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Eco-Friendly Photochemical Production of H2O2 through O2 Reduction over Carbon Nitride Frameworks Incorporated with Multiple Hetero-Elements Gun-hee Moon, Mamoru Fujitsuka, Sooyeon Kim, Tetsuro Majima, Xinchen Wang, and Wonyong Choi ACS Catal., Just Accepted Manuscript • DOI: 10.1021/acscatal.6b03334 • Publication Date (Web): 13 Mar 2017 Downloaded from http://pubs.acs.org on March 14, 2017
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ACS Catalysis
Eco-Friendly Photochemical Production of H2O2 through O2 Reduction over Carbon Nitride Frameworks Incorporated with Multiple Hetero-Elements
4 5 6 7 8 9 10 11 12
Gun-hee Moon1, Mamoru Fujitsuka2, Sooyeon Kim2, Tetsuro Majima2, Xinchen Wang3, and Wonyong Choi1* 1
Department of Chemical Engineering & Division of Environmental Science and Engineering, Pohang University of Science and Technology (POSTECH), Pohang, 37673 Korea 2
The Institute of Scientific and Industrial Research (SANKEN), Osaka University, Osaka 567-0047, Japan 3
College of Chemistry, Fuzhou University, Fuzhou 350002, P. R. China
13 14 15 16
Submitted to
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ACS Catalysis
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* To whom correspondence should be addressed (W. Choi)
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E-mail:
[email protected] Fax: +82-54-279-8299
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Abstract
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We report that in-situ incorporation of both potassium and phosphate species into
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polymeric carbon nitride (CN) framework highly enhanced the photo-production of
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hydrogen peroxide (H2O2) without the use of any noble metal co-catalysts. The
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incorporation of the earth-abundant hetero-elements (K, P, and O) (i) introduced the
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negative surface charge over the entire pH through the surface functionalization by
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phosphate species, (ii) increased the lifetime of the transient species in picosecond
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timescale via the formation of charge separation states, (iii) facilitated the interfacial
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electron transfer to dioxygen, and (iv) inhibited the decomposition of in-situ generated
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H2O2. As a result, the modified CN showed the apparent quantum yields (Φ: for H2O2
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production) that are enhanced by about 25 and 17 times (Φ420 = 8.0%; Φ320 = 26.2%) from
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those of bare CN (Φ420 = 0.32%; Φ320 = 1.55%) under monochromatic irradiation of 420
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and 320 nm, respectively. This study clearly demonstrated a simple way to design multiple
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hetero-elements incorporated CN compounds that consist of earth-abundant elements only
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(C, N, K, P, O) for the development of practical and economical solar conversion
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photocatalytic materials.
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Keywords: Photocatalysis, Carbon nitride, Solar fuel, Hydrogen peroxide synthesis, Proton
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coupled electron transfer (PCET)
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1. Introduction
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The
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oxide/sulfide/nitride should overcome many critical problems including a low solar
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light absorption, a low conversion/selectivity, a lack of long-term stability, a high
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operating cost, etc.1,2 In this regard, polymeric carbon nitride consisting of earth-
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abundant carbon and nitrogen elements only is an attractive material because of its
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visible light absorption capability and the superior stability against photo-corrosion.
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Furthermore, the conduction band (CB) and valence band (VB) potentials (ECB = -
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1.3 VNHE and EVB = 1.4 VNHE at pH 7) are thermodynamically suitable for various
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reactions such as water-splitting, partial oxidation, oxygen reduction reaction (ORR),
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and the degradation of organic pollutants.3 On the other hand, a still low photo-
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conversion efficiency needs to be overcome, so various strategies such as
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morphology control, doping, bandgap engineering, co-catalysts loading, and
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hybridization with other materials have been actively investigated.4
practical
application
of
photocatalysts
associated
with
metal
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Hydrogen peroxide (H2O2) is an eco-friendly oxidant that is widely utilized for
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chemical synthesis, disinfection, bleaching agent, liquid propellant, Fenton reaction,
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etc. H2O2 can be produced by the reaction of H2 and O2 via anthraquinone method5
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or the reduction of O2 through proton-coupled electron transfer (PCET) (O2 + 2H+ +
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2e- → H2O2 ; E0 = 0.695 VNHE).6 The photosynthetic production of H2O2 through
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PCET is safe and environmentally-benign since it needs only water, dioxygen, and
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solar light. Most of metal oxide semiconductors that are widely employed for
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photosynthetic and photocatalytic conversions are active under UV light region only,
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and H2O2 having a strong affinity to the oxide surface decomposes as soon as it is
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produced.7,8 Recently, a relatively high photo-conversion efficiency of H2O2
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production was observed over polymeric CN since tri-s-triazine moieties consisting
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of CN polymeric matrix accelerate a selective two electron transfer to O2 via the
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formation of superoxo radical and 1,4-endoperoxide species sequentially.9
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Moreover, the photoefficiency of bare CN for H2O2 production could be enhanced
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through the modification of bandgap (by incorporation of pyromellitic diimide into
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polymeric CN matrix)10 and surface properties (by amine rich mesoporous structure)
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of CN.11 In this work, potassium, phosphorus, and oxygen elements were simply
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introduced into polymeric CN matrix by solid-state thermal polymerization of
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melamine in the presence of potassium phosphate dibasic (KPD, K2HPO4). Not only
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the surface catalytic behaviour induced by the phosphate species but also the
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formation of charge trapping sites originated from hetero-elements existing over
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polymeric CN matrix, established a high apparent quantum efficiency (AQE) for
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H2O2 production without adding any noble metal cocatalysts.
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2. Results and Discussion
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2.1. Hetero-Elements (K, P, and O) Incorporated CN Polymeric Structure
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The X-ray diffraction (XRD) patterns in Figure 1a show that the in-situ
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incorporation of hetero-elements into CN framework induced a significant reduction
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of the typical peaks of CN (at 27.5o and 13.0o), ascribed to the interlayer (002)
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stacking and the interplanar structural packing of tri-s-triazine units forming 1-
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dimensional melon strands, respectively.12 According to the KPD content added (x
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mmol; x = 1, 3, 5, 7.5, and 10), the samples are noted as KPD-CN-1, 3, 5, 7.5, and
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10, respectively. When the KPD content increased from x = 1 to 10 at 550 oC, the
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peak intensity at 13.0o and 27.5o gradually decreased (Figure S1a), which indicates
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that the polymeric structure of KPD-CN-x is possibly derived from the simultaneous
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condensation of melamine and KPD. Basically, prior to reaching the sublimation
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temperature of melamine (350 oC), the condensed melamine phosphates consisting
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of various phosphate species such as orthophosphate, pyrophosphate, polyphosphate,
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and polymethaphosphate can be generated by the step-by-step condensation
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reaction,13 which are known as a halogen-free flame retardant with an excellent
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thermal resistance.14 In the case of sole melamine, melamine-based products are
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dominant up to 350 oC, but tri-s-triazine (melem) starts to be generated as a result of
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melamine rearrangement over 350 oC.15 With further increase of the temperature, the
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condensation of tri-s-triazine to polymeric networks induces the formation of CN
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around 520 oC, and the decomposition is started to be proceeded above 600 oC. The
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XRD pattern of KPD-CN-7.5 exhibits that the melamine and KPD peaks disappeared
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with increasing the calcination temperature (Figure S1b), and any trace peaks of
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original melamine and KPD were not observed at all (Figure S1c and S1d). The
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result supports that the hetero-elements were well incorporated into the CN
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framework without leaving melamine or KPD compound unreacted.
