A. Takagaki, et al.
Applied Catalysis A, General 608 (2020) 117843
oxidized boron species (BOx) on the BN surface are believed to be re-
sponsible for the oxidation activity of this material [25]. The surface
functionalization of BN also permits the use of this compound as a
photocatalyst [26] or a solid base catalyst [27,28], and theoretical
calculations have indicated that the surface functionalization of BN
sheets with hydroxyl or amino groups decreases its bandgap [29]. This
has been confirmed experimentally and has been shown to increase the
photocatalytic activity of BN during the hydrogen evolution reaction
(BELSORP-max-32 and BELLSORP mini-II, Microtrac-BEL). Each sample
was pretreated by heating under vacuum at 473 K for 2 h prior to
analysis. CO adsorption was also determined at 298 K to assess the
2
micropores in the samples. The morphologies of the materials were
examined using scanning electron microscopy (SEM, JSM-7900F, JEOL)
and transmission electron microscopy (TEM, JEM-ARM200, JEOL). The
elemental analysis of the materials was investigated using energy dis-
N
persive X-ray spectroscopy (EDS, X-Max 80, OXFORD).
[
26]. These functional groups can also be generated on BN surfaces by
The structures of the sample were investigated by solid-state NMR
spectroscopy, XAFS analysis, and X-ray photoelectron spectroscopy.
ball-milling and can serve as active sites for various liquid phase base-
catalyzed reactions [27,28].
1
1
Boron-11 magic-angle spinning ( B MAS) NMR spectra were acquired
with a Bruker Avance III HD 600WB spectrometer operating at a fre-
quency of 192.63 MHz. A Bruker MAS probe head was used with a
zirconia rotor having an outer diameter of 4 mm. The measurement was
The surface functionalization and exposed surface area of BN both
play crucial roles in its utilization as a heterogeneous catalyst. Porous
BN having high surface areas can be synthesized via a pyrolysis method.
A variety of porous BN, including mesoporous BN using amphiphilic
block copolymers, have been reported [30]. In the present study,
porous BN samples were fabricated via a pyrolysis method in con-
1
1
1
performed at room temperature with a spinning rate of 12 kHz. The
spectra were obtained with a single pulse sequence combined with
B
H
high power decoupling during signal acquisition. The flip angle of the
pulse and the recycle delay were π/8 for solution and 10 s, respectively.
The shift was expressed with respect to neat boron trifluoride diethyl
junction with various NH flow rates and subsequently examined as
3
solid base catalysts. Analyses of the surface structures, as well as the
bulk structures of these materials, were carried out using a variety of
techniques, including Fourier transform infrared spectroscopy (FTIR), B
3
etherate (CF ·(C
2
H
5
)
2
O) by setting the NaBH signal acquired while
4
spinning at 8 kHz to −42.00 ppm. B K-edge XAFS spectra were ob-
tained at the BL7A beamline of the Photon Factory at the Institute of
Materials Structure Science, High-Energy Accelerator Research
Organization (KEK-IMSS-PF). The spectra were collected using the total
electron yield method with samples mounted on carbon tape, and all
1
1
K-edge X-ray absorption fine structure (XAFS) analysis, and B solid-
state nuclear magnetic resonance (NMR) spectroscopy. A post-treat-
ment involving washing of the material, as opposed to the actual
synthesis conditions, was found to significantly improve the solid base
activity of this BN during the nitroaldol reaction. Specifically, this post-
treatment increased the yield by a factor of ten, even though X-ray
diffraction (XRD) and FTIR analyses did not indicate any changes in the
samples. In contrast, XAFS and solid-state NMR spectra indicated the
removal of BOx species after washing, followed by an increased surface
area and the emergence of micropores. These results clearly demon-
strated that the post-treatment exposed active sites on the BN surface by
removing BOx species, resulting in an enhanced solid base activity. It
should be noted that not BOx species but amino groups were active sites
for the base-catalyzed reaction while BOx species are considered to be
active sites for the oxidation reaction.
spectra were calibrated with reference to the B
2
O peak at 194.0 eV.
