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Amino-Functionalized Reduced Graphene-Oxide-Copper (I) Oxide Composite: A Prospective Catalyst for Photo-Reduction of CO2

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DOI: 10.4236/graphene.2016.52010    1,465 Downloads   1,865 Views   Citations

ABSTRACT

In the present article, an easy synthetic strategy of a novel composite photo-catalyst comprising of amino-functionalized reduced graphene oxide and Cu2O has been proposed. Role of this composite catalyst in photo reduction of CO2 has been analyzed and it is shown that both amino groups and reduced grapheme oxide, participate in enhancing quantum yield of the photo reduction process.

Received 20 March 2016; accepted 24 April 2016; published 27 April 2016

1. Introduction

In recent years, Graphene Oxide (GO) and partially reduced Graphene Oxide (rGO) are drawing attention as new generation of catalysts due to their high specific surface area, with unique graphitized basal plane structure having excellent electrical, mechanical and thermal properties [1] [2] . The wettability and accessibility of the substrates over active surface are augmented by occurrence of surface oxides as in case of GO/rGO. This leads to a better dispersion of metal or metal-oxide nanoparticles onto GO/rGO catalyst surface [3] [4] .

The presence of residual oxygen groups on reduced graphene oxide (rGO) augments the catalytic activity of rGO [5] [6] . It helps protonation/de-protonation and electronation/de-electronation reactions aided by these functional groups of rGO. Some recent works on nanoparticles―graphene or rGO composites are interesting. Generally, these composites are prepared by co-reduction of graphene oxide and metal precursor salt by chemical method using NaBH4, hydrazine hydrate, ethylene glycol, etc. as reducing agents [7] [8] . Sharma et al. [6] synthesized reduced graphene oxide/platinum composite electro catalysts by employing a fast and eco-friendly microwave-assisted poly-ol process. One of the best eco-friendly methods is the electrochemical reduction [9] of graphene oxide to rGO which is a promising and greener way of obtaining rGO. rGO-metal-oxide nano-compo- sites have been reported [10] [11] as efficient photo-catalyst/electro-catalyst for CO2 reduction.

Carbon dioxide is a major product of fossil fuel combustion. With rapid urbanization and industrialization, the increasing trend of atmospheric CO2 is alarming [12] . The natural photo-synthetic path is not enough for restoring CO2 balance. Additional large-scale CO2 reduction paths are to be explored to meet the challenges. In addition, if the reduction products are suitable fuels, those may be used in production of electricity in a fuel cell. Fuel oxidation is a thermodynamically and kinetically favorable reaction. But, reduction of CO2 to fuel is thermodynamically unfavorable and requires solar energy or electrical energy to overcome this thermodynamic barrier. It is also a kinetically difficult reaction because of high activation energies of these reactions. Thus, photo-reduc- tion or electro-reduction of CO2 requires efficient photo-catalysts or electro-catalysts for its conversion to usable fuels. In natural photo-synthetic reaction CO2 reduction occurs at dark phase or in carbon cycle catalyzed by RUBP enzyme. In laboratory conditions, CO2 is reduced onto catalytic surface directly by sun light in the presence of a suitable catalyst. The catalysts used are of the following types: (i) semiconductor metal-oxide catalysts; (ii) metal oxide-organic compound composites like Cu-oxide poly-pyrole; (iii) metal-organic compound complexes; (iv) enzyme catalysts; (v) metal/metal oxide in the presence of organic amines. Although, the first four types of catalysts have been discussed well in different reviews [13] , discussions on the amine compound mediated metal, metal-oxide photo-catalysts/electro-catalysts are only limited. Recently, we have reported [13] that nano-sized Cu(I)-oxide coated with depolymerized chitosan is an excellent electro-catalyst and photo-catalyst for CO2 reduction. We have explained [14] [15] the unique role of amino groups in chitosan in the improvement of electro-catalytic efficiency of Cu2O, proposing its ability to reduce hydrogen evolution reaction. Very recently [16] , amino-functionalized GO-Cu2O has been used as a photo-catalyst for photo bleaching of some dyes. Tang et al. [11] reported photo-reduction of CO2 by rGO-Cu2O composite. These authors have shown that efficiency of this composite catalyst is enhanced to the extent of six folds compared to the Cu2O catalyst and highlighted the positive role of rGO in the photo-reduction process of CO2. But at the same time, they have noted transformation of photo-catalyst to CuO by photo-oxidation of Cu(I) to Cu(II). Photo-oxidation occurs at the hole site of the semi-conductor catalyst. Thus, photo corrosion of Cu2O is a major problem and a challenging issue to be addressed. This motivates us to design a new catalyst with amino-functionalized rGO-Cu2O composites, so that amino-groups may be easily oxidised forming unsaturated compounds which may be regenerated protecting photo-corrosion of Cu2O. To the best of our knowledge there is no report on amino functionalized rGO-Cu2O photo-catalyzed CO2 reduction.

2. Experimental Section

Preparation of Amino Functionalized Graphene Oxide (GO)

Graphite oxide is prepared by following Hummer’s Method [17] . In a typical protocol, 2 g of Graphite flakes were mixed with 1.0 g NaNO3 and 50 ml of sulphuric acid in a beaker and stirred vigorously. The mixture was kept at 0˚C in an ice bath for 5 minutes. To the above mixture, 6 g KMnO4 is added at small intervals time and reaction temperature is generally kept below 20˚C during the addition. The temperature is then raised to 30˚C - 35˚C and maintained for 30 minutes. The mixture gradually became pasty and small amount of gas was evolved. 15 ml of water was added and the temperature was further increased to 98˚C and stirred for another 15 minutes. 30 ml of water and 2 ml of 30% H2O2 are added to ensure reduction of residual permanganate and MnO2 to colorless soluble manganese sulphate. The suspension is filtered and the residue is collected and washed successively with DI water, EtOH and 3% HCl. It is then dried in a oven kept at 40˚C for 12 hours.

