contents journal of photochemistry and photobiology a ... · using a peltier-cooled photon-counter...

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Journal of Photochemistry and Photobiology A: Chemistry 262 (2013) 52–56 Journal of Photochemistry and Photobiology A: Chemistry journa l h om epa ge: www.elsevier.com/locate/jphotochem Enhanced photocatalytic activity of BiVO 4 by co-grafting of metal ions and combining with CuBi 2 O 4 Masami Nishikawa , Souta Hiura, Yasufumi Mitani, Yoshio Nosaka ∗∗ Department of Materials Science and Technology, Nagaoka University of Technology, Nagaoka 940-2188, Japan a r t i c l e i n f o Article history: Received 19 February 2013 Received in revised form 16 April 2013 Accepted 19 April 2013 Available online 29 April 2013 Keywords: Grafting co-catalysts Metal ion deposition Composite photocatalyst Superoxide radical Hydrogen peroxide a b s t r a c t In order to improve photocatalytic activity of BiVO 4 , the co-grafting effects of two kinds of co-catalysts for electron and hole separations were examined. At first, stabilization of electrons in BiVO 4 by grafting Fe 3+ was confirmed by analyzing the formation of O 2 and H 2 O 2 as reduction intermediates of O 2 . When BiVO 4 was co-grafted with Fe 3+ and CoPi as an electron separator and a hole separator, respectively, its photocatalytic activity for decomposition of gaseous acetaldehyde with visible light (470 nm LED) was enhanced compared to the BiVO 4 grafted only by either co-catalyst. This indicated that co-grafting is effective to increase photocatalytic activity because electron and hole were effectively taken out of the BiVO 4 . Furthermore, by combined with CuBi 2 O 4 , a p-type semiconductor, the photocatalytic activity of BiVO 4 was also increased. This is because holes and electrons, which were generated in the both semiconductors, were successfully separated in BiVO and 4 CuBi O , 2 4 respectively, due to combination of electrons in the BiVO 4 with holes in the CuBi 2 O 4 . To promote the reaction between electrons in BiVO 4 and holes in CuBi 2 O 4 , we examined co-grafting effects of two kinds of co-catalyst to the composite by preparing the Cu/CuBi O –CoPi/BiVO photocatalyst. 2 4 4 The photocatalytic activity was further enhanced when it was prepared in a suitable procedure that enables us to graft the reduction and oxidation co- catalysts only at each site. © 2013 The Authors. Published by Elsevier B.V. 1. Introduction Photocatalytic materials have been used in wide application such as air purification, water purification, anti-virus and water splitting [1,2]. Photocatalytic reaction proceeds owing to holes and electrons generated in materials by absorbing light energy. The photogenerated holes have an oxidation ability and the photo- generated electrons have a reduction ability. For decomposition of organic pollutants by photocatalytic reaction, the oxidation potential of hole needs to be more positive than +1 V that is redox potential of general organic compounds. In addition, the redox potential of electrons needs to be more negative than that of oxygen (O 2 /O 2 or H 2 O 2 ) because surplus electrons that are not consumed by reduction of oxygen would increase the electron–hole recombination probability. Many materials for pho- tocatalyst, which meet these conditions, have been reported such Corresponding author. Tel.: +81 258 47 9306. ∗∗ Corresponding author. Tel.: +81 258 47 9315. E-mail addresses: [email protected] (M. Nishikawa), [email protected] (Y. Nosaka). as TiO 2 , SrTiO 3 , ZnO, ZrO 2 , WO 3 , and BiVO 4 [3–6]. Among these materials, BiVO 4 has attracted much attention in the recent years as one of the visible-light driven photocatalysts because of non- toxicity and its relatively narrow bandgap of 2.4 eV in monoclinic crystalline form. However, photocatalytic activity of BiVO 4 is gen- erally low compared to TiO 2 and WO 3 photocatalysts because the electronic potential in the valence band of BiVO 4 is more nega- tive than those of TiO 2 and WO 3 , which means weak oxidation ability against objects [7]. Since photocatalytic activity of BiVO 4 is easily influenced by crystalline phase, crystallinity, and morphol- ogy, enhancement of its photocatalytic activity was achieved by improvement of preparation process [8]. The other methods for enhancement of photocatalytic activ- ity are grafting co-catalysts. There are two kinds of co-catalysts in terms of its function: one is for separation of electrons and the other is for separation of holes. The former representative co-catalysts are Pt, Fe 3+ , and Cu 2+ [9–12]. It was reported that Fe 3+ and Cu 2+ were grafted as amorphous oxide cluster [9,10], and reduced into Fe 2+ and Cu + by receiving one electron, respectively [11,12]. The reduced metal oxide cluster with reduced ions could return into the original state by giving more than one electron to molecu- lar oxygen. The latter ones are CoO x , CoPi (CoPO x ), IrO x , and RuO x which are used for water oxidation, among which CoPi is reported to be the most effective co-catalyst for water oxidation [13]. How- ever, there were few reports concerning co-grafting effects on 1010-6030 © 2013 The Authors. Published by Elsevier B.V. http://dx.doi.org/10.1016/j.jphotochem.2013.04.018 Open access under CC BY license. Open access under CC BY license. CORE Metadata, citation and similar papers at core.ac.uk Provided by Elsevier - Publisher Connector

