1. Introduction
The rapid development of current society has increased the consumption of non-renewable fossil fuels. Human beings have to face the problem of energy shortages, and the resulting large emissions of CO
2 are also an important cause of global warming [
1,
2,
3,
4]. Currently, using sustainable solar energy to photocatalytically reduce CO
2 in high-value-added products is a promising way to simultaneously solve the greenhouse effect and the energy crisis [
5,
6]. Therefore, it is very important to design and synthesize photocatalysts with low pollution, high efficiency, and low cost [
7,
8].
As an environmentally friendly transition-metal-oxide semiconductor, NiO has excellent conductivity, good chemical stability, and non-toxicity, and it has broad application prospects at the nanoscale [
9,
10]. At the same time, it is considered to be a semiconductor that can be used for CO
2 photoreduction due to its sufficiently negative conduction band position, fast hole mobility, and high charge-carrier concentration [
11]. However, due to the high recombination degree of photogenerated carriers, the separation efficiency of electrons and holes in the reaction process is low, which greatly weakens the reactivity [
12]. In addition, wide-band-gap NiO semiconductor catalysts can only use about 3–5% of solar ultraviolet light, resulting in the low efficiency of the photocatalytic reduction of CO
2, limiting the application of NiO in photocatalysis [
13]. Therefore, NiO is often used as a co-catalyst to improve photocatalytic performance and encourage the efficient separation of photoelectrons and holes [
14]. For example, NiO can significantly improve the photocatalytic hydrogen-production performance of SrTiO
3, TiO
2, Nb
2O
5, Ga
2O
3, and other photocatalysts [
15]. However, the activity was generally low in the reported photocatalytic reduction of CO
2 by NiO [
16,
17]. Therefore, NiO is usually modified by different methods to improve the photocatalytic performance [
18].
Since NiO has suitable conduction band (CB) and valence band (VB) positions, it often forms heterostructures with many semiconductors. Zhang et al. [
19] prepared an S-type BiOBr/NiO heterojunction. The experiment showed that the layered structure of BiOBr/NiO increased the light-absorption and charge-separation performance, and it improved the redox ability of BiOBr/NiO. In addition, the NiO-layered porous-sheet structure was conducive to the adsorption of CO
2, exposing abundant active sites for CO
2 photoreduction, thus achieving excellent CO
2 photoreduction performance. Moreover, Park et al. [
20] prepared a single-layer hollow-sphere photocatalytic material (h-NiO-NiS) of NiO and NiS by partially replacing O with S on NiO hollow spheres. The construction of this heterojunction greatly enhanced the CO
2-adsorption capacity and increased the transfer of excited electrons from the NiS to the surface along the hollow spheres. The efficient transfer of electrons led to the prolongation of the photogenerated charges’ recombination times, which further increased the conversion of CO
2 to CH
4.
Moreover, charge separation can be increased by adjusting the electronic structure of NiO, thereby improving its CO
2 photoreduction activity. ** is an effective method with which to adjust the electronic structures of catalysts and has been extensively studied [
23,
24,
25,
26]. However, compared with anion do**, cation do** produces more harmful electron–hole recombination centers. Because oxygen and nitrogen show similar chemical, structural, and electronic characteristics, such as polarizability, electronegativity, coordination number, and ionic radius, when other elements (such as N 2p) with higher potential energy than O 2p atomic orbitals are introduced, new VBs instead of O 2p atomic orbitals can be formed, resulting in smaller E
bg without affecting the CB level, thereby improving the visible-light response [
27]. Therefore, non-metallic-element-N do** is a preferable way to improve the photocatalytic CO
2-reduction effect of NiO. Furthermore, it is also important to choose the appropriate do** method. The molten-salt method of element do** is an efficient and low-cost method because its molten-salt liquid environment can make the element distribution more uniform, and the treatment process before and after the reaction is very simple [
28].
In this research, NiO semiconductor catalysts with different nitrogen-do** contents were prepared using a molten-salt calcination method, and the CO
2-reduction activity was tested in a bipyridine ruthenium/triethanolamine heterogeneous catalytic system excited by different wavelengths of light [
29]. The phase composition, band structure, optical properties, and surface morphology of the doped NiO semiconductor were researched through a series of characterizations. The enhancement mechanism of the photocatalytic performance was discussed, and the possible mechanism of the photocatalytic process was analyzed.
