Subscriber access provided by Iowa State University | Library
Article
Selectively Photocatalytic Oxidation of Low Concentration Methane over Graphitic Carbon Nitride Decorated Tungsten Bronze Cesium Yuan Li, Jun Li, Gaoke Zhang, Kai Wang, and Xiaoyong Wu ACS Sustainable Chem. Eng., Just Accepted Manuscript • DOI: 10.1021/ acssuschemeng.8b06270 • Publication Date (Web): 22 Jan 2019 Downloaded from http://pubs.acs.org on January 30, 2019
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 25 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 Sustainable Chemistry & Engineering
1
Selectively Photocatalytic Oxidation of Low
2
Concentration Methane over Graphitic Carbon
3
Nitride Decorated Tungsten Bronze Cesium
4
Yuan Li1†, Jun Li1†, Gaoke Zhang1*, Kai Wang1, Xiaoyong Wu1*
5
1 State Key Laboratory of Silicate Materials for Architectures, School of Resources and
6
Environmental Engineering, Wuhan University of Technology, 122 Luoshi Road, Wuhan 430070,
7
China
8
†
9
Corresponding Author: E-mail:
[email protected];
[email protected] Y. Li and J. Li contributed equally to this paper.
10
KEYWORDS:Photocatalytic Methane Conversion, Graphic Carbon Nitride, Tungsten Bronze
11
Cesium, Selective Conversion, Low concentration methane
12
ACS Paragon Plus Environment
1
ACS Sustainable Chemistry & Engineering 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 2 of 25
13
ABSTRACT
14
Although the traditional thermal catalysis is usually used to convert the methane into value-added
15
products, its high reaction temperature results in low performance-price ratio in conversion of low
16
concentration methane. In this regard, we synthesized a series of mace-like g-C3N4 decorated
17
Cs0.33WO3 nanocomposites for photocatalytic conversion of low concentration methane under
18
mild conditions. The optimized
[email protected] (weight ratio = 3:7) photocatalyst selectively
19
converted low concentration methane (1000 ppm) into methanol with yield of 4.38 μmol/h/g under
20
light irradiation and at room temperature. Both performance experiments and trapping experiments
21
verified that the methane activation and methyl oxidation involved in photocatalytic conversion
22
process of methane. The •O2- firstly activated the methane to methyl on the surface of the g-C3N4
23
in the composite and then the photogenerated electrons from the Cs0.33WO3 in the composite
24
inhibited the peroxidation and increased the generation of methanol. This research provides a new
25
route to design and synthesize photocatalysts for converting methane into value-added chemicals.
26
Introduction
27
The uncontrolled and disordered emission of low concentration methane results in enormous
28
energy waste and exacerbates the greenhouse effect, simultaneously.1-4 So, some strategies are
29
now being actively sought to reduce the emission of methane and convert it into value-added
30
products to improve the utilization efficiency of the low concentration of natural gas.5-10 Among
31
of those strategies, the thermal catalysis has been firstly adopted to convert the trace amount of
32
methane.11 However, the high energy-consumption, low performance-price ratio and explosion
33
risk of the thermal catalysis limited its application. From the viewpoint of the cost and safety, the
ACS Paragon Plus Environment
2
Page 3 of 25 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 Sustainable Chemistry & Engineering
34
environmentally friendly photocatalysis has been considered as one of the ideal solutions to realize
35
the effective conversion of low concentration methane into value-added products.12-17
36
The methane converting via the photocatalysis approach is confronted with many fundamental
37
technical hurdles at present. As we all known, the methane is very hard to be activated by the
38
photocatalysts, because the methane is a kind of non-polar nature molecule with stable C-H bond
39
(434 kJ•mol-1).18,19 So, the initial C-H bond cleavage determines the reaction rate of the
40
photocatalytic conversion of methane. In terms of reaction process, the generation of strong
41
oxidizing free radicals, such as •O2- and •OH, by photocatalysts plays a key role for the C-H bond
42
cleavage, implying that the photocatalysts must have higher conduction band (CB) minimum than
43
the O2/•O2- (- 0.16 V versus NHE) potential or lower valence band (VB) maximum than the
44
•OH/OH- (+ 2.59 V versus NHE) potential.20-22 It is a possibility that the graphitic carbon nitride
45
(g-C3N4) nanosheets can effectively activate methane, attributing to its suitable potential of
46
conduction band.23-25 However, it is still a challenge to design the photocatalyst, which can realize
47
the selectively photocatalytic conversion of methane. Rodriguez et.al thought that some inhibitors
48
could be introduced to control the peroxidation process and realize selective photocatalysis.26 A
49
hypothesis was proposed that the appropriate amount of semi-metallic semiconductors, such as
50
tungsten bronze, which had a special band with rich reducing electrons nearby the Fermi level, 27-
51
30
52
of low concentration methane.
could composite with the g-C3N4 nanosheets to realize the selectively photocatalytic oxidation
53
Herein, we prepared a series of
[email protected] nanocomposites using ultrasonic assisted
54
synthesis strategy to successfully confirm the above hypothesis. The optimized g-
55
[email protected] nanocomposites exhibited superior photocatalytic performance for converting
56
low concentration methane into methanol and very high yield of methanol under mild condition.