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Diffuse reflectance UV-visible spectra (DRS) demonstrates that the incorporation
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of KPD into CN increased the absorbance over UV light region, whilst the change of
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visible light absorption was almost negligible (Figure 1b and Figure S2a). As a result,
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the difference of bandgap size between CN and KPD-CN-7.5 was estimated to be
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only about 0.08 eV. To confirm the shift of the CB and VB potential affected by
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KPD, the X-ray photoelectron spectroscopy (XPS) VB analysis and the
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electrochemical Mott-Schottky analysis were carried out. The VB maximum edges
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of CN and KPD-CN-7.5 are determined to be about 1.75 and 1.86 eV, respectively
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(Figure 1c), and the Mott-Schottky plots showing n-type characteristics (positive
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slope) of CN and KPD-CN-7.5 are almost the same (Figure 1d). Contrary to the
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previous studies on bandgap-engineered CN which clearly showed the bandgap size
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decrease/increase and the shift of the CB/VB potential as well,16 the hetero-elements
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did not markedly change their electronic band structure.
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As presented in Figure 2a and Table S1, the typical C-N peaks of CN between
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1200 and 1600 cm-1 were little changed in KPD-CN-7.5. The incorporation of
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potassium ions into CN framework shifted the stretching modes of tri-s-triazine ring
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at 1393 and 1538 cm-1 to 1404 and 1571 cm-1, respectively, due to a strong ion-
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dipole interaction at the nitride pots.4,17 Similar with chelation, metal ions including
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cobalt, manganese, potassium, iron, etc. can be coordinated with nonbonding
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electrons of nitrogen in the nitride pots (pore induced by trigonal bonding of tri-s-
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triazines).4, 17 The P-relevant peak of phosphate at 847 and 984 cm-1 and the P-O-C
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stretching at 903 and 1146 cm-1 were newly formed and these peaks became
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predominant with increasing KPD content (Figure S2b).18-20 On the other hand, the
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out-of-plane bending mode (also assigned as the deformation mode of N-H) at 888
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cm-1 completely disappeared.21,22 The result indicates that potassium ions and
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phosphate species are well-assembled inside polymeric CN matrix.
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The surface property of CN and KPD-CN-7.5 was also evaluated by zeta-potential
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analysis since the primary (C-NH2), secondary (C-NH-C), and tertiary (C3N) amines
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present in CN can be protonated and deprotonated depending on pH.23 The CN
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exhibits the point of zero charge (PZC) at around pH 3 (Figure 2b). However, KPD-
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CN-7.5 predominantly carries negative charge over the entire pH range from 1 to 11
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without showing PZC in terms of phosphate species.
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To analyze the chemical states for each carbon, nitrogen, potassium, phosphorus,
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and oxygen element consisting of CN and KPD-CN-7.5, a high-resolution XPS
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analysis was carried out. As shown in Figure 2c and Figure S3b, the K2p peaks were
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clearly observed at 292.6 and 295.4 eV in KPD-CN-7.5 since potassium ions were
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coordinated with nonbonding electrons of nitrogen via ion-dipole interaction, which
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is analogous to the molecular structure of metalloporphyrin and KMnO4•18-crown-
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6-ether.24,25 In Figure S3a and S3b, the C1s peaks were deconvoluted into six
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components in both CN and KPD-CN-7.5. Each deconvoluted peak (C1-6, N1-5,
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and O1-3) is denoted in Table S2. The relative intensity of the C2, C5, and C6 peaks
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increased along with the decrease of C4 intensity, which revealed that more carbon
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sites were interacted or replaced by the oxygen atoms present in phosphate species.
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Furthermore, the binding energy of C4 was positively shifted (0.2 eV) due to higher
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electronegativity of oxygen than nitrogen, and the formation of cyano group
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increased the C3 peak intensity. In the case of N1s spectra (Figure S3c and S3d), the
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ratio of N2 to (N3 + N4) was calculated as 2.12 in CN and 2.43 in KPD-CN-7.5,
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respectively. The N2 mainly participates in the build-up of bandgap structure but the
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N3 and N4 are in charge of bulk and surface properties so it can be concluded that
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the surface properties induced by protonated N3 and N4 are less accessible.26 The
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elemental XPS C/N ratio (Table S3) and elemental C/N ratio obtained by elemental
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analysis (Table S4) of CN steadily decreased with increasing the atomic percent of
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phosphorus and oxygen. Although the C/N ratio of bulk CN is not consistent
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between the elemental XPS and elemental C/N analysis (the real C/N ratio can be
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changed by the experiment conditions27,28), the decrease trend is the same in both
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cases. The P2p band was absent in CN and the single symmetric peak at 132.9 eV
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was observed in KPD-CN-7.5 (Figure S3e and S3f), which indicates that P in KPD-
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CN-7.5 is mainly combined with O instead of C and N (since P2p binding energy of
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P-C, P-O, and P-N is about 131.0, 132.9, and 133.5 eV, respectively29-31). As a result,
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the phosphate incorporation in the CN matrix induced the appearance of the O1s
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peak centered at 531.0 eV that is absent in CN (Figure S3g and S3h).
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Solid-state
31
P magic angle spinning (MAS) nuclear magnetic resonance (NMR)
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spectra of CN and KPD-CN-7.5 are compared in Figure 2d. While no peak is
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observed at all in CN, a broad peak from 17 to -50 ppm (δmax = -11.6 ppm) and
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spinning side bands are clearly shown in KPD-CN-7.5. In general, the chemical
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shifts on phosphate monoester, orthophosphate, phosphate diester, pyrophosphate,
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and polyphosphate are normally observed around at 0 ≤ δ ≤ 10, 0 ≤ δ ≤ 5, 0 ≤ δ ≤ -5,
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-5 ≤ δ ≤ -10, and -10 ≤ δ ≤ -30 ppm, respectively.32,33 Furthermore, there is no
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prominent chemical shift induced by the phosphonate group (C-P) usually observed
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over 20 ppm. The result supports that the phosphate species do not exist as a sole
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compound, but various species are incorporated into the complex CN matrix. Solid-
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state proton-decoupled
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magnetic resonance (CP-MAS NMR) spectrum of CN exhibited two evident signals
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(Figure S4). The strong peak recorded at 164.7 ppm belongs to the terminal carbon
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(N2-C-NH2 groups), and the second peak at 157.0 ppm is ascribed to the internal
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carbon (C-(N)3 groups).34 The
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revealed two signals centered at 163.9 and 156.6 ppm. The quantitative intensity
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analysis of CP-MAS NMR signals is not reliable but the number of signals and their
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relative ratio provide the useful information. The ratio of the terminal carbon to the
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internal one of CN and KPD-CN-7.5 was measured as 1.55 and 2.88, respectively.
