亚洲免费av电影一区二区三区,日韩爱爱视频,51精品视频一区二区三区,91视频爱爱,日韩欧美在线播放视频,中文字幕少妇AV,亚洲电影中文字幕,久久久久亚洲av成人网址,久久综合视频网站,国产在线不卡免费播放

        ?

        Isoelectric point-controlled preferential photodeposition of platinum on Cu2O-TiO2 composite surfaces

        2019-06-20 12:35:12MeiWngYunxuLiuDnLiJunwngTngWeixinHung
        Chinese Chemical Letters 2019年5期

        Mei Wng,Yunxu Liu,Dn Li,Junwng Tng,Weixin Hung,*

        a Hefei National Laboratory for Physical Sciences at the Microscale, Key Laboratory of Surface and Interface Chemistry and Energy Catalysis of Anhui Higher Education Institutes, CAS Key Laboratory of Materials for Energy Conversion and Department of Chemical Physics, University of Science and Technology of China, Hefei 230026, China

        b School of Pharmacy, Anhui University of Chinese Medicine, Anhui Academy of Chinese Medicine, Hefei 230012, China

        c Department of Chemical Engineering, University College London, Torrington Place, London WC1E 7JE, UK

        Keywords:

        Photocatalysts

        Photocatalytic water reduction

        Selective adsorption

        Oxide composite

        Co-catalyst

        ABSTRACT

        Photodeposition emerges as a convenient method to synthesize metal particles on semiconductor supports.In this work,we study the photodeposition of Pt on Cu2O-TiO2 composite surfaces employing H2PtCl6 aqueous solution as the precursor and reveal a key role of isoelectric point of oxide surfaces on the Pt photodeposition process.Under the photodeposition conditions, Pt metal particles are facilely photodeposited on TiO2 support; on Cu2O-TiO2 composite supports, the Cu2O surface is positively charged and enriched with photo-excited holes while the TiO2 surface is negatively charged and enriched with photo-excited electrons.This lead to the preferential adsorption of PtCl62-anion precursor on the Cu2O surface of Cu2O-TiO2 composite and the dominant formation of Pt oxide particles on Cu2O surface but few Pt metal particles on TiO2 surface.Consequently,the activity of resulting Pt/Cu2O-TiO2 composite photocatalysts in photocatalytic water reduction decreases as the Cu2O content increases.These results deepen the understanding of photodeposition processes on oxide composite surfaces.

        Photocatalytic water splitting has been extensively studied as an ideal method to produce hydrogen since the report of the Honda-Fujishima effect of water splitting using a TiO2electrode[1].It consists of photoexcitation of semiconductor photocatalyst to generate electrons and holes in the bulk, transfer of photoexcited carriers from the bulk to the surface, and photoexcited electrons-participated water reduction to H2and photoexcited holes-participated water oxidation to O2on the surface[2-4].Among various semiconductor photocatalysts for photocatalytic water splitting, TiO2is considered as a potential commercial photocatalyst due to the favorable electronic energy band structure and high photo-chemical stability [5-7].However,TiO2photocatalyst suffers from the wide band gap of around 3.2 eV [8-10]and rapid recombination of photoexcited electronhole pairs[5,6].Great effort has been thus devoted to suppressing the recombination of photoexcited electron-hole pairs to increase the efficiency of TiO2in photocatalytic water splitting,and the cocatalyst strategy is very effective.Noble metals(Pt,Pd,Au and Ag)and transitional metal oxides have been demonstrated as efficient co-catalysts for TiO2to suppress the charge recombination via the transfer of photoexcited electrons and holes from TiO2to the cocatalyst, respectively [11-20].Recently space-separated noble metal and transitional metal oxide co-catalysts have been successfully loaded on TiO2to allow simultaneous transfer of photoexcited electrons and holes from TiO2respectively to the noble metal and transitional metal oxide co-catalysts [11-13].

        Utilizing photoexcited electrons to reduce metal cations,photodeposition emerges as a convenient method to load metal particles on semiconductors [21-28].Photodeposition was also successfully used for a simultaneous loading of Au and CoOxrespectively on electron-enriched {010} face and hole-enriched{110}face of BiVO4nanocrystals[11].However,there are few works reported on photodeposition of metal particles on oxide composite surfaces.Cu2O acts as a nice hole-scavenger co-catalyst for TiO2[29-31].In this letter,we report the structures and photocatalytic performances in water reduction of Pt/Cu2O-TiO2composite photocatalysts prepared by photodeposition of Pt particles on Cu2O-TiO2composite surfaces.The results reveal an interesting isoelectric point-controlled preferential adsorption and photodeposition of Pt species on Cu2O-TiO2composite surfaces.

