2021
DOI: 10.1016/j.jtice.2021.01.028
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Understanding the origin of synergistic catalytic activities for ZnO based sonophotocatalytic degradation of methyl orange

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Cited by 28 publications
(7 citation statements)
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“…After 180 min of reaction, the BET specific surface area improved from 47.3 to 109.7 m 2 /g, and the average pore diameter increased from 20.1 to 27.7 nm, suggesting that the deaggregation of nanoparticles by ultrasound results in an enhancement in surface area. The same phenomenon was observed by Yang et al when three different morphologies of ZnO nanoparticles were synthesized and employed for sonophotocatalytic degradation of methyl orange. Surface areas of rod-like ZnO (ZnO-R) with 2.617 m 2 /g, flower-like ZnO (ZnO-F) with 14.98 m 2 /g, and sheet-like ZnO (ZnO-F) with 47.46 m 2 /g increased after the treatment.…”
Section: Sonophotocatalysis Mechanismssupporting
confidence: 79%
See 1 more Smart Citation
“…After 180 min of reaction, the BET specific surface area improved from 47.3 to 109.7 m 2 /g, and the average pore diameter increased from 20.1 to 27.7 nm, suggesting that the deaggregation of nanoparticles by ultrasound results in an enhancement in surface area. The same phenomenon was observed by Yang et al when three different morphologies of ZnO nanoparticles were synthesized and employed for sonophotocatalytic degradation of methyl orange. Surface areas of rod-like ZnO (ZnO-R) with 2.617 m 2 /g, flower-like ZnO (ZnO-F) with 14.98 m 2 /g, and sheet-like ZnO (ZnO-F) with 47.46 m 2 /g increased after the treatment.…”
Section: Sonophotocatalysis Mechanismssupporting
confidence: 79%
“…Sheet-like and flower-like morphologies usually have higher sonophotocatalytic activity, such as for the case of ZnO nanocatalysts, when compared to rod-like ZnO in the degradation of methyl orange. 46 Furthermore, desert rose morphology of ZnO with 50 nm nanosheet petals outperformed other ZnO morphologies, such as nanospheres, nanowires, and microwires in the RhB sonophotocatalytic removal. 58 For the degradation of MB, ZnS/ZnO nanotubes showed greater degradation rate than their nanorods counterpait.…”
Section: ■ Conclusion and Perspectivesmentioning
confidence: 95%
“… NiAl LDH Catalytic ozonation Methyl orange [pollutant] = 500 mg L −1 , [catalyst] = 1 g L −1 , ozone flow rate = 109 mg h −1 . ∼85 [36] ZnO Sonophotocatalysis Methyl orange [pollutant] = 50 mg L −1 , [catalyst] = 0.1 g L −1 , light source = 300 W, ultrasonic power = 200 W. ∼42 [37] ZnCr LDH Photocatalysis Rhodamine B, Rhodamine 6G, 4-chloro 2-nitro, phenol [pollutant] = 100 mg L −1 , [catalyst] = 1 g L −1 , light source = visible light. ∼57 ∼62 ∼30 [38] WS 2 Sonocatalysis Methylene blue [pollutant] = 10 mg L −1 , [catalyst] = 1 g L −1 , ultrasonic power = 250 W. ∼85 [39] FeAl LDH/ Hydrochar Photocatalysis Diethyl phthalate [pollutant] = 20 mg L −1 , [catalyst] = 1 g L −1 , light source = 500 W Xenon lamp.…”
Section: Resultsmentioning
confidence: 99%
“…Meanwhile, ZnO sonophotocatalysis synergistically accelerated the degradation of chrome intra orange G dye (30 kHz + 365 nm) [ 26 ]. Recent studies supported the existence of synergy in the ZnO-based sonophotocatalytic degradation of sulfamethoxazole (24 kHz + UVA LEDs) [ 27 ], rhodamine B (40/59 kHz + visible light) [ 28 ] and methyl orange dyes (40 kHz + Xe lamp) [ 29 ]. It should be emphasized that the above-cited studies dealt with synthesized ZnO-based composites.…”
Section: Resultsmentioning
confidence: 99%