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Considering the decrease of C/N ratio in KPD-CN-7.5, the replacement of carbon
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atoms could occur on the internal carbon sites and the formation of C-O-P bond
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might take place on the terminal sites.
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C cross polarization and magic angle spinning nuclear
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C CP-MAS NMR spectrum of KPD-CN-7.5 also
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The morphologies and the chemical composition of CN and KPD-CN-7.5 were
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confirmed by high resolution transmission electron microscope (HR-TEM) and
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energy-dispersive X-ray spectroscopy (EDS) analysis, respectively. The EDS
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mapping confirmed the presence of predominant carbon and nitrogen, and the small
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amount of oxygen as well, but any potassium and phosphorus was not measured at
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all in CN (Figure 3b-3f). However, in the case of KPD-CN-7.5, carbon, nitrogen,
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potassium, phosphorus, and oxygen were homogeneously dispersed over the
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materials (Figure 3h-3l). To further characterize the properties of CN and KPD-CN-
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7.5, the BET surface area and pore volume measurement (Figure S5a),
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thermogravimetric analysis (Figure S5b), and field-emission scanning electron
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microscopy (Figure S6) were carried out (see Supporting Information regarding the
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detailed result discussion).
205 206
2.2. Photocatalytic Production of H2O2
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First of all, it should be mentioned that the present study is not an ideal
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photosynthesis of H2O2 that utilizes water and O2 only since an excess of ethanol
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was used as an electron donor instead of water. Considering the standard reduction
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potentials of O2 reduction (E0(O2/H2O2) = 0.695 VNHE) and ethanol oxidation
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(E0(CO2/C2H5OH) = 0.085 VNHE), the overall process of H2O2 production in the
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present study is thermochemically spontaneous (that is, photocatalytic, not
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photosynthetic). The main focus of this work is to investigate the effects of hetero-
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elements on the half reaction of H2O2 production via O2 reduction, not to establish
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the ideal photosynthesis. On the other hand, the ethanol oxidation coupled with the
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production of H2O2 was not analysed in this work because the photoreaction was
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carried out under continuous O2 purging condition, which should volatilize the
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products of ethanol oxidation immediately from the solvent. However, in a previous
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study which utilized pure CN for the photochemical production of H2O2 in
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ethanol/water solvent in a closed reactor,9 most of ethanol was oxidized to
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acetaldehyde with almost stoichiometric production of H2O2 with a molar ratio of
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1:1 (i.e., O2 + CH3CH2OH → H2O2 + CH3CHO). The ethanol oxidation part should
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be similar in this study as well.
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The photoactivity was tested by monitoring the visible light-induced production
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of H2O2. The photo-production of H2O2 was compared among the CN and KPD-CN-
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x (x=1, 3, 5, 7.5, and 10) samples in the presence of ethanol as an electron donor in
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the O2-saturated catalyst suspension under visible light irradiation (λ ≥ 420 nm)
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(Figure S7a). All KPD-CN-x samples exhibited markedly enhanced activities
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compared with CN although the specific surface areas of all KPD-CN-x samples are
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significantly lower than bare CN (see Figure S5a). This indicates that the surface
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area of the catalyst samples is not an important factor and that the enhancement of
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the photocatalytic activity should be ascribed to other modified properties (e.g.,
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charge recombination, separation and interfacial transfer, nature of catalytic active
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sites) induced by the incorporation of potassium and phosphate species. The
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photoactivity for H2O2 production increased with increasing KPD content and
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reached a maximum at x=7.5. Therefore, the KPD-CN-7.5 was chosen as an optimal
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sample for further experiments. To investigate the wavelength dependence of the
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H2O2 production, the AQY was measured using a monochromatic light (λ = 320, 370,
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420, 470, and 520 nm) irradiation. As shown in Figure 4a, AQY for the production
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of H2O2 at 320 nm and 420 nm in KPD-CN-7.5 was 17 and 25 times higher than that
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of CN, respectively. In addition, the turnover frequency (TOF) of the KPD-CN-7.5
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at 320 nm and 420 nm was 49.8 and 73.1 times higher than that of CN, respectively.
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Considering that the production of H2O2 requires a PCET process, KPD-CN-7.5 is
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advantageous since it has phosphate functionalized polymeric structure, which can
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facilitate a proton transfer process.16,35-37 Since the production of H2O2 via PCET
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should be highly dependent on the proton concentration, it decreased with increasing
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pH (Figure S7b). The production of H2O2 at pH 1.0 was more than doubled from that
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at pH 3.0 for CN while the enhancement factor ([H2O2]pH=1/[H2O2]pH=3) was only 1.1
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for KPD-CN-7.5. The proton transfer in KPD-CN-7.5 was facilitated enough by the
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presence of the phosphate species, and therefore, a higher concentration of proton (at
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lower pH) has a relatively lower enhancement effect on the production of H2O2 than
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in the case of CN. Moreover, KPD-CN-7.5 exhibited much higher photoactivities
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than CN up to pH 9.0. To check the product selectivity for H2O2 compared to H2, the
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H2 evolution test was also carried out in the presence of ethanol in a tightly-sealed
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reactor under Ar(g) atmosphere under UV light irradiation for 12 h. Both CN and
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KPD-CN-7.5 evolved a very tiny amount of H2 (below 0.1 µmol), which supports
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that two-electron transfer to O2 coupled with protons (Table S5, eq. 5: O2 + 2H+ +
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2e- → H2O2) is much more favored than the direct two-electron transfer to protons
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(Table S5, eq. 18: 2H+ + 2e- → H2).
