas was introduced to the
reactor at the reaction temperature of 473 K in order to make the
conversion data start from zero at t = 0.
2.3. Catalyst characterization
2.3.1. Specific BET surface area and pore diameters
The surface areas and pore diameters were determined by N2
adsorption. The N2 adsorption was carried out at 77 K on a PMI
automated BET sorptometer. Prior to the measurements, the sam-
ples were outgassed at 523 K for 20 h. The specific surface areas
and micropore and mesopore distributions were calculated based
on the BET and BJH models.
2.3.2. H2 chemisorption
The Pd supported on activated carbon was first reduced at 733 K
in presence of 0.1 MPa H2 for 4 h before measurement. The reduced
catalyst was activated at 733 K for 1 h in vacuum and then cooled
to 313 K. The H2 chemisorption and physisorption were subse-
quently measured in a pressure range from 1 kPa to 40 kPa. Then,
the physisorbed H2 was removed by outgassing the sample at the
same temperature for 1 h. A second adsorption isotherm (physi-
sorption) was measured. The concentration of chemisorbed hydro-
gen on the metal was determined by extrapolating the differential
2.4.1.1. Kinetics of individual steps of phenol hydrodeoxygenation in
water. The reaction conditions for the TOF measurements are re-
ported as footnotes in the corresponding figures. In a typical exper-
iment exemplified by Step 1 of phenol hydrogenation, phenol