        Experimental details are described in the Supporting Information.Pt with loadings of about 0.5% was photodeposited on TiO2and Cu2O-TiO2composites employing H2PtCl6aqueous solutions as the Pt precursor.Under the photodeposition condition, the pH values of the solutions were measured to be 3.6.Table 1 summarizes compositions and BET specific surface areas of various photocatalysts.Both Pt loadings and BET specific surface areas are similar for all photocatalysts.Fig.1 shows photocatalytic H2productions as a function of reaction time of various photocatalysts in photocatalytic water reduction illuminated with simulated solar light.It can be seen that the photocatalytic H2production increases linearly with the reaction time for various photocatalysts,indicating the stability of these photocatalysts.The calculated mass-specific photocatalytic H2production rates of all photocatalysts are summarized in Table 1.0.5%Pt/TiO2exhibits a H2production rate of 4.8 mmol g-1h-1,but the H2production rate of Pt-Cu2O-TiO2composite photocatalysts keeps decreasing with the loading of Cu2O.These results suggest that the Pt and Cu2O species in Pt/Cu2O-TiO2composite photocatalysts exert a negative effect,instead of a synergetic effect, on promoting the photocatalytic performance of TiO2.

        Table 1 Compositions, BET specific surface areas and mass-specific photocatalytic H2 productions of various photocatalysts.

        Fig.1.Photocatalytic H 2 production as a function of reaction time of various Pt/Cu2O-TiO2 under simulated solar light irradiation.

        Fig.2A shows XRD patterns of various photocatalysts,in which all observed diffraction patterns could be indexed to anatase TiO2(JCPDS card: No.21-1272).No peaks associated with Cu or Pt species could be identified.This may be due to the fine dispersions of copper and platinum species on TiO2and/or the low loadings of copper and platinum in all photocatalysts.Surface structures of all photocatalysts were characterized with XPS.As shown in Fig.S1(Supporting information), all Pt/Cu2O-TiO2composite photocatalysts exhibit the same Ti 2p3/2binding energy at 458.8 eV and Cu 2p3/2binding energy at 932.4 eV that respectively correspond to TiO2and Cu2O [30].However, they exhibit Cu2O loadingdependent Pt 4f XPS features (Fig.2B).A peak at around 75.6 eV corresponds to an energy loss peak of TiO2,and other peaks at 70.9/74.3, 72.8/76.1, and 74.2/77.5 eV can be assigned to the 4f7/2/4f5/2components of metallic Pt,Pt2+,and Pt4+species,respectively[32-34].Fig.2C shows the Pt speciation in various photocatalysts.0.5%Pt/TiO2exhibits dominant metallic Pt species with minor Pt2+species.With the Cu2O loading of Pt/Cu2O-TiO2increasing, the metallic Pt species decreases and could not be observed in Pt/1%Cu2O-TiO2;the Pt2+species increases,reaches the maximum in Pt/0.5%Cu2O-TiO2and then slightly decreases in Pt/1%Cu2O-TiO2;and the Pt4+species emerges in Pt/1%Cu2O-TiO2.These XPS results demonstrate that the Pt species changes from the metallic Pt to the Pt cations in our Pt/Cu2O-TiO2photocatalysts prepared by photodeposition as the Cu2O loading increases.

        Fig.2.(A)XRD patterns,(B)Pt 4f XPS spectra with peak-fitting results,and(C)calculated Pt speciation of(a)0.5%Pt/TiO2,(b)Pt/0.005%Cu 2O-TiO2,(c)Pt/0.05%Cu2O-TiO2,(d)Pt/0.5%Cu2O-TiO2 and(e)Pt/1%Cu2O-TiO2 photocatalysts.The red line in Fig.2A represents the standard XRD pattern of anatase TiO2(JCPDS Card No.21-1272).The scatter points and solid lines in Fig.2B respectively represent the original XPS spectra and peak-fitted XPS spectra.

        Fig.3.Representative TEM and HRTEM images of(A1 and A2)0.5%Pt/TiO2,(B1,B2,B3)Pt/0.005%Cu2O-TiO2,(C1,C2,C3)Pt/0.05%Cu2O-TiO2,(D1,D2,D3)Pt/0.5%Cu2O-TiO2,and (E1, E2, E3) Pt/1%Cu2O-TiO2.Lattice spacings of 0.35, 0.21, 0.23, 0.26 and 0.22 nm correspond to TiO2(101), Cu2O(200), Pt(111), PtO(101) and PtO2(011), respectively.