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The photoactivity tests with CN and KPD-CN-7.5 were performed in air-, Ar-,
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and O2-saturated suspensions to verify the role of dioxygen for the photoproduction
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of H2O2 (Figure 4b). In general, the photo-excited CB electrons can be scavenged by
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dissolved O2 in air- or O2-saturated condition but the protons should uptake the
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electrons in the absence of O2 (Ar-atmosphere). The rate of H2O2 formation on KPD-
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CN-7.5 was markedly enhanced in the O2-saturated suspension from that in the air-
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saturated one. While the [H2O2]O2/[H2O2]air at 3 h was measured to be 1.7 for KPD-
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CN-7.5, it was 1.2 for CN. Under Ar-saturated condition, no H2O2 was formed not
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only with CN but also with KPD-CN-7.5, which confirms that H2O2 is generated
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through the reduction of O2. The KPD-CN-7.5 was stable enough to maintain the
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photocatalytic activity during the repeated cycles of H2O2 production as shown in
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Figure 4c. On the other hand, it should be noted that the overall production of H2O2
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is determined by the photocatalytic decomposition of H2O2 as well as its production
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since the photogenerated H2O2 can be subsequently decomposed on the
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photocatalyst surface. Therefore, the overall photoconversion efficiency can be
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enhanced not only by facilitating the photoreduction of O2 but also by inhibiting the
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decomposition of H2O2 on the photocatalyst surface. For example, our recent study
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demonstrated that the modification of TiO2 surface by phosphate loading inhibited
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the adsorption of H2O2 with significantly retarding the photodecomposition of H2O2,
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which resulted in a highly enhanced production of H2O2.6 In this respect, KPD-CN-
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7.5 is much better than TiO2 for H2O2 production because the adsorption of H2O2 on
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the former is negligible but the latter shows some adsorption affinity for H2O2
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[Adsorption of 100 µM H2O2 in the dark under continuous stirring for 0.5 h:
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[H2O2]ad = 0 µM for KPD-CN-7.5 (surface area: 3.4 m2/g) vs. [H2O2]ad = 12.1 µM
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for TiO2 (surface area: 47 m2/g); Although the surface area of the tested TiO2 is
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higher than KPD-CN-7.5, the higher adsorption of H2O2 on TiO2 should be ascribed
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286
mainly to the strong surface complexation of H2O2 on TiO2 (>Ti(IV)-OH)surf + H2O2
287
→ (>Ti(IV)–OOH)surf + H2O)] As a result, CN and KPD-CN-7.5 did not degrade
288
H2O2 at all under visible light (λ ≥ 420 nm) (Figure S7c). Under UV irradiation (λ ≥
289
320 nm), on the other hand, CN exhibited some activity for H2O2 decomposition but
290
KPD-CN-7.5 did not degrade H2O2 at all. The inactivity of KPD-CN-7.5 for the
291
decomposition of H2O2 should also contribute to the higher activity of KPD-CN-7.5
292
than CN. In addition, the production of H2O2 was highly affected by not only the
293
type of the electron donor (2-propanol > ethanol > methanol >> water) (Figure S8a
294
and S8b) but also the ratio of alcohol to water (Figure S8c). With CN, the
295
photocatalytic production of H2O2 was dramatically inhibited by increasing the water
296
content (from 10% to 90%) whereas that of KPD-CN-7.5 was less affected by
297
increasing the water content. That is, KPD-CN-7.5 should be much more favoured
298
than CN for the production of H2O2 in water-rich environment.
299 300
2.3. Charge Transfer Dynamics
301
The charge separation behaviour of carbon nitrides was investigated by steady-state
302
photoluminescence (PL), time-resolved PL (TRPL), slurry-type photocurrent
303
measurement, and time-resolved diffuse reflectance spectroscopy using femtosecond
304
laser. As shown in Figure 5a, the radiative recombination of excited charge pairs was
305
clearly observed in CN while the PL intensity was markedly reduced with increasing
306
KPD content, which indicates that the radiative recombination is much retarded in
307
KPD-CN-7.5 compared with CN. The wavelength dependent PL emission intensity
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for CN, KPD-CN-3, KPD-CN-7.5 reveals that the PL intensity linearly enhanced
309
with increasing the excitation wavelength for all samples since the excitation light
310
intensity has a linear correlation with the excitation wavelength as well (Figure S9).
311
However, the slope linearly decreased with increasing KPD content, which implies
312
that the hetero-elements effectively prohibit the radiative recombination through the
313
formation of charge trapping sites. The PL excitation spectrum detected at 470 nm
314
for CN shows three distinct PL bands at 271, 367, and 429 nm together with a broad
315
background signal (Figure 5b). Although the PL band at 271 nm was not observed
316
and the background signal was weak in KPD-CN-7.5, the other two PL bands were
317
still visible. The result supports that the hetero-elements generate the trapping sites
318
for charge carriers rather than the change of band structure. The mobile electrons and
319
holes produced by the excitons can freely diffuse or can be shallowly trapped over
320
the polymeric CN lattice in CN, whereas the charge carriers can be deeply trapped
321
and then the non-radiative recombination markedly takes place in KPD-CN-7.5.
322
Furthermore, it is quite probable that the recombination can be facilitated by the
323
decrease of CN wt% with increasing KPD content (Table S4) since the radiative
324
recombination occurs in polymeric CN matrix. Therefore, the average lifetime of
325
charge carriers in CN, KPD-CN-3, and KPD-CN-7.5 was estimated by fitting the
326
decay curve with three exponential terms to yield 2.51, 1.68, 0.83 ns, respectively
327
(Figure 5c). The interfacial electron transfer was also investigated by measuring the
328
PW12O303-/4- redox couple (Eo = +0.22 VNHE)-mediated photocurrent collected in the
329
visible light-irradiated suspension of catalysts.38 Figure 5d shows that the time
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330
profiles of photocurrent generation were enhanced with KPD-CN-7.5 in comparison
331
with CN, which is consistent with the higher visible light activity of KPD-CN-7.5.
332
To directly observe the presence of charge trapping sites on CN, KPD-CN-3, and
333
KPD-CN-7.5, time-resolved diffuse reflectance spectra were measured. To avoid the
334
precipitation problem occurring in aqueous suspension, all samples were
335
homogeneously coated on glass slide and reflectance change induced by laser
336
excitation was measured. Until now, few transient absorption spectroscopic studies
337
were done for CN (protonated CN,28 colloidal CN,27 mesoporous CN,39 and
338
polymeric CN40), so more depth investigation is highly required. In this study, we
339
focused on the lifetime of transient species formed by trapped charge carriers to
340
confirm the role of hetero-elements incorporated in CN framework. As shown in
341
Figure 6, the broad positive absorption band was similarly observed for all samples
342
after laser pulse at 400 nm under air. Recently, Zhang et al. reported that the positive
343
absorption was attributed to the formation of charge separation states by
344
photogenerated electron/hole pairs in colloidal CN system.27 Kuriki et al. also
345
defined that the broad positive absorption was originated from deeply trapped
346
electron/hole pairs.39 The transient absorption decay for charge separation states was
347
well fitted by the biexponential equation for all samples, and the average lifetime of
348
CN, KPD-CN-3, and KPD-CN-7.5 was calculated as 353.1, 477.7, and 1194.0 ps,
349
respectively. Although the transient absorption intensity was a little reduced in KPD-
350
CN-7.5 relative to CN due to less wt% of CN content, the charge separation process
351
is improved by the hetero-elements. The results support that the incorporation of
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hetero-elements into polymeric CN matrix could generate not only the extra charge
353
trapping sites but also the catalytic sites favourable to the PCET process, which
354
should influence the recombination kinetics and the interfacial charge transfer
355
characteristics to facilitate the photoproduction of H2O2.
