Fig. 3a shows the H
2-temperature programmed reduction (TPR) profiles of CuFe
2O
4/CNT, CuFe
2O
4, Fe
2O
3/CNT and CuO/CNT. There are two peaks at around 174 and 288 ℃ for CuO/CNT, which are assigned to the reduction of the Cu
2+ to Cu
+, Cu
+ to Cu
0, respectively [
35,
36]. There are three peaks at around 323, 499 and 568 ℃ for Fe
2O
3/CNT. The peak at around 323 ℃ is the reduction of Fe
2O
3 into Fe
3O
4, while the broad peaks at around 499 and 568 ℃ are due to the subsequent multiple reduction of Fe
3O
4 to FeO and Fe [
30,
37,
38]. Comparatively, there are four peaks at around 188, 248, 395 and 501 ℃ for CuFe
2O
4/CNT. The peak at around 188 ℃ can be ascribed to the reduction of CuFe
2O
4 to Cu
0 and Fe
2O
3 phases [
37], while the peaks at around 248, 395 and 501 ℃ are due to the further reduction of Fe
2O
3 to Fe
3O
4, Fe
3O
4 to FeO and Fe, respectively [
38]. Compared to Fe
2O
3/CNT, the Fe species in the CuFe
2O
4/CNT composite exhibit lower reduction temperature, demonstrating a synergistic effect between Cu and Fe species within the CuFe
2O
4/CNT composite, in which Cu promoted the reduction of Fe at a lower temperature [
35-
39]. The TPR profile changes induced by the interaction between Cu and Fe species indicate that the enhanced oxygen transfer properties and a better electron acceptor for CuFe
2O
4/CNT [
40,
41]. Moreover, the spectra profile of CuFe
2O
4/CNT is also different from that of CuFe
2O
4, demonstrating the interaction between CuFe
2O
4 particles and CNT supports [
42,
43], which is consistent with TEM results. Thus, the enhanced redox property of CuFe
2O
4/CNT composite would accelerate the activation of CH
4 and further formation of ethanol. From the above analysis, the Cu and Fe species in CuFe
2O
4/CNT composite remarkably affect the ethanol selectivity. Accordingly, the yield of ethanol over the CuFe
2O
4/CNT is calculated as 2.02%. The CH
4 conversion efficiency increases with the higher concentration of Fe species, so the Fe is reasoned to be the main active center for CH
4 oxidation. There are over-oxidation products of CO and CO
2 using Fe
2O
3/CNT as catalysts. The addition of Cu species can decrease the concentration of generated hydroxyl radicals, which are of strong oxidative ability to oxidize the carbon-containing intermediates. This is consistent with the electron paramagnetic resonance (EPR) radical trapping studies on Fe/ZSM-5 and Cu/ZSM-5 [
8]. The intermediates during the CH
4 oxidation process is probed by
in situ infrared (IR) spectroscopy. As shown in
Fig. 3b, no stable surface species are observed over CNT (Fig. S5 in Supporting information), confirming that the CNT alone is inert for CH
4 conversion. Two bands at around 2927 and 2857 cm
−1 are observed for the CuFe
2O
4 catalyst, which is attributed to asymmetric and symmetric CH
2 stretching modes, respectively [
44-
47]. Comparatively, one more peak at around 2963 cm
−1 corresponding to CH
3 stretching modes is found for CuFe
2O
4/CNT [
47,
48]. This confirms that the strong interaction between CuFe
2O
4 and CNTs facilitates the CH
4 activation.