ACS Paragon Plus Environment
3
ACS Sustainable Chemistry & Engineering 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 4 of 25
57
The reaction pathway of photocatalytic conversion of methane into methanol by the composite
58
was proposed based on a series of characterization techniques. Owing to the suitable band
59
structures, the g-C3N4 in the composite effectively photo-activated the methane to intermediate in
60
the activation process. Moreover, the Cs0.33WO3 in the composite inhibited the peroxidation of
61
intermediate and provided more free electrons to enhance the generation of methanol. This study
62
provides a new way for the photocatalytic conversion of low concentration methane into methanol.
63
Materials and Methods
64
Synthesis of Cs0.33WO3. The Cs0.33WO3 sample was synthesized by the reported water
65
controlled-release process.30
66
Synthesis of g-C3N4. The bulk g-C3N4 sample was prepared following the previous paper from
67
the thermal polycondensation of melamine.25 Then, 0.5 g of the bulk g-C3N4 sample was
68
ultrasonicated (3000 Hz) in the 100 ml pure water for 2 h to obtain the homogeneous suspension.
69
Then, the suspension was centrifuged at 3000 rpm for 5 min to remove the residual bulk g-C3N4
70
nanoparticles. Lastly, the supernatant of centrifuged suspension was dried in a vacuum oven at 60
71
oC
to obtain the slightly yellow g-C3N4 nanosheets.
72
Preparation of
[email protected] nanocomposites. 0.5 g of the g-C3N4 nanosheets was
73
dispersed by ultrasonication (3000 Hz) in the 100 ml mixed solution (The volume ratio of ethanol
74
and water = 3: 7) for 2 h to obtain the mixture soliquoid. Then, certain amount of Cs0.33WO3 poured
75
into the soliquoid with stirring for 12 h. Lastly, the above soliquoid was dried in a vacuum oven at
76
60 °C. The nanocomposites, in which the weight ratios of g-C3N4 and Cs0.33WO3 were 1:9, 3:7 and
77
7:3, were named as 10CW, 30CW and 70CW, respectively.
78
Characterization
ACS Paragon Plus Environment
4
Page 5 of 25 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 Sustainable Chemistry & Engineering
79
The X-ray diffraction (XRD) pattern, Raman spectra, Fourier transform infrared (FT-IR) spectra
80
and chemical state analyses of samples were characterized by a D/MAX-RB diffractometer with
81
CuKα radiation, a JY LabRam HR800 Raman microscope with the 514 nm excitation laser beam,
82
a Nexus FT-IR spectrometer and an X-ray photoelectron spectroscopy (XPS) utilizing
83
monochromatic Mg Kα source and a charge neutralizer, respectively. Transmission electron
84
microscopy (TEM) images, high resolution transmission electron microscopy (HRTEM) images
85
and selected area electron diffraction (SAED) images were taken on JEOL 2100F (280 kV). A
86
UV3500 plus
87
spectrofluorometer (Shimadzu, Japan) with emission wavelength of 312 nm and a CHI-660E
88
electrochemical workstation (Chenghua, China) was employed, in turn, to measure the absorption
89
spectra, photoluminescence (PL) spectra and photoelectrochemical data of the samples. The
90
Brunauer-Emmett-Teller (BET) specific surface areas of samples were measured by an ASAP
91
2020HD88 nitrogen adsorption apparatus (Micromeritics, American).
UV-Visible-NIR spectrophotometer (Shimadzu, Japan), a
RF-5301PC
92
Catalytic Activity Test
93
The photocatalytic experiment for conversion of methane was conducted in a home-made vessel
94
with a quartz-glass cap using a 300W Xe lamp as light source (Figure S1). The mixture gas, which
95
was mixed by 1000 ppm CH4 gas and pure air (O2: N2 = 20: 80), was used as a target gas to simulate
96
the emissions of methane from landfills, waste-water treatment, natural gas leakage, livestock
97
farming and rice cultivation.4 50 mg of the as-prepared photocatalyst was evenly deposited on the
98
bottom of vessel. Then, the target gas was pumped into the vessel for 15 min to remove the residual
99
air. Furthermore, the products were qualitatively measured by the gas chromatography
100 101
(Zhongkehuifen 7820, China). Discussion and Results
ACS Paragon Plus Environment
5
ACS Sustainable Chemistry & Engineering 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 6 of 25
102
As displayed in Figure 1a, the identified peaks in the XRD patterns of the series of
103
nanocomposites were well indexed to the peaks of the pure Cs0.33WO3 sample without any
104
impurities, but the identified diffraction peaks of the pure g-C3N4 sample cannot be clearly
105
observed in the XRD patterns of the three nanocomposites, because of the poor crystallinity and
106
high dispersion of the g-C3N4 in the composites.31 Therefore, Raman spectroscopy was employed
107
to confirm the existence of g-C3N4 in the composite. Figure 1b demonstrates that four identified
108
peaks of the g-C3N4 sample at 470, 710, 980 and 1220 cm−1 are spotted in the Raman spectrum of
109
the 30CW sample, verifying the existence of g-C3N4 in the 30CW sample.32 Furthermore, FT-IR
110
was used to research the interface between the Cs0.33WO3 and g-C3N4 in the composite. In the FT-
111
IR spectra of the pure g-C3N4 and 30CW samples as shown in Figure 1c, the troughs at 800 cm-1,
112
the broad bands between 1200 and 1700 cm-1 as well as 3200 cm-1 correspond to the characteristic
113
breathing mode of tri-s-triazine units, the stretching vibration of C-N aromatic ring and the N-H
114
stretching vibration, respectively.33-36 It can be noted that the W-O bond stretching vibration band
115
in the FT-IR spectrum of the 30CW sample displays a slight right shift as compared to that of the
116
pure Cs0.33WO3 sample (Figure 1d), indicating that the g-C3N4 in the composite affects the W-O
117
bond of the Cs0.33WO3 in the composite.37
ACS Paragon Plus Environment
6
Page 7 of 25 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 Sustainable Chemistry & Engineering
118 119 120
Figure 1. The XRD patterns (a), Raman spectra (b), FT-IR spectra (c) and magnified FT-IR spectra (d) of the different samples.
