• Comment: Some of the major claims lack citations. Additionally, and perhaps more relevant to my current decline on this draft, the draft has substantial MOS issues. I would encourage you to proofread the draft again, remove overlinking, and remove notes like the one at the top of the article. Pbritti (talk) 22:44, 19 April 2024 (UTC)


Sonocatalysis is a field of sonochemistry which is based on the use of ultrasounds to change the reactivity of a catalyst in homogenous or heterogenous catalysis. It's generally used to support the catalysis. This way of catalysis is known since the creation of sonochemistry in 1927 by Alfred Lee Loomis (1887–1975) and Robert Williams Wood (1868–1955).[1]. Sonocatalysis (and even sonochemistry at all) depends on ultrasounds which were discovered in 1794 by the Italian biologist Lazarro Spallanzani (1729–1799)[2].

Principle edit

General concept edit

Sonocatalysis isn't a self-sufficient catalysis technique, due to supporting the catalysis in reaction. Sonocatalysis and sonochemistry both come from a phenomenon called “acoustic cavitation”, which happens when a liquid is irradiated by ultrasounds. Ultrasounds will create huge local variations of pressure and temperature, affecting liquid's relative density and creating cavitation bubbles when liquid pressure decreases under its vapor pressure. When these bubbles blow up, some energy is released, which comes from the transformation of kinetic energy into heat. Sonocatalysis may happens as in homogenous phase as in heterogenous phase. This depends on the phase in which the catalyst is compared to the reaction[1].

 
Principle of energy recovery using acoustic cavitation

The blowing of cavitation bubbles can cause intense local pressure and temperature conditions, going to a 1000 atm pressure and a 5000 K temperature[1]. This may provoke the creation of highly energetic radicals. Bubbles' blowing causes the formation of hydroxyl radical  and hydrogen radical  in a water-based environment. Next, these radical may match to produces different molecules as water  , hydroperoxyl   , hydrogen peroxide   and dioxygen  [3]

Radical formation reasctions due to the decomposition of water by ultrasonds can be described this way:

 

 

 

 

 

 

Energy from ultrasonic irradiation ultrasoniques differ from heat energy or electromagnetic radiation energy. It differs in time and in pressure and energy received by a molecule.[1]. For example, a 20 kHz ultrasound make an 8,34 x 10-11 eV energy, while a 300 nm laser makes an 4,13 eV energy. These ultrasounds cause a shorter reaction time and a better yield.

Direct and indirect irradiation edit

There are two types of irradiation in sonocatalysis and sonochemistry: direct irradiation and indirect radiation. In direct irradiation, the solution is in touch with sound waves emittor (generally a transducer), while these two elements are separated by an irradiated bath in indirect irradiation. The bath transmits the radiations to the solution due to convection. While indirect irradiation is the most used irradiation technique, direct irradiation is possible too, especially when the irradiated bath may be the container for the solution too[2].

Catalysts edit

Homogenous catalysts edit

Metal carbonyls, such as Fe(CO)5, Fe3(CO)12, Cr(CO)6, Mo(CO)6 and W(CO)6, are very used in homogenous catalysis, because these are stable species in standard temperature and pressure, due to their structures[4]. Furthermore, their catalytic capacities are well-known and efficient[5].

Heterogenous catalysts edit

Carbon-based species like carbon nanotube, graphene, graphene oxide, activated carbon, biochar, g-C3N4, carbon-doped materials, Buckminsterfullerene (C60), and mesoporous carbons, are very used in heterogenous sonocatalysis. These species are great sonocatalysts because they favour the degradation process during the sonocatalysis. Furthermore, they have a huge activity and stability for sonocatalysis, and they show the nucleation effect. These properties come from features like optic activities, electrical resistivities and conductivities, chemical stabilities, forces, and their porous structures. These species are today on the technologic rise and they are more and more used[3].

Materials edit

Transducers edit

Sonocatalysis needs other equipments more than catalysts to generate ultrasounds, like ultrasounds that create ultrasounds by the transformation from electrical energy to mechanical energy. There are two types of transducers: piezoelectric transducers, and magnetostrictic transducers. The most used transducer is the piezoelectric one because it's cheaper, lighter and less bulky. This transducer is constituted of single crystals or ceramic and two electrodes fixed on the side of the precedent materials. These electrodes receive a voltage which equals at the most to the transducer's resonance frequence. Then, single crystals may be compressed or dilated, and that creates a wave[2].