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Page 1: Contents Journal of Photochemistry and Photobiology A ... · using a Peltier-cooled photon-counter head (Hamamatsu Photon-ics, H7421). For the measurements of H 2O , the photocatalyst

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Journal of Photochemistry and Photobiology A: Chemistry 262 (2013) 52– 56

Contents lists available at SciVerse ScienceDirect

Journal of Photochemistry and Photobiology A:Chemistry

journa l h om epa ge: www.elsev ier .com/ locate / jphotochem

nhanced photocatalytic activity of BiVO4 by co-grafting of metal ions andombining with CuBi2O4

asami Nishikawa ∗, Souta Hiura, Yasufumi Mitani, Yoshio Nosaka ∗∗

epartment of Materials Science and Technology, Nagaoka University of Technology, Nagaoka 940-2188, Japan

a r t i c l e i n f o

rticle history:eceived 19 February 2013eceived in revised form 16 April 2013ccepted 19 April 2013vailable online 29 April 2013

eywords:rafting co-catalystsetal ion deposition

omposite photocatalyst

a b s t r a c t

In order to improve photocatalytic activity of BiVO4, the co-grafting effects of two kinds of co-catalystsfor electron and hole separations were examined. At first, stabilization of electrons in BiVO4 by graftingFe3+ was confirmed by analyzing the formation of O2

− and H2O2 as reduction intermediates of O2. WhenBiVO4 was co-grafted with Fe3+ and CoPi as an electron separator and a hole separator, respectively,its photocatalytic activity for decomposition of gaseous acetaldehyde with visible light (470 nm LED)was enhanced compared to the BiVO4 grafted only by either co-catalyst. This indicated that co-graftingis effective to increase photocatalytic activity because electron and hole were effectively taken out ofthe BiVO4. Furthermore, by combined with CuBi2O4, a p-type semiconductor, the photocatalytic activityof BiVO4 was also increased. This is because holes and electrons, which were generated in the both

Metadata, citation and similar papers at

y Elsevier - Publisher Connector

uperoxide radicalydrogen peroxide

semiconductors, were successfully separated in BiVO and4 CuBi O ,2 4 respectively, due to combination ofelectrons in the BiVO4 with holes in the CuBi2O4. To promote the reaction between electrons in BiVO4

and holes in CuBi2O4, we examined co-grafting effects of two kinds of co-catalyst to the composite bypreparing the Cu/CuBi O –CoPi/BiVO photocatalyst.2 4 4 The photocatalytic activity was further enhancedwhen it was prepared in a suitable procedure that enables us to graft the reduction and oxidation co-catalysts only at each site.