        Representative TEM and HRTEM images of Pt/TiO2and Pt/Cu2OTiO2photocatalysts are shown in Fig.3,Figs.S2 and S3(Supporting information).The identified lattice spacings of 0.35,0.21,0.23,0.26 and 0.22 nm arise from TiO2(101),Cu2O(200),Pt(111),PtO(101)and PtO2(011),respectively[29,30,35,36].Fig.S3 gives FT-transformed patterns of TRTEM images of individual particles to distinguish nanoparticles with similar observed lattice spacings.As reported in our previous paper[29],TiO2exhibits a rod shape,and Cu2O forms a thin film on TiO2in Cu2O-TiO2composites up to 1%Cu2O-TiO2,forming TiO2(core)/Cu2O(thin film shell)rod structures in which the Cu2O shell thickness increases with the Cu2O loading.Pt/TiO2and Pt/Cu2O-TiO2photocatalysts remain rod shapes, and Cu2O exists as thin layers on TiO2in all Pt/Cu2O-TiO2photocatalysts,but exposed TiO2surfaces are always present.This is also confirmed by the DRIFTS results of CO adsorption on Pt/Cu2O-TiO2photocatalysts (Fig.S4 in Supporting information) in which the vibrational band of CO adsorption at Ti(IV) sites is observed for Pt/Cu2O-TiO2photocatalysts [37].Thus the original TiO2(core)/Cu2O (thin film shell) rod structures of Cu2O-TiO2composites get destroyed after the photodeposition processes in H2PtCl6aqueous solutions.Metallic Pt nanoparticles of 2-3 nm can be easily identified in Pt/TiO2, Pt/0.005%Cu2O-TiO2and Pt/0.05%Cu2O-TiO2but few PtO nanoparticles is found although the XPS results suggest the presence of minor PtO species.This could be attributed to the generally much higher dispersion of Pt oxides than Pt metal supported on oxide surfaces.In Pt/0.5%Cu2O-TiO2and Pt/1%Cu2OTiO2photocatalysts with Pt oxides as the dominant Pt species,PtO and PtO2nanoparticles of 3-4 nm are easily observed but Pt nanoparticles can only be occasionally found.It is found that the Pt species supported on TiO2are always metallic Pt nanoparticles while those supported on Cu2O include metallic Pt nanoparticles in Pt/0.005%Cu2O-TiO2and Pt/0.05%Cu2O-TiO2but then are exclusively PtO and PtO2nanoparticles in Pt/0.5%Cu2O-TiO2and Pt/1%Cu2O-TiO2.Meanwhile,much more Pt species are photodeposited on the Cu2O surface of Cu2O-TiO2composites than on the TiO2surface.This agrees with the XPS results of dominant Pt oxides species since the photodeposited Pt species on TiO2is mainly metallic Pt nanoparticles.

        Fig.4.Zeta potentials of TiO2, Cu2O, and various Cu2O/TiO2 composites as a function of pH values of aqueous solution.

        The above spectroscopic and microscopic characterization results demonstrate that the presence of Cu2O layers on TiO2strongly affects the photodeposition processes of Pt.The photodeposited Pt species is preferentially formed on the Cu2O surface,and changes from metallic Pt nanoparticles to PtO and PtO2nanoparticles as the Cu2O layers thicken.It is reasonable that the synthesized Pt/Cu2O-TiO2photocatalysts with dominant PtO and PtO2nanoparticles on Cu2O surface and few Pt nanoparticles on TiO2surface are less active than the synthesized Pt/TiO2catalyst with Pt nanoparticles in photocatalytic water reduction, as experimentally observed.

        Fig.5.Schematic illustration of the photodeposition process of H2PtCl6 on Cu2O/TiO2 composite.The yellow,red,blue spheres represent TiO2,Cu2O,Pt species,respectively.

