Y. Zhao et al.
Catalysis Communications 154 (2021) 106310
+
Cu
0
Cu
CuSi3
IM-CuSi
580
575
570
565
Binding energy (eV)
Fig. 3. Cu LMM Auger spectra obtained for the reduced CuSi
3
and IM-
Fig. 2. The TEM image of the reduced CuSi
3
catalyst.
CuSi catalysts.
Those data indicated that the measures we took in the catalyst synthesis
were effective toward improving the dispersion of the copper species.
However, the XRD pattern of the calcined IM-CuSi sample showed two
sample. Thus, the high copper dispersion of the CuSi
understand.
3
sample was easy to
◦
◦
sharp peaks at 2θ = 35.5 and 38.7 , accompanied by satellite peaks at
3.5. H
2
-TPR analysis
◦ ◦
4
8.8 and 61.5 , which clearly indicated that there was a large amount
of blocky CuO in the IM-CuSi sample [19].
2
H -TPR was performed to evaluate the reducibility of the calcined
The XRD patterns of the reduced samples are shown in Fig. 1(b). The
catalysts. Fig. S4 showed that the reduction peaks in CuSi
x
were all
◦
diffraction patterns of the reduced CuSi
x
samples exhibited a very weak
O species [19]. The
located in the low temperature region (200–300 C), indicating that the
copper species in these samples were made up of small particles that
◦
peak at 37.5 , which could be attributed to the Cu
2
peaks were weak and diffuse, indicating that the particle size of Cu
2
O
were easy to reduce. The H
the Cu contents from CuSi
CuSi sample was quite different from that of the CuSi
2
consumption increased with an increase in
was small and the crystallinity was poor. During the reduction process,
the forming Cu metallic species leave the silica framework, so sintering
should always occur. However, due to the stable Cu-O-Si structure and
enhanced strong metal-support interactions (SMSI) formed during the
1
to CuSi . The reduction behavior of the IM-
4
x
samples. The TPR
◦
curve of the IM-CuSi sample showed a reduction peak at 219 C, cor-
responding to the reduction of copper species with small particle size in
the IM-CuSi sample [21]. The reduction temperature was much lower
x
calcination treatment, the copper particle size in the CuSi samples after
the reduction step was still small. However, the XRD pattern of the
reduced IM-CuSi sample showed sharp diffraction peaks at 43.3, 50.4
3
than that of CuSi , indicating that the interactions formed between the
copper species and the support were weak and these copper species were
prone to be reduced. There were two additional broad hydrogen con-
◦
0
and 74.1 , which belonged to the Cu species. The XRD pattern also
◦
◦
showed weak diffraction at 37.5 corresponding to the Cu
2
O species,
sumption peaks in the high temperature regions of 260–330 C and
◦
indicating that the reduced IM-CuSi samples were mainly composed of
large metallic Cu particles and a small amount of Cu O species.
375–425 C, which could be attributed to the large particles of CuO with
2
2
poor dispersion in the IM-CuSi sample. In addition, the H consumption
observed for the IM-CuSi sample was larger than that for the CuSi
3
+
3
.3. Transmission electron microscopy (TEM)
sample with the same Cu content, indicating that some Cu species may
3
already exist in the calcined CuSi sample due to the strong interactions
The morphologies of the reduced CuSi
3
and IM-CuSi samples were
sample (Fig. 2),
among the Cu-O-Si composite structure.
3.6. XPS analysis
investigated using TEM. In the case of the reduced CuSi
3
a large number of copper species were uniformly dispersed on the sup-
port and the particle size distribution showed that the average diameter
of copper species on the sample was only 2.96 nm, which is consistent
with the XRD pattern. However, the average diameter of copper species
on the IM-CuSi catalyst was ~18 nm (Fig. S3). Apparently, the disper-
sion of copper species on the support for the IM-CuSi catalyst was poor,
which may be a result from the weak interaction formed between the
impregnated copper species and the support, and the severe agglomer-
ation of the copper species during the calcination and reduction steps.
3
The surface chemical states of the reduced CuSi and IM-CuSi sam-
2
+
ples were determined using XPS. As seen in Fig. S5, Cu was completely
reduced to its low valence state after the reduction process [22]. Further
research on the Cu Auger LMM spectra shown in Fig. 3 indicates that all
the spectra present a series of asymmetrical and broad peaks, indicating
the coexistence of Cu and Cu0 on the surface of the catalysts. Decon-
+
volution of the Cu LMM peaks was carried out and the peak located at
0
5
69.8 eV corresponded to the Cu species, while the peak with a higher
+
3
.4. N
2
O titration
BE value was the peak corresponding to the Cu species [23]. The
+
deconvolution results showed that the Cu content on the surface of the
0
+
The well dispersed Cu catalyst can produce high surface Cu and Cu
reduced CuSi
3
(58.3%) and IM-CuSi samples (28.6%) differed greatly. It
+
0
+
concentrations combined with a high Cu /(Cu + Cu ) ratio to achieve
was the special Cu-O-Si structure in the CuSi
3
sample, which strongly
+
high catalytic activity [10]. Thus, the dispersion of surface copper in the
interacted with the support, retarding the further reduction of Cu into
0
CuSi
20] and the results are listed in Table 1. The CuSi
high dispersion of copper (40.95%), which was much higher than that in
3
and IM-CuSi sample were compared using N
2
O titration studies
Cu .
[
3
sample possessed a
3.7. Catalytic performance during the hydrogenation of DMO
the IM-CuSi sample (9.72%). The N
TEM analyses showed that the CuSi
2
adsorption-desorption, XRD and
sample exhibited a significantly
3
The hydrogenation of DMO was performed to compare the catalytic
performance of the catalysts and the reaction can be seen in Scheme S1
higher surface area and much smaller Cu particle size than the IM-CuSi
3