356 357
2.4. Other Hetero-Elements Incorporated CN Materials
358
Other chemicals instead of KPD were employed as alternative reagents to investigate
359
the cationic and anionic effects on the photocatalytic production of H2O2
360
systematically and their XPS elemental analysis was also carried out (Figure 7 and
361
Table S6). When the ratio of proton to potassium was changed using H3PO4,
362
KH2PO4, K2HPO4, and K3PO4, the relative percentage of potassium, phosphorus,
363
and oxygen consisting of the samples increased in the order K3PO4 > K2HPO4 >
364
KH2PO4 > H3PO4. However, the highest photocatalytic activity was obtained with
365
K2HPO4 instead of K3PO4 because the polymeric CN matrix was decomposed in the
366
presence of K3PO4 (the C/N ratio = 0.32) (Figure 7a). No potassium was found in the
367
sample when H3PO4 was used. On the other hand, when H2SO4, KHSO4, and K2SO4
368
were employed as alternative reagents, the potassium content in the CN matrix was
369
in the order of K2SO4 > KHSO4 > H2SO4 but no sulfur element was found in the
370
samples. The highest photocatalytic activity was obtained with KHSO4, but the
371
amount of H2O2 produced was lower than that of KPD-CN-7.5 (Figure 7b). The
372
result demonstrated that KPD is a good source to incorporate both phosphate species
373
and potassium ions into the CN matrix. As for the cation effect, different dihydrogen
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374
phosphate reagents containing various cations were also tested and compared for the
375
photocatalytic activities for H2O2 production, which exhibited the reactivity order of
376
KH2PO4 > NaH2PO4 > LiH2PO4 > H3PO4 > (NH4)H2PO4 (Figure 7c). When different
377
anions (HCO3-, HSO4-, and H2PO42-) combined with potassium ion were tested, the
378
best photocatalytic activity was obtained with H2PO42- (Figure 7d). Among various
379
combinations of cationic and anionic species for the incorporation into the CN
380
matrix, the combination of potassium and dihydrogen phosphate in KPD-CN-7.5
381
showed the best photocatalytic performance.
382
383
3. Conclusions
384
Despite the simple synthetic procedure for CN, its polymeric structure is still
385
controversial (even s-heptazine has been recently considered as a basic building
386
block) and the synthetic mechanism is not fully understood.41 Therefore, it does not
387
make much sense to conclude the exact structure and synthetic mechanism in the
388
present case of modified CN. However, the analyses using various spectroscopic
389
methods revealed that the earth-abundant hetero-elements (K, P, and O) could be
390
incorporated into the carbon nitride framework via thermal polymerization to modify
391
the surface and charge transfer properties significantly and consequently to enhance
392
the photoactivities for the production of H2O2. According to DRS, XPS, and Mott-
393
Schottky plots, the incorporation of the multiple hetero-elements does not affect the
394
bandgap size and the band potential shift. The presence and chemical states of the
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hetero-elements were confirmed by FT-IR, Zeta-potential analysis, XPS, solid state
396
NMR, and EDX mapping, which comes to conclusions that 1) potassium is captured
397
as an ion by non-pair electrons of nitrogen present in CN matrix, 2) phosphorus and
398
oxygen elements exist as various phosphate species, and 3) carbon sites are attacked
399
by the oxygen present in the phosphate species relative to nitrogen sites. The high
400
photoactivity of KPD-CN-7.5 and particularly high selectivity toward H2O2 over H2
401
are attributed to 1) the enhanced light absorption (UV light region), 2) the increased
402
lifetime of the transient species, 3) the effective interfacial charge transfer to
403
dioxygen via PCET, and 4) the inhibited decomposition of in-situ generated H2O2. It
404
should be noted that such unique activity and selectivity for H2O2 production cannot
405
be an additive property of K-doped CN and P-doped CN at all (see Figure 7). The
406
KPD-modified CN is uniquely suited for the photochemical production of H2O2. The
407
incorporation of various earth-abundant elements into CN could be also possible for
408
a variety of applications. This study clearly demonstrated that the hetero-elements
409
incorporated CN can be exploited for cost-effective and environment-friendly
410
photocatalysts without utilizing any noble metals, which should be important for the
411
development of practical and economical solar conversion photocatalytic materials.
412
413
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414
4. Experimental Section
415
Materials preparation: To synthesize CN, 4 g of melamine (99%, Aldrich) in a
416
porcelain cup covered with a cap was calcined at 550 oC for 4 h (heating and cooling rate
417
was 2.2 oC/min, respectively.). After grinding the CN sample homogeneously, the aqueous
418
solution containing CN (1 g/L) was sonicated in an ultrasonic bath (JAC 4020, 400 W,
419
Sonic) for 3 h, filtered, washed, and finally dried at room temperature. Modified CN
420
compounds were prepared through a similar synthetic procedure of CN. 4 g of melamine
421
and each 1, 3, 5, 7.5, and 10 mmol of KPD (K2HPO4 99.95%, Aldrich) were
422
homogeneously ground, respectively. On the basis of 7.5 mmol, 4 g of melamine was
423
mixed and ground with phosphoric acid (85 wt.% in water, Aldrich), potassium phosphate
424
monobasic (99.99%, Aldrich), potassium phosphate tribasic (98%, Aldrich), sulfuric acid
425
(95.0-98.0%, Aldrich), potassium bisulfate (99%, Aldrich), potassium sulfate (99.99%,
426
Aldrich), ammonium phosphate monobasic (99.999%, Aldrich), lithium phosphate
427
monobasic (99.99%, Aldrich), sodium phosphate monobasic (99.0%, Aldrich), and
428
potassium bicarbonate (99.95%, Aldrich), respectively. Phosphoric acid or sulfuric acid
429
mixed melamine powder was dried at 80 oC for 3 h to remove water and then was ground
430
again. The other procedure is the same with CN synthetic procedure.
431
Photocatalytic activity tests: 20 mg of each sample was dispersed in the solution
432
containing 36 mL of purified water and 4 mL of ethanol by ultra-sonication. The pH of the
433
suspension was controlled by HClO4 or KOH. Before the irradiation, the suspension was
434
stirred under O2 purging for 30 min to make it O2-saturated. The reactor was irradiated by a
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300-W Xe arc lamp (Oriel) under continuous stirring and purging. Light was passed
436
through a 10-cm IR filter and a cutoff filter (λ ≥ 420 nm or λ ≥ 320 nm), and then was
437
focused onto the reactor. The intensity of the incident light filtered through cutoff filters (λ
438
≥ 420 nm and λ ≥ 320 nm) was determined to be about 726.8 mW/cm2 and 833 mW/cm2,
439
respectively, which was measured by a power meter (Newport 1830-C).