121
Firstly, SEM test was conducted to directly observe the morphology of the samples. The cloud-
122
like particles in the Figure S2a attribute to the g-C3N4 samples and the rod-like samples in the
123
Figure S2b correspond to the Cs0.33WO3 samples, respectively. Besides, Figure S2c displays that
124
the Cs0.33WO3 was wrapped by the g-C3N4 in the composites. Furthermore, as shown in Figure 2a-
125
f, HAADF-STEM and mapping analyses directly demonstrate the elements spatial distribution and
126
morphology of the 30CW sample. It is not hard to be seen that a large number of blade-like g-C3N4
127
samples were loaded on the surface of rod-like Cs0.33WO3 sample to form the mace-like
128
nanocomposites. From Figure 2g-h, the lattice fringe spacing of 0.32 nm is observed on Cs0.33WO3
129
nanorods, which is assigned to (200) crystallographic plane with 0.32 nm lattice fringe spacing.
ACS Paragon Plus Environment
7
ACS Sustainable Chemistry & Engineering 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 8 of 25
130
Meanwhile, the SAED pattern displays two closest light spots, which attribute to the (202) and
131
(200) planes, respectively (Figure 2i). The above results prove that g-C3N4 nanosheets were
132
successfully anchored onto the Cs0.33WO3 nanorods.
133 134 135
Figure 2. The elements mapping (a-f), TEM image (g), HRTEM image (h) and SEAD pattern (i) of the 30CW sample.
136
The survey XPS spectrum in Figure 3a displays that the as-prepared 30CW sample is composed
137
of W, C, N, O and Cs elements. As shown in Figure 3b, the C 1s spectrum can be deconvoluted
138
into two components of the sp2 carbon (284.6 eV) and N=C-N bond (287.5 eV), respectively.38
139
The insert of Figure 3c illustrates that Cs 3d has two binding-energy peaks at 133.2 and 134.8 eV,
140
which correspond to Cs 3d5/2, and Cs 3d3/2, respectively.37 The peaks of N 1s at 398.2, 399.3 and
ACS Paragon Plus Environment
8
Page 9 of 25 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 Sustainable Chemistry & Engineering
141
400.7 eV are attributed to the bonds of C-N=C, N-C3 and N-H, respectively (Figure 3d).39 The O
142
1s binding-energy peaks locate at 533.2 eV from the bond of O-H (H2O), 531.5 eV from the
143
adsorbed O2 and 529.8 eV from the bond of O-W (Figure 3e).40 In addition, the W 4f binding-
144
energy spectrum in Figure 3f demonstrates four peaks. The peaks at 35.5 and 37.4 eV belong to
145
W6+, and the other peaks at 34.0 and 36.4 eV correspond to W5+.41
146 147 148
Figure 3. The survey XPS spectrum of 30CW (a) and its corresponding high resolution XPS spectra of C 1s (b), Cs 3d (c), N 1s (d), O 1s (e) and W 4f (f), respectively.
149
Figure 4a shows the methanol yield of the corresponding samples at CH4 (1000ppm) and pure
150
air mixed atmosphere under the irradiation of full spectrum light and at the room temperature. The
151
pure Cs0.33WO3 sample did not display photocatalytic activity for conversion of methane. Figure
152
4a and S3 demonstrate that pure g-C3N4 sample photo-catalyzed methane to CO2 and CO directly.
153
In addition, the per gram of the 10CW, 30CW and 70CW samples can convert methane into ca.
154
0.66, 17.50 and 7.70 µmol of methanol, respectively, under full spectrum light irradiation for 4 h.
ACS Paragon Plus Environment
9
ACS Sustainable Chemistry & Engineering 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 10 of 25
155
Importantly, the optimized 30CW sample displayed the best performance of selective
156
photocatalysis under the same reaction condition. As shown in Figure 4b, the photocatalytic
157
product of the 30CW sample consists of ca. 51.59 % of CH3OH, ca. 12.08 % of CO and ca. 36.33
158
% of CO2, deducing that the Cs0.33WO3 in the composite protected the intermediates from
159
peroxidation. As shown in Figure S4, the 30CW sample did not demonstrate photocatalytic activity
160
for conversion of methane under near infrared light irradiation and displayed nice activity under
161
ultraviolet light irradiation. In Figure 4c, the 30CW sample still presented good photocatalysis and
162
photostability after 4 times tests (4 h full spectrum light irradiation for each time). In order to
163
confirm that the production of methanol was really originated from methane, the reaction of
164
photocatalytic conversion of methane was conducted using the 30CW sample in a pure air (N2: O2
165
= 80: 20) atmosphere without any carbon gases. It is easily to be seen from Figure S5 that no
166
product is generated in the above condition, revealing that the carbon of methanol in the products
167
should come from methane. Figure 4d shows the FT-IR spectra of the fresh and reacted 30CW
168
samples, respectively. Methane has a special IR vibration mode at 1320 cm-1 which only can be
169
observed in the FT-IR spectrum of the reacted 30CW sample.6 Significantly, compared to the FT-
170
IR spectrum of the fresh 30CW sample, only the band of chemisorbed methyl radical at 1425 cm-
171
1 was detected
172
activation process.
