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Table 1 Surface copper components based on Cu LMM deconvolution and surface atomic ratios of Cl to Cu based on XPS analysis
Kinetic energies (eV)
2+
+
0
a
2+
+
0
b
Samples
Cu
Cu
Cu
Peak area ratios , Cu : Cu : Cu
Atomic ratios , Cl : Cu
Bulk CuCl
Reacted CuCl/Si
Chlorinated CuCl/Si
918
917.7
918
916
916
916
—
918.7
918.7
7.7 : 1 : 0
0.3 : 1 : 1.4
2.4 : 1 : 0.7
1 : 1
0.3 : 1
0.8 : 1
a
2+
+
0
b
Peak area ratios among Cu , Cu , and Cu were calculated by the deconvolution of Cu LMM XAES. Atomic ratios of Cl to Cu were obtained by
XPS analysis.
with peak positions at 916, 917.7–918, and 918.7 eV corre-
+
2+
0
sponding to Cu , Cu , and Cu species, and the XAES peaks
+
2+
were deconvoluted into three symmetrical peaks of Cu , Cu ,
and Cu species by using a XPSPEAK41 soware. Considering
0
that a shoulder peak appeared at 912 eV, an extra Gaussian–
Lorentzian band with the peak position at ca. 912 eV was used to
eliminate the effect of other orbital electrons on the XAES.
According to the deconvolution results, the surface copper
2
+
+
species of the bulk CuCl were composed of Cu and Cu
components (Fig. 4). The surface copper species of the reacted
CuCl/Si and chlorinated CuCl/Si mixtures were composed of
Scheme 1 Reactions between CuCl and bulk Si and the chlorination
reaction.
2
+
+
0
Cu , Cu , and Cu components. Aer taking part in the reac-
0
tion, in addition to the formation of the metallic Cu compo-
2
+
ꢁ
nent, the surface Cu content of the reacted CuCl/Si mixture
was obviously less than that of the bulk CuCl, but the surface
The binding energies of Cl 2p3/2 and Cl 2p1/2 of Cl of the
bulk CuCl, reacted CuCl/Si, and chlorinated CuCl/Si samples
were ca. 198.7 and 200.3 eV, respectively (Fig. 3b). According to
the deconvolution of the Cl 2p3/2 and Cl 2p1/2 peaks, the area
ratios of the Cl 2p3/2 peak to the Cl 2p1/2 peak for the three
samples were 1 : 0.8, 1 : 1.9, and 1 : 0.8, respectively, revealing
that there was an interaction between Si and Cl during the
reaction process. Aer chlorination, the CuCl phase was
recovered because the bulk CuCl and chlorinated CuCl/Si
+
Cu content of the reacted CuCl/Si mixture was larger than that
2
+
of the bulk CuCl, indicating that Cu was reduced to copper
species with lower valence states (Table 1). Aer chlorination,
2
+
+
the total content of surface Cu and Cu species of the chlori-
nated CuCl/Si mixture increased as compared to that of the
2
+
reacted CuCl/Si mixture. Considering that the surface Cu
species of the chlorinated CuCl/Si mixture could be attributed
+
to the oxidation of Cu during the sample characterization
samples had the same area ratios of Cl 2p3/2 to Cl 2p1/2
.
17
process in air, it was reasonable to suggest that chlorination
The Cu 2p3/2 and Cu 2p1/2 peaks of the bulk CuCl, reacted
CuCl/Si, and chlorinated CuCl/Si samples were doublet (Fig. 3c).
The presence of a satellite peak at ca. 942.5 eV for the three
+
increased the surface Cu content.
The XPS analysis revealed that the surface atomic ratio of Cl
to Cu in the reacted CuCl/Si mixture was lower than that in the
bulk CuCl (Table 1). Chlorination of the reacted CuCl/Si mixture
increased the surface atomic ratio of Cl to Cu. It could be
explained as follows. During the reaction process, CuCl crys-
2
+
12
samples indicated the presence of Cu species. The Cu 2p3/2
and Cu 2p1/2 peaks at ca. 935 and 955 eV were ascribed to those
2
+
of Cu species, whereas the Cu 2p3/2 and Cu 2p1/2 peaks at
+
9
32.4 and 952.3 eV were ascribed to those of Cu and/or metallic
0
13–16
tallites reacted with silicon to form Cu
x
Si
y
Cl
z
species. Further-
Cu species. The XPS analysis revealed that the three
samples contained Cu , Cu and/or Cu species. The presence
of the Cu species is observed because CuCl is easily oxidized
ꢁ
2
+
+
0
more, Cl from the Cu
Si
x
Cl
y
z
species reacted with Si and/or
2
+
methanol, removing it from the active species. This process
ꢁ
caused the decrease in Cl content of Cu
Si
x y
Cl
z
0
active species.
when it is exposed to air during the ex situ sample character-
ꢁ
With the consumption of Cl , metallic Cu was formed.
However, chlorination treatment caused the formation of CuCl
17
ization process.
+
0
Considering that Cu and metallic Cu have similar binding
energies, it is difficult to distinguish them based on Cu 2p
spectra. X-ray excited Auger Electron Spectroscopy (XAES) was
and probably recovered the Cu
x
Si
y
Cl
z
active species. The reac-
tions are suggested in Scheme 1.
2
+
+
used to determine the surface compositions of the Cu , Cu ,
0
0
13,16,18–20
3.2. Chemical structures of Cu
mixtures aer pretreatment and reaction
3.2.1. XRD analysis. When Cu O and CuO were used as the
Cu species are centered at 916, 918, and 918.7 eV, respec- catalysts, Cu O and CuO phases existed in the pretreated
Therefore, we chose Gaussian–Lorentzian bands samples, respectively (Fig. 5a and b). However, aer reacting at
2
O/Si, CuO/Si, and Cu /Si
and Cu species.
The Cu LMM XAES of the bulk CuCl,
reacted CuCl/Si, and chlorinated CuCl/Si samples are shown in
+
2+
Fig. 4. Literatures report that the XAES peaks of Cu , Cu , and
2
0
2
13,16,18–20
tively.
ꢀ
0
2
20–260 C for 3 h, the metallic Cu phase was formed with the
19320 | RSC Adv., 2018, 8, 19317–19325
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