3
The oxidation state of elements over the surface was analyzed by XPS
(KRATOS Ultra 2, Shimadzu). The binding energies in each measure-
ment were referenced to the core level of the C1s peak (284.8 eV).
The solid base strength of the sample was determined by acquiring
FTIR spectra following CHCl adsorption, employing a mercury cad-
3
−1
mium telluride detector with a resolution of 4 cm . The sample was
pressed into a disk with a radius of 1.0 cm without KBr and pretreated
in the measurement cell at 473 K under vacuum for 1 h. The sample was
then cooled to 303 K, and a spectrum was recorded. Following this,
gaseous CHCl
3
was introduced into the cell, and the sample was ex-
posed to a saturated CHCl
3
atmosphere for 30 min. Following the re-
2
. Experimental
moval of CHCl from the cell over a span of 30 min, the spectrum of the
3
sample was acquired, and a difference spectrum was obtained by sub-
2.1. Catalyst preparation
tracting the spectrum of the original material.
The BN samples were synthesized using boric acid (Kishida, 99.5 %)
2.3. Nitroaldol reaction
and hexamethylenetetramine (HMTA) (Wako, 99.0 %) according to a
literature procedure [31]. Briefly, 20 mmol of boric acid and 40 mmol
of HMTA were dissolved in 100 mL of water. After evaporating the
solution, the resulting white precursor powder was transferred to an
The catalytic activity of each material as a solid base was de-
termined using the nitroaldol reaction. Reactions were conducted using
50 mg of the catalyst in 2 mL of a toluene solution containing 60.5 μL of
p-methoxybenzaldehyde (0.5 mmol), 68.0 μL of nitromethane
(1.25 mmol) and 19.5 μL of n-decane (0.1 mmol) in a glass reactor
vessel (ACE glass). The reaction was performed at 373 K for 8 h in an oil
bath under stirring. Aliquots of the solution were removed using a
syringe and analyzed by gas chromatography (GC) with a flame ioni-
zation detector (GC-2014, DB-1MS column, Shimadzu). For the quan-
tification of the reactant and products, n-decane was used as an internal
standard, and each calibration curve was made in advance. For the
qualification of products, gas chromatography-mass spectrometry
alumina boat and heated at 1273 K for 3 h in an NH flow (50, 100 or
3
3
−1
1
50 cm (NTP) min ). The brown powder obtained from this proce-
dure was ground using a mortar, then washed by stirring in water
overnight at 333 K. The sample was subsequently collected by cen-
trifugation or filtration, after which it was dried at 353 K in an oven.
The synthesized BN is denoted herein as BNX-Y, where X represents the
3
−1
flow rate of NH (50, 100 or 150 cm (NTP) min ), and Y denotes the
3
method used to collect the sample (no Y: without washing, C: cen-
trifugation and F: filtration).
(
GC–MS, GCMS-QP2010Ultra, Shimadzu) was used. The measurement
2
.2. Characterization
error was within 5%. For example, we tested the activity of BN50-F
three times in which a product yield was 32.0, 31.6, and 32.3 %. This
difference is included in the significant figures. For the recyclability
test, the catalysts were collected by centrifugation at 3000 rpm, washed
with 10 mL of toluene three times, dried overnight, and reused for
further reactions.
The crystal structure of the BN was investigated by XRD (RINT-
2
500HLR+, Rigaku) with Cu Kα radiation (λ = 0.15418 nm), oper-
ating at a voltage of 40 kV and a current of 80 mA. Scans were obtained
−
1
at a rate of 5° min with a step width of 0.05° for 2θ values of 10° to
7
0°. The surface functional groups of the samples were characterized by
FTIR spectroscopy (FT/IR-6600, JASCO) after pressing the materials
into pellets with KBr. The surface areas were evaluated by the
Brunauer-Emmett-Teller (BET) method using nitrogen adsorption
3. Results and discussion
Fig. 1 shows XRD patterns and FTIR spectra obtained from the as-
2