in the reacted 30CW sample, implying that methyl is the only product in the methane
ACS Paragon Plus Environment
10
Page 11 of 25 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 Sustainable Chemistry & Engineering
173 174
Figure 4. The photocatalytic activities for conversion of methane of the samples at CH4 (1000
175
ppm) and pure air atmosphere under the irradiation of full spectrum light: the yield of CH3OH for
176
the pure g-C3N4, 10CW, 30CW, 70CW and pure Cs0.33WO3 samples (a), the generation of various
177
products during photocatalytic process over the 30CW sample (b), the photostability of the 30CW
178
sample (c), respectively, and the FT-IR spectra of the fresh and reacted 30CW samples (d).
179
The specific surface area, band structure, immigration of photogenerated carries and reaction
180
process were studied to clarify the mechanism of photocatalytic conversion of methane. As shown
181
in Table S1, the specific surface areas of all the samples are small (Table S1). DRS measurement
182
was carried out to study the light absorption capability and band structure of the photocatalysts.42
183
As shown in Figure 5a, the intrinsic absorption edges of all samples are less than 480 nm. In
184
addition, the band gap energy of the pure g-C3N4, pure Cs0.33WO3, 10CW, 30CW and 70CW
ACS Paragon Plus Environment
11
ACS Sustainable Chemistry & Engineering 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 12 of 25
185
samples are calculated to be approximate 2.75, 2.58, 2.61, 2.67 and 2.73 eV, respectively,
186
according to the formula:
187
𝐸𝑔 = hν𝑚𝑖𝑛 = hc/𝜆𝑚𝑎𝑥 = 1240 ⁄ 𝜆𝑚𝑎𝑥
(1)
188
where, h is the Planck constant (6.626×10-34 J S), ν min is the minimum frequency of light, c is the
189
speed of light (3×108 m/s), λmax is the maximum absorption edge and Eg is band gap. Furthermore,
190
except the g-C3N4 sample, the other samples display the near infrared (NIR) light absorption
191
property more or less, because the W5+ atoms in the Cs0.33WO3 based samples and pure Cs0.33WO3
192
sample contribute a new band.43,44 Figure 5b demonstrates the VB maximum position of the pure
193
g-C3N4, pure Cs0.33WO3 and 30CW samples are located at 1.50, 1.86 and 1.44 eV, respectively.
194
Therefore, The CB minimum positions of the pure g-C3N4, pure Cs0.33WO3 and 30CW samples
195
are calculated to be -1.25, -0.72 and -1.23 eV, respectively, according to the formula:
196
𝐸𝐶𝐵 = 𝐸𝑉𝐵 − 𝐸𝑔
(2)
197
where, EVB is the VB maximum potential and ECB is CB minimum potential. In addition, the broad
198
peaks nearby the Femi level imply that lots of electrons are localized at this state.45 Therefore, the
199
photons could easily drive the electrons from the localization state to CB.44
200
ACS Paragon Plus Environment
12
Page 13 of 25 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 Sustainable Chemistry & Engineering
201
Figure 5. UV-vis-NIR DRS spectra for the pure g-C3N4, 10CW, 30CW, 70CW and pure
202
Cs0.33WO3 samples (a) and valence band XPS measurement plots for the pure g-C3N4, 30CW and
203
pure Cs0.33WO3 samples (b).
204
PL and photoelectrochemical measurements were conducted to evaluate the separation ability
205
of photogenerated carries. Figure 6a displays the two broad photoluminescence peaks between 440
206
and 470 nm, implying that the photoinduced electrons and holes in the 30CW sample have lower
207
recombination ratio than that in the pure g-C3N4 sample.46 In addition, the transient photocurrent
208
responses of the g-C3N4, Cs0.33WO3 and 30CW samples illustrate uniform photocurrent response
209
(Figure 6b). Compared to the pure components, the 30CW sample showed the best photocurrent
210
response and the lowest electrical impedance (Figure 6c), indicating that the 30CW sample can
211
more effectively separate and immigrate the photogenerated carries than the g-C3N4 and Cs0.33WO3
212
samples.47
213
The radical species trapping experiments were implemented to study the process of
214
photocatalytic conversion of methane. 0.2 mmol of K2Cr2O7, para-Quinone, salicylic acid and
215
Na2C2O4 were adopted as the scavengers of e-, •O2-, •OH and h+, respectively.48 As shown in Figure
216
6d, both K2Cr2O7 and para-Quinone strongly affect the yield of methanol, implying that the •O2-
217
and e- should be main radicals in the process of photocatalytic conversion of methane. Meanwhile,
218
both salicylic acid group and Na2C2O4 group have no obvious effect on the methanol yield,
219
indicating that the •OH and h+ radicals were not main radicals in the photocatalytic reaction.
220
Furthermore, anaerobic condition experiment in Figure S6 verifies that the oxygen in the air
221
participated in the photocatalytic conversion reaction of methane. So, it is deduced that the •O2-
222
promoted the generation of methoxyl radicals.