440
To calculate the apparent quantum yield (AQY), the incident light was passed through a
441
SAP301 grating monochromator (Newport, Oriel 77250). The light intensity was measured
442
using an optical power meter (1815-C, Newport) with a photodiode detector (818-UV,
443
Newport). The light intensity at 320, 370, 420, 470, and 520 nm was measured as 0.16,
444
0.40, 0.74, 1.06, and 0.75 mW, respectively. AQY was estimated from the formula of
445
ΦAQY(%) = (Number of H2O2 formed x 2)/ (Number of incident photons) x 100. The
446
turnover number was calculated after 6 h irradiation. The number of C6N8 units on the
447
surface was assumed as 7.55 x 10-5 mol/g in both CN and KPD-CN-7.5. The C6N8 unit per
448
area was 0.22 nm-2, and the surface area of CN and KPD-CN-7.5 was 10 and 3.4 m2/g,
449
respectively.
450
The recycle test was performed as follows. 20 mg of the sample was dispersed in the
451
solution containing 36 mL of purified water and 4 mL of ethanol (pHi = 3), which was
452
irradiated at λ ≥ 420 nm under continuous O2 purging condition. After 1st cycle, the
453
suspension was filtered, washed, and then re-dispersed in the solution (0.5 g/L of the
454
photocatalyst and 10 vol.% of ethanol) by ultra-sonication. The same procedure was
455
repeated up to 4th cycle. The photocatalytic decomposition of H2O2 with using bare CN and
456
KPD-CN-7.5 was carried out as follows: 0.5 g/L of the photocatalyst was dispersed in the
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457
solution containing 5 mM of H2O2 at pH 3.0. Before the irradiation, the suspension was
458
kept in dark for 30 min and then visible (λ ≥ 420 nm) or UV light (λ ≥ 320 nm) was
459
sequentially irradiated under continuous O2 purging condition. Methanol and 2-propanol
460
were also tested as an alternative electron donor. The photocatalytic H2 evolution was
461
tested as well to estimate the selectivity toward H2O2 by a gas chromatograph (GC,
462
HP6890N) with a thermal conductivity detector.
463
464
Supporting Information
465
Experimental details, characterizations of KPD-CN-x (x = 0, 1, 3, 5, 7.5, and 10) (XRD,
466
DRUVS, FT-IR, high resolution XPS,
467
volume, TGA, FE-SEM, steady-state photoluminescence, and elemental analysis), the
468
photocatalytic generation of H2O2 depending on KPD content, pH, and electron donors, and
469
the photocatalytic decomposition of H2O2 under UV and visible irradiation. This material is
470
available free of charge via the Internet at http://pubs.acs.org.
13
C CP-MAS NMR, BET surface area & pore
471
472
Acknowledgements
473
This work was financially supported by the Global Research Laboratory (GRL)
474
Program (No. NRF-2014K1A1A2041044) and KCAP (Sogang Univ.) (No. 2009-
475
0093880), which were funded by the Korea Government (MSIP) through the
476
National Research Foundation (NRF).
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References
479 480 481 482 483 484 485 486 487 488 489 490 491 492 493 494 495 496 497 498 499 500 501 502 503 504 505 506 507 508 509 510 511 512 513 514 515 516 517 518 519 520 521 522 523
(1) Colmenares, J. C.; Luque R. Chem. Soc. Rev. 2014, 43, 765-778. (2) Park, H.; Kim, H. I.; Moon, G. H.; Choi, W. Energy Environ. Sci. 2016, 9, 411-433. (3) Wang, Y.; Wang, X. C.; Antonietti, M. Angew. Chem.-Int. Edit. 2012, 51, 68-89. (4) Cao, S.; Low, J.; Yu, J.; Jaroniec, M. Adv. Mater. 2015, 27, 2150-2176. (5) Campos-Martin, J. M.; Blanco-Brieva, G.; Fierro, J. L. G. Angew. Chem.-Int. Edit. 2006, 45, 6962-6984. (6) Moon, G. H.; Kim, W.; Bokare, A. D.; Sung, N. E.; Choi, W. Energy Environ. Sci. 2014, 7, 4023-4028. (7) Hoffmann, M. R.; Martin, S. T.; Choi, W.; Bahnemann, D. W. Chem. Rev. 1995, 95, 69-96. (8) Maurino, V.; Minero, C.; Mariella, G.; Pelizzetti, E. Chem. Commun., 2005, 2627-2629. (9) Shiraishi, Y.; Kanazawa, S.; Sugano, Y.; Tsukamoto, D.; Sakamoto, H.; Ichikawa, S.; Hirai, T. ACS Catal. 2014, 4, 774-780. (10) Shiraishi, Y.; Kanazawa, S.; Kofuji, Y.; Sakamoto, H.; Ichikawa, S.; Tanaka, S.; Hirai, T. Angew. Chem.Int. Edit. 2014, 53, 13454-13459. (11) Shiraishi, Y.; Kofuji, Y.; Sakamoto, H.; Tanaka, S.; Ichikawa, S.; Hirai, T. ACS Catal. 2015, 5, 30583066. (12) Wang, X. C.; Maeda, K.; Thomas, A.; Takanabe, K.; Xin, G.; Carlsson, J. M.; Domen, K.; Antonietti, M. Nat. Mater. 2009, 8, 76-80. (13) Cichy, B.; Luczkowska, D.; Nowak, M.; Wladyka-Przybylak, M. Ind. Eng. Chem. Res. 2003, 42, 28972905. (14) Cichy, B.; Kuzdzal, E. Ind. Eng. Chem. Res. 2012, 51, 16531-16536. (15) Thomas, A.; Fischer, A.; Goettmann, F.; Antonietti, M.; Müller, J.-O.; Schlögl, R.; Carlsson, J. M. J. Mater. Chem. 2008, 18, 4893-4908. (16) Chu, S.; Wang, Y.; Guo, Y.; Feng, J.; Wang, C.; Luo, W.; Fan, X.; Zou, Z. ACS Catal. 2013, 3, 912-919. (17) Gao, H.; Yan, S.; Wang, J.; Huang, Y. A.; Wang, P.; Li, Z.; Zou, Z. Phys. Chem. Chem. Phys. 2013, 15, 18077-18084. (18) Khabashesku, V. N.; Zimmerman, J. L.; Margrave, J. L. Chem. Mater. 