        During the photodeposition process, the [PtCl4]2-precursor needs to adsorb on the oxide surface prior its photoreduction.Depending on its isoelectric point and the pH value of aqueous solution, an oxide surface in the aqueous solution is negatively,neutrally, or positively charged.We measured Zeta potentials of TiO2,Cu2O,and various Cu2O/TiO2composites as a function of pH values (Fig.4), from which the isoelectric point of TiO2, 0.005%Cu2O/TiO2, 0.05%Cu2O/TiO2, 0.5%Cu2O/TiO2, 1%Cu2O/TiO2and commercial Cu2O is determined as 3.1, 4.8, 5.3, 5.8, 7.1 and 10.2,respectively.The pH value of employed H2[PtCl4]aqueous solution is measured to be 3.6, thus the TiO2surface of Cu2O-TiO2composites is locally negatively charged while the Cu2O surface is locally strongly positively charged.Based on these observations,we proposed a photodeposition mechanism of Pt on Cu2O-TiO2composites (Fig.5).Under the employed photodeposition conditions, the negatively-charged [PtCl4]2-precursor adsorb majorly on the strongly positively-charged Cu2O surface of Cu2O-TiO2composites but minorly on the negatively-charged TiO2surface, resulting in the preferential adsorption of [PtCl4]2-precursor on Cu2O surface of Cu2O-TiO2composites.Illuminated with light,both Cu2O and anatase TiO2are photoexcited to produce the electron-hole carriers, and the excited electrons in the conduction band of Cu2O tend to transfer to the conduction band of TiO2at the Cu2O-TiO2junction interface while the excited holes in the valence band of TiO2tend to transfer to the valence band of Cu2O.This leads to electron-rich TiO2and hole-rich Cu2O in Cu2OTiO2composites.Thus, the[PtCl4]2-species on electron-rich TiO2surface can be facilely reduced to form metallic Pt nanoparticles while those on hole-rich Cu2O surface can not be adequately reduced and tend to form PtO nanoparticles and even PtO2nanoparticles.The reduction extent of [PtCl4]2-species on Cu2O surface decreases as its thickness on TiO2increases.Thus, oxide isoelectric point plays an important role in the photodeposition of Pt on Cu2O-TiO2composite surfaces via preferential adsorption of[PtCl4]2-precursor.These reveal the important role of surface chemistry in photo-induced chemical processes on solid surfaces[38].

        In summary, we have successfully investigated the photodeposition processes of Pt on Cu2O-TiO2composite surfaces employing H2PtCl6aqueous solution as the precursor and revealed a key role of oxide isoelectric point-controlled adsorption of[PtCl4]2-precursor in the photodeposition of Pt on Cu2O-TiO2composites.Under the photodeposition conditions, the PtCl62-precursor adsorb dominantly on positively-charged and holeenriched Cu2O surface of Cu2O-TiO2composites, but minorly on negatively-charged and electron-enriched TiO2surface.This leads to the dominant formation of Pt oxide particles on Cu2O surface but few Pt metal particles on TiO2surface.Consequently,the activity of resulting Pt/Cu2O-TiO2composite photocatalysts in photocatalytic water reduction decreases as the Cu2O content increases.These results deepen the understanding of photodeposition processes on oxide composite surfaces.

        Acknowledgments

        This work was financially supported by the National Key R&D Program of Ministry of Science and Technology of China (No.2017YFB0602205), the National Natural Science Foundation of China (Nos.21525313, 91745202, 21703001) and the Changjiang Scholars Program of Ministry of Education of China.

        Appendix A.Supplementary data

        Supplementarymaterialrelatedtothisarticlecanbefound,inthe online version,at doi:https://doi.org/10.1016/j.cclet.2019.01.017.

        大香焦av一区二区三区| 国产亚洲午夜精品| 亚洲人妻中文字幕在线视频| 国产高潮迭起久久av| 亚洲精品国产成人片| 国产人妻久久精品二区三区| 国产日韩欧美911在线观看| 少妇又色又爽又刺激的视频| 最近免费中文字幕中文高清6 | 亚洲产国偷v产偷v自拍色戒| 一二三四中文字幕日韩乱码| 精品人妻69一区二区三区蜜桃| 中文字幕日韩三级片| 久久国产36精品色熟妇| 人妻在线日韩免费视频| 国产精品久久综合桃花网| a√无码在线观看| 久久精品亚洲国产av网站| 国产国产人免费人成免费视频| 亚洲暴爽av天天爽日日碰| 无码国产精品一区二区免费式芒果 | 国产精品亚洲专区无码不卡| 国产成人国产三级国产精品 | 日日碰狠狠添天天爽超碰97| 欧美精品v欧洲高清| 久久这里只有精品黄色| 国产毛女同一区二区三区| 性色av浪潮av色欲av| 久久福利青草精品资源| 久久久精品国产老熟女| 成人中文乱幕日产无线码| 69精品丰满人妻无码视频a片| 日本激情视频一区在线观看| 亚洲精选自偷拍一区二| 无码任你躁久久久久久久| 亚洲动漫成人一区二区| 国产一区二区白浆在线观看| 性久久久久久| 中文字幕无码无码专区| 一本久久综合亚洲鲁鲁五月夫| 国产18禁黄网站免费观看 |