ACS Paragon Plus Environment
13
ACS Sustainable Chemistry & Engineering 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 14 of 25
223 224
Figure 6. Photoluminescence spectra under 312 nm excitation for the 30CW and g-C3N4
225
samples (a), transient photocurrent responses under full spectrum light irradiation (b) and
226
electrochemical impedance spectra (c) for the 30CW, pure g-C3N4 and pure Cs0.33WO3 samples,
227
the radical species trapping experiments of the 30CW sample (d).
228
Figure 7a demonstrates the activation mechanism that the photocatalyst oxidize methane to
229
methyl using •O2-. As shown in Figure 7b, the following reaction processes are divided to two
230
reaction pathways, including selective oxidation path and peroxidation path. In the selective
231
oxidation pathway, the photogenerated free electron from Cs0.33WO3 transferred rapidly to the
232
decorated g-C3N4 and inhibited the peroxidation of methoxyl radicals. In addition, a little CO2
233
produced in the photocatalytic conversion might be attributed to the oxidation of methane over the
234
g-C3N4 nanosheets that did not bond with the Cs0.33WO3 nanorods in the composite.
ACS Paragon Plus Environment
14
Page 15 of 25 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 Sustainable Chemistry & Engineering
235 236
Figure 7. The activation mechanism for photocatalytic oxidation of methane (a) and proposed
237
reaction scheme for photocatalytic conversion of methane (b).
238
Conclusions
239
A series of mace-like
[email protected] nanocomposites were prepared using ultrasonic
240
assisted synthesis strategy for photocatalytic conversion of low concentration methane into
241
methanol under mild conditions. The optimized
[email protected] composite showed superior
242
photocatalytic performance for conversion of methane into methanol, attributing to the synergistic
243
effect of photoinduced •O2- from the g-C3N4 in the composite and photogenerated electrons from
244
the Cs0.33WO3 in the composite. The •O2- dominated the cleavage rate the C-H bond and prompted
245
the generation of the intermediate, methoxyl. The photogenerated electrons protected the methoxyl
246
from the peroxidation and selectively enhanced the conversion ratio from methoxyl into methanol.
247
The strategy of components proportion regulating in the
[email protected] nanocomposites
248
controlled the production of •O2- radical and photogenerated electrons, resulting in the effective
ACS Paragon Plus Environment
15
ACS Sustainable Chemistry & Engineering 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 16 of 25
249
and selective photocatalytic performance. This research supplied a new strategy for selective
250
photocatalytic conversion of methane into added-value products.
251
ASSOCIATED CONTENT
252
Supporting Information
253
The schematic diagram of photocatalytic experiment for conversion of methane; The
254
photocatalytic performance for conversion of methane for the pure g-C3N4 sample; The
255
photocatalytic performance for conversion of methane for the 30CW sample under pure air
256
condition; The photocatalytic performance for conversion of methane without O2.
257
AUTHOR INFORMATION
258
Corresponding Author
259
* Phone; Fax: +86-27-87887445; E-mail:
[email protected] (G.K. Zhang) ;
260
[email protected] (X.Y. Wu).
261
Notes
262
The authors declare no competing financial interest.
263
Author Contributions
264
†Y.
265
Zhang and X.Y. Wu conceived the project; K. Wang helped to discuss the results and the
266
corresponding analysis.
267
ACKNOWLEDGMENT
Li and J. Li contributed equally to this paper; Y. Li and J. Li performed the experiments; G.K.
ACS Paragon Plus Environment
16
Page 17 of 25 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
268
ACS Sustainable Chemistry & Engineering
This work was supported by the National Natural Science Foundation of China (NSFC
269
No.51472194 and No.51602237) and the NSFC of Hubei Province (2610CFA078).
270
REFERENCES
271
(1) Dong, L.; Wei, S.; Tan, S.; Zhang, H. GTL or LNG: which is the best way to monetize “
272
stranded” natural gas? Petro. Sc. 2008, 5, 388-394, DOI: 10.1007/s12182-008-0063-8.
273 274
(2) Kirschke, S.; Bousquet, P.; Zeng, G. Three decades of global methane sources and sinks. Nat. Geosci. 2013, 6, 813-823, DOI: 10.1038/ngeo1955.
275
(3) Alvarez, R. A.; Pacala, S. W.; Winebrake, J. J.; Chameides, W. L.; Hamburg, S. P. Greater
276
focus needed on methane leakage from natural gas infrastructure. Proc. Natl Acad. Sci. 2012,
277
109, 6435-6440, DOI: 10.1073/pnas.1202407109.
278 279
(4) Schmale, J.; Shindell, D.; Schneidemesser, E. V.; Chabay, I.; Lawrence, M. Air pollution: Clean up our skies. Nature 2014, 515, 335-337, DOI: 10.1038/515335a.
280
(5) Chen, X.X.; Li, Y.P.; Pan, X.Y.; Cortie, D.; Huang, X.T.; Yi, Z.G. Photocatalytic oxidation
281
of methane over silver decorated zinc oxide nanocatalysts, Nat. Commun. 2016, 7, 12273.
282
DOI: 10.1038/ncomms12273.
283
(6) Sobolev, V.I.; Dubkov, K.A.; Panna, O.V.; Panov, G.I. Selective oxidation of methane to
284
methanol on a FeZSM-5 surface. Catal. Today 1995, 24, 251-252, DOI: 10.1016/0920-
285
5861(95)00035-E.
286
(7) Starokon, E.V.; Parfenov, M.V.; Arzumanov, S.S.; Pirutko, L.V.; Stepanov, A.G.; Panov. G.I.