. Introduction

Photocatalytic materials have been used in wide applicationuch as air purification, water purification, anti-virus and waterplitting [1,2]. Photocatalytic reaction proceeds owing to holes andlectrons generated in materials by absorbing light energy. Thehotogenerated holes have an oxidation ability and the photo-enerated electrons have a reduction ability. For decompositionf organic pollutants by photocatalytic reaction, the oxidationotential of hole needs to be more positive than +1 V that isedox potential of general organic compounds. In addition, theedox potential of electrons needs to be more negative thanhat of oxygen (O2/O2

− or H2O2) because surplus electrons that

re not consumed by reduction of oxygen would increase thelectron–hole recombination probability. Many materials for pho-ocatalyst, which meet these conditions, have been reported such

∗ Corresponding author. Tel.: +81 258 47 9306.∗∗ Corresponding author. Tel.: +81 258 47 9315.

E-mail addresses: [email protected] (M. Nishikawa),[email protected] (Y. Nosaka).

010-6030 © 2013 The Authors. Published by Elsevier B.V.ttp://dx.doi.org/10.1016/j.jphotochem.2013.04.018

Open access under CC BY license.

© 2013 The Authors. Published by Elsevier B.V.

as TiO2, SrTiO3, ZnO, ZrO2, WO3, and BiVO4 [3–6]. Among thesematerials, BiVO4 has attracted much attention in the recent yearsas one of the visible-light driven photocatalysts because of non-toxicity and its relatively narrow bandgap of ∼2.4 eV in monocliniccrystalline form. However, photocatalytic activity of BiVO4 is gen-erally low compared to TiO2 and WO3 photocatalysts because theelectronic potential in the valence band of BiVO4 is more nega-tive than those of TiO2 and WO3, which means weak oxidationability against objects [7]. Since photocatalytic activity of BiVO4 iseasily influenced by crystalline phase, crystallinity, and morphol-ogy, enhancement of its photocatalytic activity was achieved byimprovement of preparation process [8].

The other methods for enhancement of photocatalytic activ-ity are grafting co-catalysts. There are two kinds of co-catalysts interms of its function: one is for separation of electrons and the otheris for separation of holes. The former representative co-catalystsare Pt, Fe3+, and Cu2+ [9–12]. It was reported that Fe3+ and Cu2+

were grafted as amorphous oxide cluster [9,10], and reduced intoFe2+ and Cu+ by receiving one electron, respectively [11,12]. Thereduced metal oxide cluster with reduced ions could return intothe original state by giving more than one electron to molecu-

Open access under CC BY license.

lar oxygen. The latter ones are CoOx, CoPi (CoPOx), IrOx, and RuOx

which are used for water oxidation, among which CoPi is reportedto be the most effective co-catalyst for water oxidation [13]. How-ever, there were few reports concerning co-grafting effects on

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ry and Photobiology A: Chemistry 262 (2013) 52– 56 53

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hotocatalytic activity especially in gaseous phase. We expectedhat by co-grafting of both co-catalysts for separations of electronsnd holes, photocatalytic activity in gaseous phase would be furthernhanced. Moreover, complex of BiVO4 with the other materials of-type semiconductor is also effective for enhancing photocatalyticctivity.

In the present work, we examined the co-grafting effects of twoinds of co-catalysts for separation of electrons and holes and theombining effect with the other materials on the photocatalyticctivity of BiVO4. Candidate co-catalysts were Fe3+ and Cu2+ forlectron separators and CoPi for a hole separator in view of theirerformances and cost. For a candidate of combined material, weelected CuBi2O4 which is a p-type semiconductor with bandgapf 1.5 eV. Since the top of the valence band of CuBi2O4 is around1.0 V (vs. SHE at pH 0) [14] and the bottom of the conductionand of BiVO4 is around 0 V (vs. SHE at pH 0), we expect that pho-ogenerated holes in CuBi2O4 can react with electrons in BiVO4.urthermore, co-grafting effect of co-catalyst on the photocatalyticctivity of the CuBi2O4 and BiVO4 composite (CuBi2O4–BiVO4) wasxamined for enhancing photocatalytic activity of BiVO4.

. Experimental

.1. Materials

BiVO4 powder used was provided by Alfa Aesar. CuBi2O4 powdern tetragonal form was prepared by solid-phase synthesis from thetoichiometric mixture of CuO and Bi2O3 at 973 K for 24 h in air.he formation of CuBi2O4 was confirmed from its XRD pattern.

