Angewandte
Communications
Chemie
particles, which induces a high local temperature that
facilitates CO2 activation; 2) self-hydrolysis of the boron
particles driven by the photothermal effect, which in situ
produces H2 as the active proton source and electron donor
for CO2 reduction and boron oxides as promoters of CO2
adsorption; and 3) the unique catalytic properties of boron.
In this study, commercial amorphous boron powders were
used as the starting materials. As boron has a strong capability
to form stable covalently bonded molecular networks, even
amorphous boron has previously been demonstrated to
inevitably contain regular boron icosahedra.[9] Accordingly,
as seen from our X-ray diffraction (XRD) patterns (Fig-
ure S1), some diffraction peaks belonging to b-rhombohedral
boron (JCPDS 01-080-0323) were observed for the amor-
phous boron samples, which is consistent with previous
reports.[9,10] The TEM image in Figure 1a shows the network
morphology of amorphous boron. The amorphous nature was
confirmed by high-resolution TEM (HRTEM) imaging (Fig-
ure 1b) as no obvious lattice fringes were observed. It should
be noted that in agreement with the XRD results, some
crystalline boron particles were also found during our TEM
studies.
visible regions of the solar spectrum that also tail even into
the NIR region. The former absorption probably originates
from the interband transitions, and the latter might be related
to the absence of long-range order in the amorphous boron
particles.[13] The intense absorption of amorphous boron
implies its high capability for the utilization of solar energy.
Considering the benefits of high temperatures for CO2
activation, we investigated the photothermal effect of this
amorphous boron material. The changes in temperature upon
light irradiation at different intensities are depicted in Fig-
ure 1d. As expected, upon light irradiation, an instant and
remarkable increase in the temperature of the sample was
observed (reaching the maximum temperature within
10 min). Furthermore, a nearly linear relationship between
the increase in temperature and the light intensity was
observed for the present system (Figure S3). At a light
intensity of 456 mWcmÀ2 (full arc with a maximum input
power of 300 W), the temperature of the sample increased up
to 4628C. Taken together, these results clearly demonstrate
the good photothermal properties of the amorphous boron
material, which should be beneficial for the activation of CO2
and subsequent photoreduction.
Before investigating the CO2 photoreduction, the CO2
adsorption properties of the amorphous boron material were
studied. For comparison, commercial TiO2, a widely used
photocatalyst for CO2 reduction, was also tested. As shown in
Figure S4, although these two compounds possess nearly
equal specific surface areas, the CO2 uptake of the amorphous
boron sample was more than twice as large than that of TiO2.
This should be related to the presence of boron oxides on the
surface of the boron material (Figure S5),[14] which are usually
considered as trapping sites for CO2.[15] Considering the
superior CO2 adsorption capacity and excellent photothermal
properties, this amorphous boron material was anticipated to
display high CO2 photoreduction activity.
In the CO2 photoreduction measurements, water was used
as the hydrogen source, and no additional sacrificial agents or
metal cocatalysts were employed in the reaction system.
These features should be advantageous for potential applica-
tions. As expected, full arc irradiation of the amorphous
boron material led to continuous formation of CO and CH4 by
CO2 photoreduction with reaction rates of 1.0 and
2.5 mmolhÀ1, respectively (Figure 2a). Even under visible-
light irradiation (l > 400 nm), the use of the amorphous boron
catalyst still led to the formation of CO at 0.8 mmolhÀ1 and
CH4 at 1.9 mmolhÀ1 (Figure 2b and Figure S6). To the best of
our knowledge, this is the first example of CO2 photo-
reduction over amorphous boron. Moreover, it should be
noted that the boron material outperformed most photo-
catalysis systems for CO2 photoreduction (Table S1). Under
long-term irradiation, both CH4 and CO production increased
in a nearly linear fashion (Figure S7). This suggests that the
catalytic activity of the amorphous boron material for CO2
photoreduction is fairly stable. When experiments were
performed without light irradiation or in the absence of the
boron material, CO and CH4 were not detected (Figure 2b).
This result indicates the necessity for light and boron in this
CO2 reduction. To further confirm the origin of the CO and
CH4 products, isotope tracer analyses were conducted with
Figure 1. a) TEM and b) HRTEM images and c) UV/Vis/NIR spectrum
of the amorphous boron material. The inserted background in gray in
(c) is a solar irradiation spectrum. d) The increase in temperature of
amorphous boron samples under light irradiation at different light
intensities.
Owing to the rather negative potential required for CO2
reduction and also the fairly positive potential needed for the
oxidation of water or sacrificial agents,[3a,11] a photocatalyst
that might enable photocatalytic CO2 reduction must possess
a very large band gap (usually the photocatalyst presents in
white or light yellow color),[1c,2c,12] thus significantly limiting
the efficiency of solar light utilization (Figure S2). In sharp
contrast, the amorphous boron catalyst employed here has
a typical dark brown color (Figure S2b), implying that it has
a wide light absorption range. According to the absorption
spectrum in Figure 1c, the amorphous boron particles show
excellent absorption features (absorbance > 1) in the UV and
2
ꢀ 2017 Wiley-VCH Verlag GmbH & Co. KGaA, Weinheim
Angew. Chem. Int. Ed. 2017, 56, 1 – 6
These are not the final page numbers!