287
Oxidation of methane to methanol on the surface of FeZSM-5 zeolite. J. Catal. 2013, 300, 47
288
-54. DOI: 10.1016/j.jcat.2012.12.030.
ACS Paragon Plus Environment
17
ACS Sustainable Chemistry & Engineering 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 18 of 25
289
(8) Groothaert, M.H.; Smeets, P.J.; Sels, B.F.; Jacobs, P.A.; Schoonheydt, R.A. Selective
290
oxidation of methane by the Bis(μ-oxo)dicopper core stabilized on ZSM-5 and mordenite
291
zeolites. J. Am. Chem. Soc. 2005, 127, 1394-1395, DOI: 10.1021/ja047158u.
292
(9) Sheppard, T.; Hamill, C.D.; Goguet, A.; Rooney, D.W.; Thompson, J.M. A low temperature,
293
isothermal gas-phase system for conversion of methane to methanol over Cu-ZSM-5. Chem.
294
Commun. 2014, 50, 11053-11055, DOI: 10.1039/c4cc02832e.
295
(10) Sushkevich, V.L.; Palagin, D.; Ranocchiari, M.; van Bokhoven, J.A. Selective anaerobic
296
oxidation of methane enables direct synthesis of methanol. Science 2017, 356, 523-527, DOI:
297
10.1126/science.aar4968.
298 299
(11) Shilov, A.E.; Shul’pin, G.B. Activation of C-H bonds by metal complexes. Chem. Rev. 1997, 97, 2879-2932, DOI: 10.1007/s12182-008-0063-8.
300
(12) Mukherjee, S.; Maji, B.; Tlahuext-Aca, A.; Glorius, F. Visible-light-promoted activation of
301
unactivated C(sp3)-H bonds and their selective trifluoromethylthiolation. J. Am. Chem. Soc.
302
2016, 138, 16200-16203, DOI: 10.1021/jacs.6b09970.
303
(13) Graetzel, M.; Thampi, K.R.; Kiwi, J. Methane oxidation at room temperature and atmospheric
304
pressure activated by light via polytungstate dispersed on titania. J. Phys. Chem. 1989, 93,
305
4128-4132, DOI: 10.1021/j100347a050.
306 307 308 309
(14) Lien, C.F.; Chen, M.T.; Lin, Y.F.; Lin, J.L. Photooxidation of methane over TiO2. J. Chin. Chem. Soc. 2004, 51, 37-42, DOI: 10.1002/jccs.200400007. (15) Yuliati, L.; Yoshida, H. Photocatalytic conversion of methane. Chem. Soc. Rev. 2008, 37, 1592-1602, DOI: 10.1039/B710575B.
ACS Paragon Plus Environment
18
Page 19 of 25 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 Sustainable Chemistry & Engineering
310
(16) In, S.; Nielsen, M.G.; Vesborg, P.C.K.; Hou, Y.D.; Abrams, B.L.; Henriksen, T.R.; Hansen,
311
O.; Chorkendorff, I. Photocatalytic methane decomposition over vertically aligned transparent
312
TiO2 nanotube arrays. Chem. Commun. 2011, 47, 2613-2615, DOI: 10.1039/c0cc02570d.
313
(17) Villa, K.; Murcia-López, S.; Andreu, T.; Morante, J.R. Mesoporous WO 3 photocatalyst for
314
the partial oxidation of methane to methanol using electron scavengers. Appl. Catal. B:
315
Environ. 2017, 201, 128-136, DOI: 10.1016/j.apcatb.2014.07.055.
316
(18) Cook, A.K.; Schimler, S.D.; Matzger, A.J.; Sanford, M.S. Catalyst-controlled selectivity in
317
the C-H borylation of methane and ethane. Science 2016, 351, 1421-1424, DOI:
318
10.1126/science.aad9289.
319
(19) Sushkevich, V.L.; Palagin, D.; van Bokhoven, J.A. The effect of the active-site structure on
320
the activity of Copper Mordenite in the aerobic and anaerobic conversion of methane into
321
methanol. Angew. Chem. Int. Ed. 2018, 57, 8906-8910, DOI: 10.1002/anie.201802922.
322
(20) Dong, B.B.; Liu, T.F.; Li, C.; Zhang, F.X. Species, engineering and characterizations of
323
defects in TiO2-based photocatalyst. Chinese Chem. Lett. 2018, 29, 671-680, DOI:
324
10.1016/j.cclet.2017.12.002.
325
(21) Xu, Y.X.; Li, A.L.; Yao, T.T.; Ma, C.T.; Zhang, X.W.; Shah, J.H.; Han, H.X. Strategies for
326
efficient charge separation and transfer in artificial photosynthesis of solar fuels.
327
ChemSusChem 2017, 10, 4277-4305, DOI: 10.1002/cssc.201701598.
328
(22) Zheng, M.; Cao, X.H.; Ding, Y.; Tian, T.; Lin, J.Q. Boosting photocatalytic water oxidation
329
achieved by BiVO4 coupled with iron-containing polyoxometalate: Analysis the true catalyst.
330
J. Catal. 2018, 363, 109-116, DOI: 10.1016/j.jcat.2018.04.022.
ACS Paragon Plus Environment
19
ACS Sustainable Chemistry & Engineering 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 20 of 25
331
(23) Bi, L.L.; Meng, D.D.; Bu, Q.J.; Lin, Y.H.; Wang, D.J.; Xie. T.F. Electron acceptor of Ni
332
decorated porous carbon nitride applied in photocatalytic hydrogen production. Phys. Chem.