Fe3+ or Cu2+ was grafted on each photocatalyst by impregna-ion method. 10 mL of distilled water was added to a mixturef FeCl3·6H2O or CuCl2·2H2O and 1 g of photocatalysts. TheeCl3·6H2O or CuCl2·2H2O was weighted so that the weight fractionf Fe or Cu relative to each photocatalyst was 0.025–0.2 wt%. Eachixed solution was heated at 90 ◦C for 1 h under stirring. The solu-

ion was centrifuged and then the solid powder was sufficientlyashed with distilled water. The obtained powder was dried at

10 ◦C for 24 h.CoPi was grafted on BiVO4 grains by photochemical deposition

ethod. Potassium phosphate buffer solution of 0.1 M adjustedo pH 7, containing the desired amount of CoCl2 and BiVO4 pow-er, was irradiated for 1 hour by a 150 W Xe lamp. The CoCl2 waseighted so that the weight fraction of Co relative to each photo-

atalyst was 0.5–1.5 wt%. The powder was washed with distilledater and dried.

CuBi2O4–BiVO4 composites were prepared by mixing CuBi2O4nd BiVO4 powders in the desired weight ratios, that is,uBi2O4/(CuBi2O4 + BiVO4) = 0.1–0.5. After the mixing, the powderas usually heat treated at 150 ◦C for 3 h.

.2. Characterization

Optical absorption spectra of photocatalyst powders were mea-ured using a probe spectrometer (Avantes, Inc.) consisting ofvaSpec-2048, AvaLight-DH-S-BAL, and a reflection probe. Theecorded reflectance was converted to Kubelka–Munk functionhich corresponds to the absorbance.

Photocatalytic activities were measured for the acetaldehyde asollows. Photocatalyst powder of 0.15 g was spread on a Petri dishf 4 cm diameter and then the dish was placed in the circulated

eactor (270 cm3 in volume) with mixed gas of O2/N2 = 1:4. Thecetaldehyde gas of 100 �L and liquid water of 10 �L were injectednto the reactor. The dish placed in the reactor was irradiated by aED of � = 470 nm at the intensity of 20 mW/cm2, and the amount

Fig. 1. UV–vis absorption spectra of BiVO4, Fe/BiVO4, Cu/BiVO4 and CoPi/BiVO4

photocatalysts.

of generated CO2 was monitored by a gas analyzer (LI-COR, LI-840)equipped in the circulation reactor system [12].

The generation of O2− was observed by using a luminol

chemiluminescence probe method [15]. Photocatalyst of 15 mgwas added in 0.01 M NaOH solution of 3.5 mL in a quartz cell(1 cm × 1 cm) and then the suspension was irradiated by a He–Cdlaser (KIMMON, IK5652R-G) at � = 442 nm with 14 mW. After theirradiation, 50 �L of 7 mM luminol solution was immediately addedin the suspension. The chemiluminescence intensity was measuredusing a Peltier-cooled photon-counter head (Hamamatsu Photon-ics, H7421).

For the measurements of H2O2, the photocatalyst suspensionwas irradiated by the laser and then was kept in dark to eliminateO2

−. 50 �L of 7 mM luminol solution was added in the suspen-sion and then the suspension was kept in dark for 10 min. 50 �Lof hemoglobin solution was added in the suspension and then thechemiluminescence intensity was measured. To convert the chemi-luminescence intensities to the absolute concentration of O2

− andH2O2, the apparatus factor was calculated from the experimentwhere all luminol molecules are consumed for the reaction withan excess amount of H2O2.

3. Results and discussion

3.1. Grafting effects of co-catalysts for electron and holeseparations

Fig. 1 shows UV–vis spectra of BiVO4, Fe3+ grafted BiVO4(Fe/BiVO4), Cu2+ grafted BiVO4 (Cu/BiVO4), and CoPi grafted BiVO4(CoPi/BiVO4) photocatalyst powders. The absorption intensity ofthe BiVO4 starts to increase at around 520 nm. Those of the Fe/BiVO4and Cu/BiVO4 were almost the same as the BiVO4. This observationis different from the cases of Fe/TiO2 and Cu/TiO2 photocatalystpowders, where the absorption shoulder was observed at longerwavelength region than the absorption edge, due to the direct elec-tron transfer from valence band of TiO2 to the grafted Fe or Cu ions[9–12]. If the direct electron transfer from valence band of BiVO4to the grafted Fe or Cu ions would occur, the absorption shoulderat the absorption edge should be observed. Although the electronicpotential of conduction band of BiVO4 is more negative than thoseof Fe3+/Fe2+ or Cu2+/Cu+ [16], the direct electron transfer from thevalence band of the BiVO4 to the grafted Fe or Cu ions did not takeplace. Also for CoPi/BiVO4, new absorption did not appear. This indi-cated that by grafting CoPi, new electronic excitation, for examplefrom the BiVO4 valence band to the CoPi, did not occur.