Some examples of transducers edit

  • The ultrasonic cleaner is a bath full of liquid. The liquid can transmit acoustic energy from the bottom of the bath to the solution in the container. This cleaner generates often ultrasounds with low frequences ( from 20 to 60 kHz ) and is cheap. However, it has some inconvenients, like the difficulty to control the liquid temperature in the bath, and the fact that irradiation isn't equal everywhere in the bath[2].
  • The cup-horn reactor seems like the ultrasonic cleaning, but it may irradiate using both direct and indirect irradiation. While ultrasonic cleaning only generates ultrasounds with low frequences, the cup-horn reactor can generate ultrasounds with high frequences too, and with a higher intensity. However, this equipment is very expensive due to its conception[2].
  • The « whistle » reactor is a reactor in which the reaction mix is continuously pumped through an adjustable-width opening, in a delimited area where cavitation happens. Ultrasonic waves are generated in this area by the vibration of blades during the passing of the pumped solution. This reactor is often used for homogenous reaction mixes, as the solid part of heterogenous mixes can’t pass through the whistle. About its use, this type of reactor is less used than the two precedent others[2].

Applications edit

The use of sonocatalysis has risen.[6] Today, sonocatalysis is used in lots of fields, like medicine, pharmacology, metallurgy, environment, nanotechnology, and wastewater treatment.

Health edit

Active ingredient synthesis edit

The example of pyrazole edit

Several studies showed that sonocatalysis could favour pyrazole synthesis yield, compounds that has antimicrobial, antihypertensive, anti-inflammatory and anticonvulsant activities.

A study developed a new way of synthsis for this molecule, using ecological and economical reactants while keeping a high yield and using sonocatalysis.[7]

 
3-methyl-5-phenyl-4,5-dihydro-1H-pyrazole-1-carbothioamide synthesis under sonocatalysis

The following table contains is an example for the 3-methyl-5-phenyl-4,5-dihydro-1H-pyrazole-1-carbothioamide synthesis:

3-methyl-5-phenyl-4,5-dihydro-1H-pyrazole-1-carbothioamide synthesis duration
Duration (min) Yield (%)
Reaction under sonocatalysis (*) 20 76
Reaction without sonocatalysis (*) 20 16
Literature[8] 120 66

(*) synthesis conditions are described on the picture above

Environment edit

Pollutants degradation edit

An example of the sonocatalysis use is to degrade pollutants. Indeed, ultrasounds can generate the  radical from a water molecule. his radical is a strong oxydizing agent, which can degrade persistent organic pollutent. However, reaction speed for hydrophobic compounds is low. That's why ultrasounds are often paired with a solid catalyst. The add of this catalyst means lthe add of atomic nucleus that amplify the cavity phenomenon, and so the ultrasonic efficiency too. Near the solid-liquid contact surface is applied an other pressure on one of the sides of the bubble, that causes a more violent blowing of the bubble[3].

46 cationic red bleaching edit

This principle can apply to the oxidated bleaching of 46 cationic red[9] by zinc oxide held by bentonite. Actually, more than 10% to 20% of organic dyes are lost and released in nature. Finding new ways to improve dyes’ bleaching is an actual topic, as these dyes may be toxic and carcinogenous. L’oxydation comes from the   radical, whose oxidant capacities are known. Indeed, we can observe that a higher concentration of the   radical provokes a better 46 red cationic bleaching, as the bleaching of cationic red is of 17,8% before using ultrasounds and of 81,6% after using ultrasounds[9]. However, sonocatalysis’ efficiency mainly comes from the combination of both catalyst and ultrasounds. For example, we observe a cationic red bleaching of only 25,4% by applying only ultrasounds[9].

Rhodamine B degradation edit

Sonocatalysis use is found in rhodamine B degradation too. Rhodamine B is a synthetic dye which may be harmful for aquatic plant when released in wastewater[10].

