1
26
S. Lee et al. / Journal of Catalysis 365 (2018) 125–137
structures [25,26], carbon diffusion coating layers [27], as well as
solid acid supports [28–35]; and judicious combinations of these
approaches. However, despite considerable efforts over the last
decade, the direct synthesis of hydrogen peroxide remains a chal-
lenging reaction because the hydrogen peroxide yield under intrin-
sically safe and non-corrosive conditions is still unsatisfactory and
H
2
PdCl
water was mixed with a solution of the anionic metal precursor
(PdCl dissolved in 0.2 M HCl), and the mixed solution was stirred
4
[40–43]. Activated carbon (1 g) suspended in deionized
2
at 298 K for 2 h (Pd intake 5 wt%). After heating to 353 K, 0.5 M
NaOH solution was added to the suspension until the pH of the
mixed solution reached 12. After additional stirring for 2 h, a
reduction reaction was performed by bubbling hydrogen
(20 mL/min) at the same temperature for 2 h under vigorous stir-
ring. During these steps, the temperature of the suspension was
maintained at 353 K using a double-jacked reactor connected to
a circulator. At the end of the reduction, the catalyst was filtered
at room temperature, thoroughly washed with deionized water,
and dried overnight at 393 K.
the use of caustic additives and H
and safety issues [36,37].
2 2
/O mixtures causes corrosion
Herein, we propose an efficient catalyst design based on a selec-
tive adsorption deposition method to achieve high reaction perfor-
mance in the direct synthesis of hydrogen peroxide. The formation
of extremely small and monodispersed Pd nanoparticles on an acti-
vated carbon support was realized by the combination of the selec-
tive adsorption of metal precursor cations on the negatively charged
activated carbon surface and the homogeneous surface deposition of
palladium hydroxide by hydroxide ions that are slowly generated
upon urea decomposition. As will be discussed, the as-prepared
Pd/C catalyst showed superior reaction performance compared to
the Pd/C catalysts prepared by conventional method. The excep-
tional catalytic activity is comparable to that of previously reported
Pd catalysts supported on various carbon materials.
Moreover, by performing systematic characterizations and test
reactions, we elucidated the crucial role of the oxygen groups (par-
ticularly the carboxyl groups) of the activated carbon surface in the
catalytic performance. Most related studies focused on the changes
in the catalytic activity with respect to the different physicochem-
ical properties of various carbon materials [27,38,39]. We believe
that the systemically designed selective adsorption deposition
method can be extended to other catalyst designs that require
highly dispersed active metal sites.
The preparation of a Pd/C catalyst using the cationic palladium
3 4 3 2
precursor Pd(NH ) (NO ) was carried out by a modified selective
adsorption deposition method [44,45]. Activated carbon was sus-
pended in deionized water, and the suspension was adjusted to
3
pH 4 by the addition of HNO . After adding the tetraamminepalla-
dium(II) nitrate solution at 298 K, the mixed solution was stirred
for 2 h to allow the selective adsorption (Pd intake 5 wt%). After
the temperature was raised to 353 K, urea was added under vigor-
ous stirring. The pH of the resulting mixture gradually increased
and finally reached a constant value after 12–24 h; therefore, the
deposition procedure was continued for 24 h. The pH of the sus-
pension was monitored during this step, and the amount of urea
was adjusted to maintain the final pH at ca. 6.3. After the deposi-
tion, the slurry was filtered, thoroughly washed with deionized
water, and dried overnight at 393 K. The sample was reduced in
the presence of mixed N
473 K for 3 h (heating rate = 5 K/min).
2 2 2
/H gas (50 mol% H , 100 mL/min) at
2
.4. Characterization of the surface-modified activated carbon and
2
. Experimental
catalyst
2
.1. Chemicals
The textural properties of the surface-modified activated car-
bons, such as the specific surface area, pore volume, and pore
diameter, were determined by N adsorption using a BELSORP-
Max (BEL, Japan) at 77 K. Prior to adsorption, the samples were
degassed at 423 K overnight under vacuum. The distribution of
the oxygen-containing functional groups on the activated carbon
surface was determined by titration following Boehm’s method
Catalyst carrier grade activated carbon (Norit, surface area
2
3
2
1
007 m /g, pore volume 0.87 cm /g, pore diameter 3.47 nm) was
received from Carbot. Palladium chloride (99.9%) and tetraam-
minepalladium(II) nitrate solution (5.0 wt% as Pd) were supplied
by Strem-Chemicals. Cerium(IV) sulfate standard solution (0.25 N
in 2–3 N sulfuric acid), ferroin indicator (0.1 wt% solution in
water), sodium bromide (>99%), 1-decene (>97%), and heptane
[
46]. The temperature-dependent evolution of the decomposition
gases from an activated carbon domain was monitored by
temperature-programmed desorption-mass spectrometry (TPD-
Mass, BEL-CAT-Mass, Japan). Before the experiment, the samples
were dried using helium flowing at the rate of 100 mL/min at
(
(
(
(
(
99%) were purchased from Sigma-Aldrich. Hydrogen peroxide
34.5%), acetic acid (99.5%), nitric acid (60 wt%), hydrochloric acid
35–37%), sulfuric acid (96%), urea (99%), sodium hydroxide
98.0%), sodium carbonate anhydrous (99.5%), sodium bicarbonate
99%), and methanol (99.5%) were supplied by Samchun Chemicals
3
1
73 K for 2 h. The temperature of the samples was increased to
273 K at a ramping rate of 5 K/min, and the decomposition gases
in Korea. All the chemicals were used as-received without further
purification.
were detected using a mass spectrometer. Diffuse reflectance infra-
red Fourier transform spectra (DRIFTS) of the surface-modified
activated carbon were recorded using
a FT-IR spectrometer
2.2. Surface modification of the activated carbon support
(
Nicolet iS50 with DTGS detector, Thermo Fischer Scientific, USA)
equipped with a diffuse IR chamber (Pike Technology, USA).
UV–visible spectra were collected using a Hitachi U-2900 UV–Vis
spectrophotometer. Zeta potential measurements were carried
out in a wide pH range 2–12 using a zeta potential analyzer
For the introduction of oxygen-containing functional groups on
the surface, activated carbon was refluxed for 6 h in acid or acid/
oxidant solutions of different concentrations: 1 wt% HNO , 10 wt
HNO , and 10 wt% HNO /10 wt% H . After the surface modifi-
3
%
3
3
2 2
O
(
ELS-8000, Otsuka Electronics, Japan). The Pd content loaded on
cation, the resulting activated carbon was thoroughly washed with
water and dried in an oven at 383 K for 12 h. The samples were
stored in a desiccator under nitrogen before use.
the activated carbon was determined by inductively coupled
plasma atomic emission spectroscopy (ICP-AES) using a Perkin-
Elmer OPTIMA 7300 DV. For ICP analysis, palladium was extracted
3
using HNO /HCl mixture solution under microwave digestion. The
2
.3. Preparation of the Pd/C catalysts using anionic and cationic metal
Pd content on an activated carbon support was measured three
times and the average value was used. The oxygen/carbon atomic
ratio of the surface-modified activated carbon and the binding
energies of Pd in the Pd/C catalysts were determined by X-ray pho-
toelectron spectroscopy (MultiLab 2000, Thermo VG Scientific, UK)
precursors
The Pd/C catalyst was prepared via a well-known deposition-
precipitation method with the anionic palladium precursor