For BiVO4, its valence band consists of Bi6s or hybrid Bi6s–O2p[6] and therefore valence electrons are localized at a Bi atom orbetween Bi and O atoms. By using a quantum mechanical terms,transition dipole moment for light absorption is determined by one

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54 M. Nishikawa et al. / Journal of Photochemistry and Photobiology A: Chemistry 262 (2013) 52– 56

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hyde would be achieved by the same reaction mechanism. Hence itwas concluded that CoPi played a role for hole separation (Fig. 4(c)).The increase of photocatalytic activity of CoPi/BiVO4 would beattributed to the suppression of electron–hole recombination by

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ig. 2. Photocatalytic activities of various BiVO4 powders modified with Fe and Cu iof gaseous acetaldehyde under visible light irradiation for 1 h with 470-nm LED. Th

enter integral. In other words, wave functions, or electron distribu-ions, must be overlapped between the ground state and the excitedtate to have a light absorption. Therefore, in the present case, whenhemical bond of Bi O Fe or Bi O Cu is formed by grafting Fe oru ions on the BiVO4 surface, the electronic excitation by light irra-iation would be difficult to occur within the O Fe or O Cu bond.n the other hand, the valence band of TiO2 mainly consists of O2prbitals. Therefore electrons in the valence band possibly involve Otoms next to the grafted metal ions, and they could be excited tohe metal ions.

Fig. 2 shows the amounts of CO2 generated in 1 h by pho-ocatalytic decomposition of gaseous acetaldehyde under visibleight irradiation with 470 nm LED. For the bare BiVO4 alone, amall amount of CO2 of 3 ppm/h was observed, indicating thatrobability of electron–hole recombination was high. In contrast,hen Fe ions were grafted on the BiVO4 surface, photocatalytic

ctivity was increased up to 30 ppm/h at Fe grafting ratio of.1 wt%.

To examine the role of Fe ions, the amounts of O2− and H2O2

enerated under visible light irradiation at � = 442 nm was mea-ured and the experimental results are shown in Fig. 3. For the bareiVO4, O2

− was preferentially generated compared to H2O2. Thisndicated that the electron photoproduced at the conduction bandirectly reduced O2 into O2

− because electronic potential of theonduction band bottom of BiVO4 is around −0.42 V (vs. SHE at pH) which is more negative than that of O2/O2

− = −0.033 V (vs. SHE atH 7). In contrast, for Fe/BiVO4, the amount of O2

− was decreasedhile that of H2O2 was increased. This indicated that the grafted Fe

ons which receive electrons can reduce O2 into H2O2. Therefore,he redox potential of Fe3+/Fe2+ in the grafted Fe ions may be nearo the redox potential of (O2, 2H+)/H2O2 of +0.695 V (vs. SHE at pH). The Fe ions would receive electrons from conduction band notrom the direct transfer from valence band as shown in Fig. 4(a).he amount of generated H2O2 seems to be somewhat small. Weonsidered that the generated H2O2 would decompose into H2Ond O2 by disproportionation due to a catalytic effect of the graftede ions. For the Cu/BiVO4, the photocatalytic activity was increasedimilarly to the case of the Fe/BiVO4. Considering that redox poten-ial of Cu2+/Cu+ = +0.16 (vs. SHE at pH 0), Cu ions can also receive

lectrons from conduction band like Fe ions, indication that Cu ionslso played an important role for electron separation. Based on pre-ious a report [11], Cu ions which receive electrons would reduce2 into O2

−.7)

CoPi. Activities were presented by the amounts of CO2 generated by decompositionbers indicate the content of co-catalysts in unit of wt%.

