Zn-Cu promoted TiO2 photocatalyst for CO2 reduction with H2O under UV light

https://doi.org/10.1016/j.apcatb.2015.12.037Get rights and content

Highlights

  • TPD-CO2 results for TiO2 samples have recorded different strengths of CO2 adsorption.

  • Cu1+ and Cu2+ species coexist in CT and CZT photocatalysts.

  • CH4 production achieved the range of 126–184 μmol/g after 24 h-irradiation period.

  • CH4 formation has increased in the following order: TiO2 (P-25)  TiO2 < CT < CZT.

  • The interaction between CO2 and photocatalyst has influence on photoactivity.

Abstract

The photocatalytic reduction of CO2 has been studied aiming to find a useful application for such low cost and abundant raw material. Besides reducing CO2 in the atmosphere, the process can contribute for the generation of high energy products (CH4 and CH3OH). The reaction was performed in liquid phase, batch, at 25 °C, with the photocatalyst (1 g/L) maintained in suspension. UVC lamp (18 W, 254 nm) was chosen as the radiation source. Photocatalysts were prepared using oxides of titanium, copper and zinc. Commercial TiO2 (P-25, Degussa) was utilized as reference. Techniques such as N2 adsorption, XRF, SEM-EDS, XRD, XPS, DRS UV–vis and TPD-CO2 were used for photocatalysts characterization. Catalysts having specific area ranging from 36 to 52 m2/g and bandgap energies varying from 3.0 to 3.3 eV were obtained. TPD-CO2 results showed different strengths of CO2 adsorption for each photocatalyst. In the performance tests, CH4 production achieved the range of 126–184 μmol/gcat after a 24 h-irradiation period. Regarding the photocatalysts tested, it was observed increased CH4 formation in the following order: TiO2 (P-25)  TiO2 < 2%CuO/TiO2 < 2%CuO–19%ZnO/TiO2. Results indicate that the interaction between CO2 and the photocatalyst influences the photocatalytic activity.

Introduction

As a consequence of new modes of production, since the Industrial Revolution, technology has had a profound effect on socioeconomic and environmental conditions. Atmospheric concentrations of CO2 have grown exponentially since that period and nowadays it is considered the gas that mostly contributes to the greenhouse effect [1], [2], [3]. This assertion is questioned in numerous studies linking global warming to Earth’s natural aging process and not to human activities. Even with those divergent views, there is a consensus toward the need to reduce CO2 emissions.

Among the alternatives to decrease atmospheric CO2 concentrations, CO2 capture and sequestration is one of the most studied [4]. In this scenario, CO2 reuse in chemical processes became an important issue and alternatives such as heterogeneous catalytic and electrocatalytic conversions were brought to light. The development of alternative production processes using CO2 as a non-expensive feedstock or co-feeding may actually help to reduce the inconvenience caused by the uncontrolled release of gas.

The artificial photosynthesis process was named as such because of the similarity to nature’s photosynthesis performed by plants [5], [6]. While plants transform solar energy in chemical, with the help of chlorophyll, generating O2 and glucose, CO2 photocatalytic reduction is assisted by a photocatalyst and UV irradiation, transforming water and CO2 into organic compounds of high energy level. Therefore, researchers dealing with artificial photosynthesis have great interest in environmental issues [7], [8], [9]. The choice for CO2 photocatalytic reduction represents a sustainable and economically viable alternative: that is, it enables the use of both sunlight as a radiation source and CO2 as raw material. The most employed photocatalysts in that type of reaction are semiconductor materials, such as TiO2, ZnO and ZrO2 [7], [10], [11], [12], [13].

Titanium dioxide (TiO2) and zinc oxide (ZnO) are the most common materials used in heterogeneous photocatalysis for bringing the features of low cost, low toxicity, photostability, high catalytic activity [14], activation by sunlight and, finally, chemical stability over a wide pH range. The energy required to activate both oxides, TiO2 and ZnO, by light is approximately 3.2 eV, which corresponds to UV radiation of wavelength shorter than 387 nm [15]. That characteristic enables the use of sunlight as the radiation source, since the wavelengths in this range represent approximately 3% of the solar spectrum that reaches the Earth́s surface. Watanabe [16] has shown that ZnO can reduce CO2 with a reductant molecule – H2O or H2 – under high pressures of 25–35 kg/cm2 of CO2 gas generating oxygenated compounds. Pérez-Larios et al. [17] have used TiO2–ZnO mixed oxides to improve from water splitting. The results showed an activity six times higher for TiO2–ZnO-X mixed oxides than that for bare TiO2 semiconductor.