333
Chem. Phys. 2016, 18, 31534-31541, DOI: 10.1039/C6CP05618K.
334
(24) Bi, L.L.; Xu, D.D.; Zhang, L.J.; Lin, Y.H.; Wang D.J.; Xie. T.F. Metal Ni-loaded g-C3N4 for
335
enhanced photocatalytic H2 evolution activity: the change in surface band bending. Phys.
336
Chem. Chem. Phys. 2015, 17, 29899-29905, DOI: 10.1039/C5CP05158D.
337
(25) Bi, L.L.; Gao, X.P.; Zhang, L.J.; Wang, D.J.; Zou, X.X.; Xie, T.F. Enhanced photocatalytic
338
hydrogen evolution of NiCoP/g-C3N4 with improved separation efficiency and charge transfer
339
efficiency. ChemSusChem 2018, 11, 276-284, DOI: 10.1002/cssc.201701574.
340
(26) Lustemberg, P.G.; Palomino, R.M.; Gutiérrez, R.A.; Grinter, D.C.; Vorokhta, M.; Liu, Z.Y.;
341
Ramírez, P.J.; Matolín, V.; Ganduglia-Pirovano, M.V.; Senanayake, S.D.; Rodriguez, J.A.
342
Direct conversion of methane to methanol on Ni-Ceria surfaces: metal-support interactions
343
and water-enabled catalytic conversion by site blocking. J. Am. Chem. Soc. 2018, 140, 7681-
344
7687, DOI: 10.1021/jacs.8b03809.
345 346
(27) Takeda, H.; Adachi, K. Near infrared absorption of tungsten oxide nanoparticle dispersions. J. Am. Ceram. Soc. 2007, 90, 4059-4061, DOI: 10.1111/j.1551-2916.2007.02065.x.
347
(28) Guo, C.S.; Yin, S.; Huang, Y.F.; Dong, Q.; Sato, T. Synthesis of W 18O49 nanorod via
348
ammonium tungsten oxide and its interesting optical properties. Langmuir 2011, 27, 12172-
349
12178, DOI: 10.1021/la202513q.
350
(29) Adachi, K.; Asahi, T. Activation of plasmons and polarons in solar control cesium tungsten
351
bronze and reduced tungsten oxide nanoparticles. J. Mater. Res. 2012, 27, 965-970, DOI:
352
10.1557/jmr.2012.25.
ACS Paragon Plus Environment
20
Page 21 of 25 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 Sustainable Chemistry & Engineering
353
(30) Li, Y.; Wu, X.Y.; Li, J.; Wang, K.; Zhang, G.K. Z-scheme g-C3N4@CsxWO3 heterostructure
354
as smart window coating for UV isolating, Vis penetrating, NIR shielding and full spectrum
355
photocatalytic decomposing VOCs. Appl. Catal. B: Environ. 2018, 229, 218-226, DOI:
356
10.1016/j.apcatb.2018.02.024.
357
(31) Xu, J.; Zhang, L.W.; Shi, R.; Zhu, Y.F. Chemical exfoliation of graphitic carbon nitride for
358
efficient heterogeneous photocatalysis. J. Mater. Chem. A. 2013, 46, 4766-14772, DOI:
359
10.1039/c3ta13188b.
360
(32) Wang, X.M.; Ma, W.G.; Xu, Z.Q.; Wang, H.; Fan, W.J.; Zong, X.; Li, C. Metal phosphide
361
catalysts anchored on metal-caged graphitic carbon towards efficient and durable hydrogen
362
evolution
363
10.1016/j.nanoen.2018.04.011.
electrocatalysis.
Nano
Energy
2018,
48,
500-509,
DOI:
364
(33) Li, J.; Zhao, W.H.; Wang, J.; Song, S.X.; Wu, X.Y.; Zhang, G.K. Noble metal-free modified
365
ultrathin carbon nitride with promoted molecular oxygen activation for photocatalytic
366
formaldehyde oxidization and DFT study. Appl. Surf. Sci. 2018, 485, 59-69, DOI:
367
10.1016/j.apsusc.2018.07.015.
368
(34) Cui, Y.; Zhang, J.; Zhang, G.; Huang, J.; Liu, P.; Antonietti, M.; Wang, X. Synthesis of bulk
369
and nanoporous carbon nitride polymers from ammonium thiocyanate for photocatalytic
370
hydrogen evolution. J. Mater. Chem. 2011, 21, 13032, DOI: 10.1039/c1jm11961c.
371
(35) Liu, J.; Zhang, T.; Wang, Z.; Dawson, G.; Chen, W. Simple pyrolysis of urea into graphitic
372
carbon nitride with recyclable adsorption and photocatalytic activity. J. Mater. Chem. 2011,
373
21, 14398, DOI: 10.1039/c1jm12620b.
ACS Paragon Plus Environment
21
ACS Sustainable Chemistry & Engineering 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 22 of 25
374
(36) Liu, M.J.; Xia, P.F.; Zhang, L.Y.; Cheng, B.; Yu. J.G. Enhanced photocatalytic H 2‑production
375
activity of g‑C3N4 nanosheets via optimal photodeposition of Pt as cocatalyst. ACS
376
Sustainable Chem. Eng. 2018, 6, 10472−10480, DOI: 10.1021/acssuschemeng.8b01835.