For the CoPi/BiVO4, the photocatalytic activity was alsoincreased. Based on a previous report, Co2+ turns to Co3+ or Co4+

by giving one or two electrons to the valence band of host mate-rials and then generated Co4+ can oxidize H2O into O2 [13]. In thepresent work, photocatalytic decomposition of gaseous acetalde-

120100806040200

Irradiation time (s)

Fig. 3. Generation of O2− and H2O2 under visible light irradiation at � = 442 nm for

bare BiVO4 (�) and Fe/BiVO4 (�; Fe ion grafted BiVO4).

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M. Nishikawa et al. / Journal of Photochemistry and Photobiology A: Chemistry 262 (2013) 52– 56 55

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CuBi2O4:BiVO4 = 1:4, though the obtained maximum activity waslower than the cases of grafting co-catalysts shown in Fig. 2.

Based on the UV–vis reflectance spectra, absorption intensity at� = 470 nm for CuBi2O4 was higher than that of BiVO4, though the

Fig. 4. Charge transfer processes of (a) Fe/BiVO4

he effective hole separation although the oxidation potential ofo4+/Co2+ is more negative than that of BiVO4 valence band. Amongingle grafted co-catalysts used, 1.0 wt%-CoPi/BiVO4 showed theighest photocatalytic activity of 49 ppm/h, which was about 16imes as high as the bare BiVO4.

In the case of single grafting of co-catalyst, by changing graftingatio alone, the increment of photocatalytic activity was restricted.herefore, further charge separation by co-grafting of co-catalystsor electron and hole separations is needed for enhancing photocat-lytic activity. The recombination caused by remained free carrieror single grafting can be suppressed by co-grafting. Fe ions areandomly grafted on the BiVO4 surface and, in contrast, CoPis areelectively grafted on the oxidation site of the BiVO4 surface byhotodeposition. Owing to the control of each grafting procedure,ne could graft Fe3+ and CoPi at each different site. Thus, we grafted.0 wt%-CoPi on the BiVO4 after grafting 0.1 wt%-Fe ions to preventhe grafting of the CoPi onto the Fe ions, which would promote aeverse reaction. The co-grafted BiVO4 showed further high photo-atalytic activity of 63 ppm/h compared to the single grafted BiVO4,hich was 21 times as high as the bare BiVO4. This indicates that

oth electrons and hole were successfully taken out of the BiVO4s illustrated in Fig. 4(d).

.2. Combining effect with CuBi2O4

Fig. 5 shows UV–vis spectra of CuBi O –BiVO composites. The

2 4 4bsorption intensity of the CuBi2O4 alone starts to increase atround 850 nm. The spectra of the CuBi2O4–BiVO4 composites wereombined by summing the absorptions of the bare BiVO4 and

Fig. 5. UV–vis absorption spectra of CuBi2O4–BiVO4 composites.

u/BiVO4, (c) CoPi/BiVO4 and (d) Fe + CoPi/BiVO4.

CuBi2O4. Therefore, BiVO4 was simply contacted with CuBi2O4 anddid not react with CuBi2O4 at their interface.

Fig. 6 shows amounts of CO2 generated in one hour by pho-tocatalytic decomposition of gaseous acetaldehyde under visiblelight irradiation at � = 470 nm. For the bare CuBi2O4, photocatalyticactivity was not observed at all. Even after the Cu and Fe ionswere grafted on the CuBi2O4, the photocatalytic activity was notobserved (data not shown). This is due to the CuBi2O4 valence bandtop of +1.0 V (vs. SHE at pH 0), which is too negative to decomposeorganic pollutants. In contrast, for the CuBi2O4–BiVO4 composites,photocatalytic activities appeared. This indicated that the electronsphotogenerated in the BiVO4 reacted with the holes photogen-erated in the CuBi2O4 and then the remained holes and electronswere successfully separated in BiVO4 and CuBi2O4, respectively,because BiVO4 and CuBi2O4 alone show little or no photocatalyticactivity. The maximum photocatalytic activity of 22 ppm/h wasobtained at the weight ratio, CuBi2O4/(CuBi2O4 + BiVO4), of 0.2, or

Fig. 6. Photocatalytic activities of CuBi2O4–BiVO4 composite photocatalysts. Activi-ties are presented by the amounts of CO2 generated by photocatalytic decompositionof gaseous acetaldehyde under visible light irradiation for one hour with 470-nmLED. The numbers indicate the weight ratio of CuBi2O4 to CuBi2O4 + BiVO4.