Theoretical and experimental studies have shown that the crystal phase of TiO2 and the defect disorders in TiO2 have influence on CO2 adsorption, activation and dissociation processes [13]. According to Rodriguez et al. [18], the presence of defects on TiO2 surface induces the formation of new adsorption configurations, in which CO2 is bonded at the defect sites. Electrons stored in the oxygen-deficient (VO) can be spontaneously transferred to CO2 and once the CO2 is formed, the radical may decompose into CO through the occupation of one oxygen atom into the VO site.

Regarding photoreduction and photooxidation applications, the effect of metallic dopants, such as Ce, Cu, CuO, Pt, Au and Ag, in TiO2 has also been reported [19], [20]. However, a high concentration of metal/metal oxide can generate recombination centers of electron-hole pairs, leading to a reduction of photocatalytic efficiency. Another possibility is the use of nonmetals as doped and co-doped materials (for instance, C, N, S, F, etc.), which results in a significant narrowing of the bandgap, if compared to metal doping, leading to high photocatalytic efficiency under visible light irradiation [21], [22], [23], [24], [25], [26].

Copper oxide (CuO) has been extensively studied in CO2 photocatalytic reduction for several reasons. First, the presence of copper associated to the photocatalyst has an important role in CH3OH production, increasing significantly its production if compared to a photocatalyst without promoter. Another reason for using CuO is the redistribution of electric charge on the surface of the semiconductor support [10], [19], [27]. According to Tseng et al. [28], copper plays the role of a trapper of electrons preventing the recombination electron-hole pair and consequently promoting significant increase in photoefficiency. They have observed that the highest CO2 conversion occurred when Cu content was 2% and that large amounts of photocatalyst in the reaction may hinder the diffusion of UV irradiation [28]. Slamet et al. [15] found that the photocatalysts promoted by CuO showed better performance than the materials promoted by the species Cu0 and Cu+1.

In the present study, the influence of Zn–Cu deposition on the photoactivity of TiO2 has been investigated in the photocatalytic reduction of CO2 with H2O to produce C1 fuels, such as CH4 or CH3OH. The direct impact of the presence of the brookite phase, instead of rutile phase, on the photocatalytic properties was also investigated. Additionally, CO2 adsorption capacity of the photocatalysts was measured by temperature programmed CO2 desorption to evaluate CO2 interaction with the photocatalysts.

Section snippets

Catalyst preparation

TiO2 was prepared by slow hydrolysis of titanium isopropoxide—Ti(OCH(CH3)2)4 (97%, SIGMA–ALDRICH). Due to the reagent instability, the reaction was carried out in inert atmosphere, using a plastic chamber previously filled with N2. The precipitate obtained was filtered and washed, dried in an oven at 120 °C overnight and submitted to calcination at 550 °C for 6 h using airflow (30 mL/min) [29]. TiO2 resulting from this procedure was used in the preparation of the other photocatalysts.

2%CuO/TiO2

Photocatalysts characterization

XRD pattern of photocatalysts in Fig. 2 shows the anatase and brookite phases of TiO2 with peaks of greater intensity in 2θ = 25.28° and 2θ = 25.34°, respectively. As those peaks overlap, brookite phase identification was made by the second highest peak intensity at 2θ = 30.81°. The quantification of crystalline phases was estimated as 79% of anatase and 21% of brookite phases.

Regarding CT photocatalyst, no characteristic peak of either copper oxide (2θ = 35.5° and 36.4° for CuO and Cu2O, respectively)

Conclusion

The physicochemical characterization has shown that copper oxide is found dispersed on TiO2 independent of the preparation method, co-precipitation or impregnation. Co-precipitation deposition caused the formation of filamentous structures on CZT surface, in which the zincite phase (ZnO) has been identified. Addition of copper and zinc oxides to TiO2 has promoted a decrease in specific area if compared to pure TiO2. DRS UV–vis spectra have indicated that CZT photocatalyst increases the

Acknowledgments

The authors would like to thank the National Council for Scientific and Technological Development (CNPq) for financial support. The authors also thank M.Sc. Carlos André C. Perez (NUCAT), Dr. Fábio Barboza Passos and M.Sc. Hugo A. Oliveira (RECAT/Universidade Federal Fluminense) for XPS analyses.

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