| Literature DB >> 29302040 |
Yitao Dai1,2, Chao Li2, Yanbin Shen2,3, Tingbin Lim2, Jian Xu2, Yongwang Li2, Hans Niemantsverdriet2,4, Flemming Besenbacher1, Nina Lock5, Ren Su6.
Abstract
Solar-driven photocatalysis has attracted significant attention in water splitting, CO2 reduction and organic synthesis. The syntheses of valuable azo- and azoxyaromatic dyes via selective photoreduction of nitroaromatic compounds have been realised using supported plasmonic metal nanoparticles at elevated temperatures (≥90 °C); however, the high cost, low efficiency and poor selectivity of such catalyst systems at room temperature limit their application. Here we demonstrate that the inexpensive graphitic C3N4 is an efficient photocatalyst for selective syntheses of a series of azo- and azoxy-aromatic compounds from their corresponding nitroaromatics under either purple (410 nm) or blue light (450 nm) excitation. The high efficiency and high selectivity towards azo- and azoxy-aromatic compounds can be attributed to the weakly bound photogenerated surface adsorbed H-atoms and a favourable N-N coupling reaction. The results reveal financial and environmental potential of photocatalysis for mass production of valuable chemicals.Entities:
Year: 2018 PMID: 29302040 PMCID: PMC5754351 DOI: 10.1038/s41467-017-02527-8
Source DB: PubMed Journal: Nat Commun ISSN: 2041-1723 Impact factor: 14.919
Possible products formed by photocatalytic reduction of nitroaromatic compounds and comparison of the conversion and selectivity of different photocatalysts
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| Entry | Photocatalysts | Cost (€ g−1) | Radiation | Temperature (°C) | Conversion (%) | Selectivity (%) | ||
| Azoxy- | Azo- | Aniline | ||||||
| 1 | SiO2/CdS/Rha | 7.7 | 436 nm, 25 h | RT | 80 | 68 | 5 | 5 |
| 2 | Au/TiO2 b | 14.4 | >430 nm, 12 h | RT | 95 | 0 | 99 | N/A |
| 3 | Cu/Graphenec | 92.2 | >400 nm, 5 h | 90 | 98 | N/A | 98 | N/A |
| 4 | TiO2/N3/Ptd | 57.1 | 530 nm, 24 h | RT | >99 | 0 | 0 | 100 |
| 5 | Au/TiO2-Age | 7.6 | >450 nm, 10 h | RT | 100 | 0 | 0 | 100 |
| 6 | Ni2P/CdSf | 6.2 | >420 nm, 24 h | RT | 99 | 0 | 0 | >99 |
| 7 | g-C3N4 g | 0.1 | 450 nm, 12 h | RT | 97 | 95 | 5 | 0 |
| 8 | g-C3N4 h | 0.1 | 410 nm, 5 h | RT | 95 | 6 | 94 | 0 |
| 9 | A-g-C3N4 g | 0.1 | 450 nm, 12 h | RT | 1 | 99 | 0 | <1 |
a High-pressure Hg lamp (0.007 W cm−2)[18]
b 0.01 M KOH, 300 W Xe lamp (>430 nm, 0.01 W cm−2)[19]
c 0.01 M KOH, 300 W Xe lamp (400–800 nm, 0.15 W cm−2)[16]
d N3 dye on TiO2 with Pt, triethanolamine (TEOA) as scavenger, 3 W 530 nm LED[26]
e 500 W Xe lamp (450–600 nm, 0.083 W cm−2)[24]
f LED lamp (>420 nm, 30 × 3 W), Na2S and Na2SO3 in water[23]
g 0.01 M KOH, 450 nm LED (440–460 nm, 0.03 W cm−2)
h 0.01 M KOH, 410 nm LED (400–420 nm, 0.03 W cm−2)
Fig. 1Photocatalytic performance. a, b Photoconversion (Con.) and selectivity (Sel.) of nitrobenzene to azobenzene and azoxybenzene using g-C3N4 under 410 and 450 nm irradiation (lab-scale). c Photoconversion of nitrobenzene to azoxybenzene using g-C3N4 at different starting concentrations under 450 nm irradiation. Reaction conditions: 8 mM nitrobenzene, 10 mM KOH, and 50 mg catalyst in 10 mL isopropanol under N2 atmosphere. d, e Up-scaled reactions with volumes of 800 mL and 80 L, respectively. The nitrobenzene photoconversion tests were performed under solar radiation in Beijing (30/9/2016-2/10/2016, 25-30 °C, 800 mL) and Shenzhen (18/12/2016-5/1/2017, 25–30 °C, 80 L). The starting concentration of nitrobenzene was 8 mM. f, g Conversion and selectivity for the scaled-up tests
Photocatalytic reduction of various nitroaromatic compounds to azoxy- (I) and azo- (II) aromatic compounds using the g-C3N4 photocatalyst
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| Entry | R | Light (nm) | Time (h) | Conversion (%) | Selectivity (%) | Ratio | ||