Page 5: Contents Journal of Photochemistry and Photobiology A ... · using a Peltier-cooled photon-counter head (Hamamatsu Photon-ics, H7421). For the measurements of H 2O , the photocatalyst

56 M. Nishikawa et al. / Journal of Photochemistry and

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bsorbance ratio between two materials could not be estimatedrom Fig. 5. Since the component ratio (4:1) of BiVO4 presented the

aximum activity, the absorption of CuBi2O4 at 470 nm should be times larger than that of BiVO4 to balance the number of photonsbsorbed in each semiconductor. As stated above, the maximumctivity obtained was smaller than that obtained by grafting co-atalyst. Namely, to increase the photocatalytic activity, graftingf co-catalyst was effective because the co-catalyst was stronglydsorbed on the photocatalyst surface, leading to smooth electronransfer. In contrast, for the CuBi2O4–BiVO4 composite, electronransfer through the interface between BiVO4 and CuBi2O4 is dif-cult to occur because electron–hole recombination probability inach semiconductor was high.

To increase the frequency of recombination between electronshotogenerated in BiVO4 and holes photogenerated in CuBi2O4, wexamined the grafting of co-catalyst on the CuBi2O4–BiVO4 com-osite. CoPi as a hole trap was grafted on the BiVO4 and Cu2+ asn electron trap was grafted on the CuBi2O4. Where the weightatio of the composite was fixed to 0.2. Its photocatalytic activityas largely increased to 185 ppm/h as shown in Fig. 6. This valueas about 60 times as high as that of the bare BiVO4 and higher

han that of the BiVO4 co-grafted with Fe3+ and CoPi shown inig. 2. This indicates that electrons, which have been stabilized inhe BiVO4 by grafting CoPi, can easily react through the interfaceith holes in the CuBi2O4, which have been stabilized by graftingu2+. This effective separation process is schematically shown inig. 7.

Next, we prepared the co-catalyst grafted composite by graft-ng Cu2+ and then CoPi after mixing CuBi2O4 and BiVO4 in the

eight ratio of 0.2. Its photocatalytic activity was decreased to4 ppm/h (data not shown in Fig. 6). This is due to the obstruction of

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Photobiology A: Chemistry 262 (2013) 52– 56

oxidation site because Cu2+ was randomly adsorbed on the com-posite surface, resulting in the promotion of reverse reaction.Therefore, it is important for this composite photocatalysts thatco-catalysts for electron and hole separations could be graftedonly at reduction site and oxidation site, respectively. In otherwords, Cu2+ should be grafted on CuBi2O4 before the preparationof CuBi2O4–BiVO4 composite. Thus, it was demonstrated that, bya suitable grafting procedure, co-catalysts can also enhance theactivity of composite photocatalysts.

4. Conclusions

We examined the effects of grafting of two kinds of co-catalystson the photocatalytic activity of BiVO4. For the BiVO4 co-graftedwith Fe3+ and CoPi as electron and hole separators, respectively(Fig. 4(d)), its photocatalytic activity was enhanced compared tothe cases of single co-catalyst grafting for electron or hole separa-tion (Fig. 4(b) and (c)). Therefore, co-grafting was demonstrated tobe effective for enhancing photocatalytic activity because electronand hole were effectively stabilized. Furthermore, by compositedwith CuBi2O4, the photocatalytic activity was also increased. Thisis because electrons photogenerated in the BiVO4 reacted withholes that photogenerated in the p-type CuBi2O4 semiconductorand then holes and electrons were successfully separated in BiVO4and CuBi2O4, respectively. In addition, it was revealed that co-grafting of two kinds of co-catalyst to the composite was effectiveto promote the reaction between electrons in BiVO4 and holes inCuBi2O4 (see Fig. 7), leading further enhancement of the photocat-alytic activity.

References

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