Graphene oxide (GO) is prepared by suspending 0.020 g graphite oxide in 40 ml DI water and ultrasonicated for 1 hour for exfoliation. The homogeneous mixture is centrifuged at 3000 rpm for 30 minutes to get non-se- diment supernatant solution. After decanting the supernatant solution, the residue is washed, dried and characterized.

Graphene oxide (0.01 g) is taken in a small hydrothermal reactor and mixed with NN dimethyl tetra-ethylene diamine solution and heated for 30 minutes at 800ºC during this process the amino functionalized GO is obtained by the following reaction.

The amino functionalized GO is then taken in a round bottom flask mixed with CuSO4 (0.1 M) solution and NH2OH∙HCl is added as a reducing agent, the entire mixture is stirred magnetically at 50˚C for 2 h, the reaction mixture is cooled to room temperature and centrifuged. The residue is washed with DI water and re-dispersed for photo-reduction of CO2 study. The composite particles so formed have been primarily characterized by UV- Visible, SEM and EDX studies.

3. Result and Discussion

Preparation of graphite oxide from graphite powder by Hummers method is a conventional protocol for such preparation. But exfoliation of graphite oxide to graphene oxide (GO) depends on sonication conditions. Degree of exfoliation depends on frequency as well as time of exfoliation. It may be mentioned that highly exfoliated sheets may undergo agglomeration forming aggregated colloidal dispersions.

Amino functionalized GO (AGO) is obtained by well reported protocol; however caution has been taken during hydrothermal amino functionalization reaction.

Figure 1(a) shows the UV-visible spectra of very dilute GO dispersions in water, it is seen that GO does not absorb visible light, indicating it is not playing any role at the light absorption stage. But the composite particle absorbs at 635 nm (Figure 1(b)) owing to the excitation of electrons from valence band of Cu2O to its conductance band (band gap energy of Cu2O is around 2.0 eV). This value is close to the reported value [11] of rGO- Cu2O particles indicating copper is present as Cu(I).

SEM image of GO is shown in Figure 2(a), which indicates presence of sheet like structure but similar image for the composite particles shows almost spherical particles of average sizes 300 nm. EDX data indicates presence of C, O, N and Cu in the composite particle.

Since the main propose of this article is to project the role of amino groups and rGO in catalytic reduction of CO2, we propose, a logical scheme (Figure 3) to understand the probable mechanism. The key idea behind such an analysis is that the photo-excited electron from conduction band of Cu(I)-oxide gets easily trapped by rGO [11] and transfer to adsorbed CO2 (as shown in the Figure 3). The holes on the valence band of Cu2O will be scavenged [18] by the electrons from the amines attached to rGO. It is well reported amino-compounds act as sacrificial electron donor in photo-catalytic reactions. In doing so, the amino-compounds get oxidized to unsaturated compounds (shown in Figure 3) which are difficult [18] to regenerate in situ. But here photo-generated hydrogen [19] onto rGO surface may regenerate the sacrificed amine simple by chemical reduction. Recently [19] , electro-catalytic reduction of CO2 onto Cu loaded poly-pyrole has been reported, these authors have proposed formation of H add atom onto poly -pyrole surface, which reduces adsorbed CO2 chemically.

The photo-excited electron transfer from conduction band of Cu2O via rGO to adsorbed CO2 is well explained [11] . In fact, electronation of CO2 to radical anion is difficult, but proton assisted electronation with for-

mation of formic acid [CO2 + 2H+ + 2e = H2CO3], occurs at much lower potential. But water oxidation reaction on the hole site is extremely difficult [20] relative to hole scavenging by sacrificial amine, hence amino functionalized amine is a better choice.

The scheme will significantly reduce the photo-excited electron-hole recombination reaction, a major pitfall of enhancing quantum yield of photo-chemical process onto semiconductor surfaces. Very recently, possible use of renewable amine in photo-catalytic reduction of CO2 onto Pt has been proposed [18] .

(a) (b)

Figure 1. UV-visible spectra of GO dispersions in water (a) and Cu2O composite in water (b).

(a) (b)

Figure 2. SEM image of GO (a) and Cu2O composite in water (b).

Figure 3. Synthetic scheme of amino-rGO-Cu2O composite and their photo-catalytic reaction for CO2 reduction.

It is reported homogeneous catalyst enhances CO2 reduction by forming CO2-catalyst soluble adduct with a less kinetic barrier for electron transfer process. Whereas, it is known heterogeneous catalyst has poor efficiency due to low CO2 adsorption of onto its surfaces. But, presence of amino groups onto catalytic surface, enhance adsorption of CO2. Therefore, proposed combined amine functionalized reduced graphene oxide Cu(I)-oxide composite will serve as an ideal photo-catalyst for CO2 reduction.

4. Conclusion

Based on our primary studies and critical analysis, we have presented for the first time an easy synthetic strategy of amino-functionalized rGO-Cu2O nano composite photo-catalyst and analyzed that both rGO and amino groups play an important role in enhancing quantum yield of photo-catalyzed reduction of CO2. Design of future composite photo-catalysts combing rGO, Cu2O and amino-compounds will certainly help to reduce photo-corro- sion of Cu2O.

Acknowledgements

SBM is thankful to HOD, Chemistry, NITA for providing with necessary support.

Cite this paper

Basumallick, S. (2016) Amino-Functionalized Reduced Graphene-Oxide-Copper (I) Oxide Composite: A Prospective Catalyst for Photo-Reduction of CO2. Graphene, 5, 90-95. doi: 10.4236/graphene.2016.52010.

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