| I + II | Amine | I | II | |||||
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| 410 | 8 | 100 | 100 | 0 | 2 | 98 |
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| 450 | 12 | 100 | 100 | 0 | 92 | 8 | |
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| 410 | 20 | 95 | 100 | 0 | 5 | 95 |
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| 450 | 14 | 92 | 90 | 10 | 99 | 1 | |
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| 410a | 38 | 98 | 100 | 0 | 3 | 97 |
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| 450b | 60 | 100 | 96 | 4 | 94 | 6 | |
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| 410c | 35 | 100 | 100 | 0 | 4 | 96 |
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| 450c | 36 | 95 | 100 | 0 | 92 | 8 | |
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| 410 | 13 | 100 | 100 | 0 | 8 | 92 |
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| 450d | 12 | 100 | 90 | 10 | 63 | 37 | |
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| 410b | 20 | 100 | 91 | 9 | 7 | 93 |
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| 450e | 12 | 96 | 99 | 1 | 97 | 3 | |
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| 410f | 20 | 100 | 100 | 0 | 0 | 100 |
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| 450g | 24 | 90 | 100 | 0 | 93 | 7 | |
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| 410 | 14 | 90 | 94 | 6 | 5 | 95 |
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| 450g | 12 | 100 | 100 | 0 | 98 | 2 | |
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| 410 | 12 | 60 | 100 | 0 | 0 | 100 |
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| 450 | 12 | 80 | 100 | 0 | 95 | 5 | |
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| 410b | 30 | 100 | 100 | 0 | 0 | 100 |
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| 450g | 60 | 91 | 100 | 0 | 90 | 10 | |
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| 410h | 24 | 100 | 100 | 0 | 3 | 97 |
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| 450e | 20 | 93 | 100 | 0 | 99 | 1 | |
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| 410b | 22 | 100 | 100 | 0 | 0 | 100 |
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| 450i | 38 | 100 | 100 | 0 | 90 | 10 | |
General reaction conditions: 8 mM substrates, 30 mW cm−2 light intensity, 10 mM KOH, and 50 mg catalyst in 10 mL isopropanol under deaerated condition
a20 mW cm−2, 4 mM p-iodo nitrobenzene
b20 mW cm−2
c20 mW cm−2, 20 mM KOH
d30 mW cm−2, 20 mM KOH
e30 mW cm−2, 40 mM KOH
f10 mW cm−2, 40 mM KOH
g30 mW cm−2
h20 mW cm−2, 40 mM KOH
i10 mW cm−2, 20 mM KOH
Fig. 2Reaction mechanism analysis. a The consumption of dissolved O2 (O2 reduction and isopropanol oxidation) under irradiation using various photocatalysts determined by in-situ MS. A 365 nm LED was used for TiO2 and a 450 nm LED was used for all other tests. b Post-mortem TPD spectra revealing the desorption of Hads from the g-C3N4 and A-g-C3N4 surfaces. The TPD was performed on vacuum dried samples after reaction without adsorption of additional H2. c Scheme of the suggested reaction pathway. The reduction reaction will be hindered if Hads binds strongly to the catalyst. d Reaction path for the photoconversion of nitroaromatic compounds to azoxy-, azo-aromatic compounds, and amines. NBS = Nitrosobenzene, NPH = N-phenylhydroxylamine
Fig. 3Proposed reaction mechanisms. a Energy scheme of the photocatalytic nitrobenzene reduction on g-C3N4. The redox potentials of nitrobenzene (NB) to azoxybenzene plus isopropanol (IP) to acetone (AC), and the CB and VB positions are referenced to the SHE[32,33]. b and c suggested possible active sites for isopropanol oxidation and nitrobenzene reduction according to calculations. Grey: C, light purple: N, white: structural H, light blue: surface adsorbed H (Hads)