2000, 12, 3264-3270. (19) Miller, F. A.; Wilkins, C. H. Anal. Chem. 1952, 24, 1253-1294. (20) Yang, Z.; Wang, Z.; Li, J.; Chen, J. RSC Adv. 2012, 2, 11432-11437. (21) Huang, Y.; Wang, Y.; Bi, Y.; Jin, J.; Ehsan, M. F.; Fu, M.; He, T. RSC Adv. 2015, 5, 33254-33261. (22) Dong, F.; Wang, Z.; Sun, Y.; Ho, W. K.; Zhang, H. J. Colloid Interface Sci. 2013, 401, 70-79. (23) Zhu, B. C.; Xia, P. F.; Ho, W. K.; Yu, J. G. Appl. Surf. Sci. 2015, 344, 188-195. (24) Hu, S.; Li, F.; Fan, Z.; Wang, F.; Zhao, Y.; Lv, Z. Dalton Trans. 2015, 44, 1084-1092. (25) Moulder, J. F.; Stickle, W. F.; Sobol, P. E.; Bomben, K. Handbook of X-ray Photoelectron Spectroscopy, 2nd ed.; Perkin-Elmer, Physical Electronics Division: Eden Prairie, MN, 1992. (26) Martin, D. J.; Qiu, K.; Shevlin, S. A.; Handoko, A. D.; Chen, X.; Guo, Z.; Tang, J. Angew. Chem.-Int. Edit. 2014, 53, 9240-9245. (27) Zhang, H. Y.; Chen, Y. P.; Lu, R.; Li, R. Y.; Yu, A. C. Phys. Chem. Chem. Phys. 2016, 18, 14904-14910. (28) Ye, C.; Li, J.-X.; Li, Z.-J.; Li, X.-B.; Fan, X.-B.; Zhang, L.-P.; Chen, B.; Tung, C.-H.; Wu, L.-Z. ACS Catal. 2015, 5, 6973-6979. (29) Puziy, A. M.; Poddubnaya, O. I.; Socha, R. P.; Gurgul, J.; Wisniewski, M. Carbon 2008, 46, 2113-2123. (30) Gorham, J.; Torres, J.; Wolfe, G.; d'Agostino, A.; Fairbrother, D. H. J. Phys. Chem. B 2005, 109, 2037920386. (31) Zhang, Y. J.; Mori, T.; Ye, J. H.; Antonietti, M. J. Am. Chem. Soc. 2010, 132, 6294-6295. (32) Sannigrahi, P.; Ingall, E. D.; Benner, R. Geochim. Cosmochim. Acta 2006, 70, 5868-5882. (33) He, Z.; Honeycutt, C. W.; Xing, B.; McDowell, R. W.; Pellechia, P. J.; Zhang, T. Soil Sci. 2007, 172, 501-515.
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524 525 526 527 528 529 530 531 532 533 534 535 536 537
(34) Jürgens, B.; Irran, E.; Senker, J.; Kroll, P.; Müller, H.; Schnick, W. J. Am. Chem. Soc. 2003, 125, 1028810300. (35) Kreuer, K. D.; Paddison, S. J.; Spohr, E.; Schuster, M. Chem. Rev. 2004, 104, 4637-4678. (36) Vilciauskas, L.; Tuckerman, M. E.; Bester, G.; Paddison, S. J.; Kreuer, K. D. Nat. Chem. 2012, 4, 461466. (37) Park, H.; Choi, W. J. Phys. Cehm. B 2003, 107, 3885-3890. (38) Liu, G.; Wang, T.; Zhang, H.; Meng, X.; Hao, D.; Chang, K.; Li, P.; Kako, T.; Ye, J. Angew. Chem.-Int. Edit. 2015, 54, 13561-13565. (39) Kuriki, R.; Matsunaga, H.; Nakashima, T.; Wada, K.; Yamakata, A.; Ishitani, O.; Maeda, K. J. Am. Chem. Soc. 2016, 138, 5159-5170. (40) Merschjann, C.; Tschierlei, S.; Tyborski, T.; Kailasam, K.; Orthmann, S.; Hollmann, D.; Schedel-Niedrig, T.; Thomas, A.; Lochbrunner, S. Adv. Mater. 2015, 27, 7993-7999. (41) Schwarzer, A.; Saplinova, T.; Kroke, E. Coord. Chem. Rev. 2013, 257, 2032-2062.
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558 559
560
563
* CN
KPD-CN-7.5 564 20
40
565
568
2.0 1.5
1 0
CN
2.0
2.5
3.0
3.5
4.0
hν ν (eV)
0.5
KPD-CN-7.5 300
400
500
600
700
Wavelength (nm)
2θ θ
(c)
2
1.0
0.0 200
80
CN KPD-CN-7.5
3
(d)
CN
4
3 10 -2
CN KPD-CN-7.5
KPD-CN-7.5
2
-2
567
2.5
C /10 F
566
60
4
(hν ν F(R))1/2
Intensity (a.u.)
561 562
(b) 3.0
*
Absorbance (K.M)
(a)
Intensity (a.u.)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Catalysis
1
569 570
-2
0
2
4
6
8
10
12
0 -0.5
14
0.0
0.5
1.0
Potential (V) vs. Ag/AgCl
Binding Energy (eV) 571 572
Figure 1. (a) XRD spectra, (b) DRUVS spectra, (c) XPS valence band analysis, (d) Mott-
573
Schottky plots for bare CN and KPD-CN-7.5. Inset in (b): Tauc plot for bare CN and KPD-
574
CN-7.5.
575 576 577 578
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(b)
(a)
581 582 583
CN
C≡N
KPD-CN-7.5
584
*
*
586
20
CN KPD-CN-7.5
0
-20
-40
-60
1000
585
ζ potential (mV)
580
Transmittance (a.u.)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
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1500
2000
2500
0
2
4
-1
P2p
8
10
12
pH
Wavenumber (cm )
(c)
6
(d)
C1s
O1s
K2p
CN
587 588
KPD-CN-7.5 KPD-CN-7.5
589
CN 130
590
135
* 285
290
295
530
535
100
* 50
0
-50
-100
ppm
Binding Energy (eV) 591 592
Figure 2. (a) ATR FT-IR spectra (Asterisks indicate the bonding, P-O-C, and the arrows
593
represent the peak shift of typical peaks of CN) of bare CN and KPD-CN-7.5. (b) zeta-
594
potential analysis of bare CN and KPD-CN-7.5. (c) XPS P2p, C1s, K2p, and O1s core-level
595
spectra of bare CN and KPD-CN-7.5. (d) 31P MAS NMR spectra of bare CN and KPD-CN-
596
7.5.
597 598 599
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Page 27 of 33
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ACS Catalysis
600
601 602
Figure 3. (a) TEM image of bare CN. (b-f) EDX mapping corresponding to panel (a). (g)
603
TEM image of KPD-CN-7.5. (h-l) EDX mapping corresponding to panel (g). Red, green,
604
blue, purple, and sky-blue color represent C (b and h), N (c and i), K (d and j), P (e and k),
605
and O (f and l) elements, respectively.