377
(37) Shi, A.Y.; Li, H.H.; Yin, S.; Zhang, J.C.; Wang, Y.H. H 2 Evolution over g-C3N4/CsxWO3
378
under
379
10.1016/j.apcatb.2018.01.070.
NIR
light.
Appl.
Catal.
B:
Environ.
2018,
228,
75-86,
DOI:
380
(38) Chuang, P.K.; Wu, K.H.; Yeh, T.F.; Teng, H.S. Extending the π‑conjugation of g‑C3N4 by
381
incorporating aromatic carbon for photocatalytic H 2 evolution from aqueous solution. ACS
382
Sustainable Chem. Eng. 2016, 4, 5989-5997, DOI: 10.1021/acssuschemeng.6b01266.
383
(39) Wu, X.H.; Chen, F.Y.; Wang, X.F.; Yu, H.G. In situ one-step hydrothermal synthesis of
384
oxygen-containing groups-modified g-C3N4 for the improved photocatalytic H2-evolution
385
performance, Appl. Surf. Sci. 2018, 427, 645-653, DOI: 10.1016/j.apsusc.2017.08.050.
386
(40) Wu, X.Y.; Yin, S.; Xue, D.F.; Komarneni, S.; Sato, T. A Cs xWO3/ZnO nanocomposite as a
387
smart coating for photocatalytic environmental cleanup and heat insulation. Nanoscale 2015,
388
7, 17048-17054, DOI: 10.1039/c5nr04452a.
389
(41) Hou, J.G.; Cao, S.Y.; Wu, Y.Z.; Liang, F.; Sun, Y.F.; Lin, Z.S.; Sun, L.C. Simultaneously
390
efficient light absorption and charge transport of phosphate and oxygen-vacancy confined in
391
bismuth tungstate atomic layers triggering robust solar CO 2 reduction. Nano Energy 2017, 32,
392
359-366, DOI: 10.1016/j.nanoen.2016.12.054.
ACS Paragon Plus Environment
22
Page 23 of 25 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 Sustainable Chemistry & Engineering
393
(42) Li, J.; Wang, J.; Zhang, G.K.; Li, Y.; Wang, K. Enhanced molecular oxygen activation of
394
Ni2+-doped BiO2-x nanosheets under UV, visible and near-infrared irradiation: Mechanism and
395
DFT study. Appl. Catal. B: Environ. 2018, 234, 167-177, DOI: 10.1016/j.apcatb.2018.04.016.
396
(43) Guo, C.S.; Yin, S.; Yan, M.; Sato, T. Facile synthesis of homogeneous CsxWO3 nanorods with
397
excellent low-emissivity and NIR shielding property by a water controlled-release process. J.
398
Mater. Chem. 2011, 21, 5099-5105, DOI: 10.1039/c0jm04379f.
399
(44) Migas, D.B.; Shaposhnikov, V.L.; Rodin, V. N.; Borisenko, V.E. Tungsten oxides. I. Effects
400
of oxygen vacancies and doping on electronic and optical properties of different phases of
401
WO3. J. Appl. Phys. 2010, 108, 093713-093726, DOI: 10.1063/1.3505688.
402
(45) Zhang, N.; Jalil, A.; Wu, D.X.; Chen, S.M.; Liu, Y.F.; Gao, C.; Ye, W.; Qi, Z.M.; Ju, H.X.;
403
Wang, C.M.; Wu, X.J.; Song, L.; Zhu, J.F.; Xiong, Y.J. Refining defect states in W 18O49 by
404
Mo doping: A strategy for tuning N2 activation towards solar-driven nitrogen fixation. J. Am.
405
Chem. Soc. 2018, 140, 9434-9443, DOI: 10.1021/jacs.8b02076.
406
(46) Wang, K.; Wu, X.Y.; Zhang, G.K.; Li, J.; Li. Y. Ba5Ta4O15 nanosheet/AgVO3 nanoribbon
407
heterojunctions with enhanced photocatalytic oxidation performance: hole dominated charge
408
transfer path and plasmonic effect insight. ACS Sustainable Chem. Eng. 2018, 6, 6682-6692,
409
DOI: 10.1021/acssuschemeng.8b00477.
410
(47) Yang, G.; Ding, H.; Chen, D.M.; Feng, J.J.; Hao, Q.; Zhu, Y.F. Construction of urchin-like
411
ZnIn2S4-Au-TiO2 heterostructure with enhanced activity for photocatalytic hydrogen
412
evolution. Appl. Catal. B: Environ. 2018, 234, 260-267, DOI: 10.1016/j.apcatb.2018.04.038.
ACS Paragon Plus Environment
23
ACS Sustainable Chemistry & Engineering 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 24 of 25
413
(48) Wang, K.; Li, Y.; Zhang, G.K.; Li, J.; Wu. X.Y. 0D Bi nanodots/2D Bi3NbO7 nanosheets
414
heterojunctions for efficient visible light photocatalytic degradation of antibiotics: Enhanced
415
molecular oxygen activation and mechanism insight. Appl. Catal. B: Environ. 2019, 240, 39-
416
49, DOI: 10.1016/j.apcatb.2018.08.063.
417
ACS Paragon Plus Environment
24
Page 25 of 25 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
418
ACS Sustainable Chemistry & Engineering
Table of Contents (TOC)
419 420
Synopsis
421
The synergistic effect of g-C3N4 and Cs0.33WO3 in the composite results in the selectively
422
photocatalytic conversion of methane into methanol.
ACS Paragon Plus Environment
25