3. Experimental Section
3.1. Materials
The used chemicals were nickel nitrate hexahydrate (Ni(NO
3)
2·6H
2O, Sinopharm Chemical Reagent Co., Ltd., Shanghai, China), sodium hydroxide (NaOH, Shanghai Aladdin Biochemical Technology Co., Ltd., Shanghai, China), anhydrous lithium chloride (LiCl, Shanghai McLean Biochemical Technology Co., Ltd., Shanghai, China), potassium chloride (KCl, ** source, excessive urea was added to the reaction to reduce the effect of volatilization. The preparation process of nitrogen-doped NiO was as follows: a total of 5 mmol of precursor Ni(OH)
2, m g urea (m = 0.2,0.3,0.4,0.5), 2.7 g of LiCl, and 3.3 g of KCl were fully ground and then calcined at 400 °C for 3 h. The bulk after reaction was fully dissolved in appropriate DI water and filtered, after which it was washed several times with DI water and ethanol alternately and dried at 60 °C for 8 h to obtain N-NiO-x (x is 1, 2, 3, 4). Nitrogen and oxygen contents over N-NiO-2 were determined by inert-gas-fusion technique using a nitrogen-and-oxygen elemental analyzer (LECO Corp., TC-436AR, St. Joseph, USA). The carbon content was obtained by carbon–sulfur analyzer. The ratio of C over N-NiO-2 was 0.02 wt% (probable error), which was negligible compared with 2.03 wt% N and 19.21 wt% (
Table S2).
3.5. Photocatalytic CO2 Reduction
In this research, the catalytic performances of the samples were evaluated for CO2-reduction activity. The light source was an 80-watt LED lamp (illumination wavelengths were 365 nm, 420 nm, 550 nm, Zhenjiang Yinzhu Chemical Technology Co., Ltd., Zhenjiang, China). Typically, 30 mg of the catalyst, 5 mg of [Ru(bpy)3]Cl2·6H2O (denoted as Ru), 3 mL of MeCN, 2 mL of H2O, and 1 mL of TEOA were added to a 50-milliliter quartz reactor. Before the start of the reaction, the reactor was first vented with pure CO2 for 30 min in the dark, in order to make the reaction system reach the adsorption saturation of CO2; next, 1 mL of gas was extracted every 2 h under illumination and injected into a chromatographic system (H2 and CO were detected by thermal-conductivity detector and flame-ionization detector, respectively).
The CO selectivity was calculated using the following formula:
where
YCO and
YH2 represent the yields of CO and
H2, respectively.
Furthermore, the optical powers at different wavelengths were measured via an optical power meter, with a probe area of 1 × 1 cm
2 to contact light. The light-irradiation area was 2.5 × 2.5 cm
2. The apparent quantum efficiency (AQE) was calculated using the following formula:
where
N: the number of incident photons;
E: the accumulated light energy in the given area (J);
: the wavelength of the light;
h: Planck’s constant (6.626 × 10−34 J·s);
c: the velocity of light (3 × 108 m·s−1).
3.6. Characterizations
The phase structure of the material was measured using X-ray diffraction (XRD, Cu Kα, λ = 0.15406 nm, Bruker D8 Advance). The microstructure and element distributions of the prepared samples were evaluated using scanning-electron microscopy (SEM, FESEM ZEISS sigma 500, Oberkochen, Batenwerburg, GER), transmission-electron microscopy (TEM, JEM-2100F), and energy-dispersive X-ray spectroscopy (EDX). The X-ray photoelectron spectra (XPS, Thermo Fisher, K-Alpha, Waltham, MA, USA) were examined to study the chemical states of the elements. The UV–Vis diffuse-reflectance spectra (DRS, Shimadzu UV-2600, Kyoto, Japan) were examined using BaSO4 as the reference standard, in order to study the optical absorption properties of the samples. The vacancy-defect state in the photocatalyst was analyzed with electron paramagnetic resonance (EPR, Bruker ER200-SLC, Billerica, MA, USA) measurement at room temperature. The CO2 adsorption at 273 K under ice–water-mixture conditions was studied on an automatic physical adsorption instrument (ASAP 2020, Norcross, Georgia, USA). Steady-state fluorescence (PL) spectra detected the reintegration of exposed electron–hole pairs at an excitation wavelength of 250 nm with a fluorescence spectrometer (FLS 980, Edinburgh, Scotland). Photoelectrochemical measurements were carried out in a three-electrode system on an electrochemical workstation (Shanghai Chenhua CHI-660E, Shanghai, China) using 0.1 mol/L Na2SO4 or 0.1 mol/L K3Fe(CN)6/K4Fe(CN)6 buffer solution as the electrolyte solution, Ag/AgCl as the reference electrode, Pt wire as the auxiliary electrode, and indium-tin-oxide conductive glass (ITO) as the working electrode (10 mg of the sample was dissolved in 3 drops of ethanol, including 10 μL of nafion solution, after which the solution was subjected to ultrasound for 40 min to completely disperse the sample, with an effective loading area of 0.25 cm2).