606 607 608 609 610 611 612 613 614 615
27
ACS Paragon Plus Environment
ACS Catalysis
616
(a) CN KPD-CN-7.5
617 618 619 620 621
(b) 2.0
CN (O2)
623 624
H2O2 [mM]
622
CN (Air) CN (Ar) KPD-CN-7.5 (O2)
1.5
KPD-CN-7.5 (Air) KPD-CN-7.5 (Ar)
1.0
0.5
625 0.0 0
626
(c) 627
2
628 629 630
4
6
8
Irradiation time (h) 3.5
KPD-CN-7.5 CN
3.0
[H2O2] (mM)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 28 of 33
2.5
1st
2.0
3rd
2nd
4th
1.5 1.0 0.5 0.0
631
0
12
24
36
48
Irradiation time (h) 632 633
Figure 4. (a) Apparent quantum yield (AQY, Left axis) and turnover frequency (Right axis)
634
of bare CN and KPD-CN-7.5 for H2O2 production under monochromatic light irradiation.
635
(b) Comparison of the photoproduction of H2O2 under air-, N2-, and O2-saturated
636
conditions for bare CN and KPD-CN-7.5. (c) Repeated runs of H2O2 generation in the
28
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ACS Catalysis
637
visible light-irradiated suspension of bare CN and KPD-CN-7.5. (b, c) The experimental
638
conditions were: 0.5 g/L of photocatalyst, 10 vol% of ethanol, pHi = 3.0, and λ ≥ 420 nm
639
(polychromatic).
640 641 642 643 644 645 646 647 648 649 650 651 652 653 654 655 656
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ACS Catalysis
657
(a)
CN
660 661
λex = 400 nm
4
KPD-CN-3
4
5
Intensity (10 CPS)
5
659
(b)
6
Intensity (10 CPS)
658
2
KPD-CN-7.5
CN
4 3
KPD-CN-3
2
x2 1 0 250
0 450
500
550
600
650
300
665 666 667 668
(d)
1
400
25
POM*
CN KPD-CN-3 KPD-CN-7.5
Photocurrent (µ µA)
664
(c)
350
Waverlength (nm)
Wavelength (nm) 663
KPD-CN-7.5
λem = 470 nm
662
PL Intensity (Norm.)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 30 of 33
0.1
0.01
20
e
15 10
POM
-
KPD-CN-7.5 CN
5 0
0
10
20
30
40
50
0
500
1000
1500
2000
Time (s)
Time (ns)
669
Figure 5. (a) PL emission spectra (λex = 400 nm) and (b) PL excitation spectra at 470 nm of
670
bare CN, KPD-CN-3, and KPD-CN-7.5. (c) TRPL spectra monitored at 480-490 nm of bare
671
CN, KPD-CN-3, and KPD-CN-7.5 coated on glass slide after the excitation with 400 nm
672
laser pulse. The curves were fitted to triexponential equation: y = y0 + A1exp(-t/τ1) +
673
A2exp(-t/τ2) + A3exp(-t/τ3). (d) Time-profiles of POM-mediated photocurrent collected on a
674
Pt electrode in the irradiated suspension of bare CN and KPD-CN-7.5. The experimental
675
conditions were: 0.5 g/L catalyst, 2 mM PW12O303-, pHi = 3, λ ≥ 420 nm, 0.1 M NaClO4, Pt
676
electrode held at 0.7 V (vs Ag/AgCl), and continuously Ar-purged.
677 678
30
ACS Paragon Plus Environment
(a) %Abs
680 681
ps
0.20
10 52 102 202 522 1022 1522 2022
0.15 0.10
682 0.05
683
CN
0.00
684
700
ps 0.20
(d)
10 52 102 202 522 1022 1522 2022
0.15 0.10 0.05
KPD-CN-3
688 600
689
692
700
τ2 666.82 ps
A2
0.285
: 353.1 ps
0.2
500
1000
1500
2000
2500
3000
Delay Time (ps) 1.0 0.8
τ1
45.17 ps
A1
0.415
τ2
1103.5 ps
A2
0.287
: 477.7 ps
0.6 0.4 0.2
0
500
(e)
ps 0.20
(f)
10 52 102 202 522 1022 1522 2022
0.15 0.10 0.05
1000
1500
2000
2500
3000
Delay Time (ps)
Wavelength (nm)
KPD-CN-7.5
693 0.00
694
0.329
0.4
800
Normalized % Abs750nm
691
A1
0.0
0.00
690
τ1 81.48 ps
0.6
0
Wavelength (nm)
% Abs
687
0.8
800
(c) 685
1.0
0.0 600
686
(b)
Normalized % Abs750nm
679
% Abs
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Catalysis
Normalized % Abs750nm
Page 31 of 33
1.0 0.8
τ1 130.73 ps
A1
0.459
τ2 3057.0 ps
A2
0.262
: 1194.0 ps
0.6 0.4 0.2 0.0
600
700
800
0
500
Wavelength (nm)
1000
1500
2000
2500
3000
Delay Time (ps)
695
Figure 6. Time-resolved diffuse reflectance spectra for (a) bare CN, (c) KPD-CN-3, and (e)
696
KPD-CN-7.5 recorded by 400 nm femtosecond laser pulse excitation under air. Decay
697
curves of transient absorption intensity at 750 nm for (b) bare CN, (d) KPD-CN-3, and (f)
698
KPD-CN-7.5. The dotted line curves are fitted to the biexponential equation: y = y0 +
699
A1exp(-t/τ1) + A2exp(-t/τ2).
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ACS Paragon Plus Environment
ACS Catalysis
700
703 704
None H2SO4
2.5
None H3PO4
2.0
K2HPO4
KHSO4
KH2PO4
H2O2 [mM]
702
(b) 1.5
(a) 3.0 H2O2 [mM]
701
K3PO4
1.5 1.0
1.0
K2SO4
0.5
0.5 0.0
0.0
705
0
4
8
0
12
4
Irradiation Time (h)
708 709 710
None H3PO4
None KHCO3
(NH4)H2PO4
1.5
LiH2PO4 NaH2PO4
1.0
KH2PO4
0.5
KHSO4
1.5
KH2PO4
1.0
0.5
0.0
0.0 0
711
12
(d) 2.0
(c) 2.0
707
8
Irradiation Time (h)
H2O2 [mM]
706
H2O2 [mM]
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 32 of 33
4
8
12
0
Irradiation Time (h)
4
8
12
Irradiation Time (h)
712
Figure 7. (a) Different types of potassium phosphate. (b) Different kinds of potassium
713
sulfate. (c) Cationic effect based on dihydrogen phosphate species. (d) Anionic effect based
714
on potassium. The experimental conditions were as follows: 0.5 g/L of photocatalyst, 10
715
vol.% of ethanol, pHi = 3.0, and continuous O2-purged atmosphere.
716 717 718 719 720 721
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722
ACS Catalysis
Table of content (TOC)
723
33
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