 
Rhodamine B molecule

Application to reactions edit

The Fenton's reaction edit

Sonocatalysis can be applied for reactions like Fenton's reaction. By associating sonocatalysis (at a 20 kHz frequence) and Fenton's reaction, with a 5,0 mg/L iron chloride (  ) mass concentration and a PH of 4, degradation efficiency is about 80% after 12 minutes[11].

References edit

  1. ^ a b c d Suslick, Kenneth S.; Didenko, Yuri; Fang, Ming M.; Hyeon, Taeghwan (1999-02-15). "Acoustic cavitation and its chemical consequences". Philosophical Transactions of the Royal Society of London. Series A: Mathematical, Physical and Engineering Sciences. 357 (1751): 335–353. Bibcode:1999RSPTA.357..335S. doi:10.1098/rsta.1999.0330. ISSN 1364-503X. Retrieved 2024-03-29.
  2. ^ a b c d e f Behling, Ronan, Nahla Araji, et Grégory Chatel. « Qu’est-ce que la sonochimie ? » L’actualité Chimique 410 (septembre 2016): 11‑20.
  3. ^ a b c Gholami, Peyman, Alireza Khataee, Reza Darvishi Cheshmeh Soltani, et Amit Bhatnagar. « A Review on Carbon-Based Materials for Heterogeneous Sonocatalysis: Fundamentals, Properties and Applications ». Ultrasonics Sonochemistry 58 (novembre 2019): 104681. https://doi.org/10.1016/j.ultsonch.2019.104681.
  4. ^ Ameen, J. G., et H. F. Durfee. « The structure of metal carbonyls ». Journal of Chemical Education 48, nᵒ 6 (1 juin 1971): 372. https://doi.org/10.1021/ed048p372.
  5. ^ Suslick, Kenneth S., James W. Goodale, Paul F. Schubert, et Hau H. Wang. « Sonochemistry and sonocatalysis of metal carbonyls ». Journal of the American Chemical Society 105, nᵒ 18 (1 septembre 1983): 5781‑85. https://doi.org/10.1021/ja00356a014.
  6. ^ « Sonochemistry and sonocatalysis: Harnessing sound for enhanced catalytic-assisted reactions ». Consulté le 26 février 2024. https://new.societechimiquedefrance.fr/wp-content/uploads/woocommerce_uploads/2023/11/489_AC11_2023_WEB_V2-bqo2n5.pdf.
  7. ^ Pizzuti, Lucas, Luciana A. Piovesan, Alex F. C. Flores, Frank H. Quina, et Claudio M. P. Pereira. « Environmentally friendly sonocatalysis promoted preparation of 1-thiocarbamoyl-3,5-diaryl-4,5-dihydro-1H-pyrazoles ». Ultrasonics Sonochemistry 16, nᵒ 6 (1 août 2009): 728‑31. https://doi.org/10.1016/j.ultsonch.2009.02.005.
  8. ^ Rathinasamy, Suresh, Subhas Somalingappa Karki, Shiladitya Bhattacharya, Lakshmanan Manikandan, Senthilkumar G. Prabakaran, Malaya Gupta, et Upal Kanti Mazumder. « Synthesis and anticancer activity of certain mononuclear Ru (II) Complexes ». Journal of enzyme inhibition and medicinal chemistry 21, nᵒ 5 (2006): 501‑7. https://doi.org/10.1080/14756360600703396.
  9. ^ a b c Darvishi Cheshmeh Soltani, Reza, Sahand Jorfi, Mahdi Safari, et Mohammad-Sadegh Rajaei. « Enhanced Sonocatalysis of Textile Wastewater Using Bentonite-Supported ZnO Nanoparticles: Response Surface Methodological Approach ». Journal of Environmental Management 179 (septembre 2016): 47‑57. https://doi.org/10.1016/j.jenvman.2016.05.001.
  10. ^ Sharma, Jyotshana, Shubhangani Sharma, Upma Bhatt, et Vineet Soni. « Toxic effects of Rhodamine B on antioxidant system and photosynthesis of Hydrilla verticillata ». Journal of Hazardous Materials Letters 3 (1 novembre 2022): 100069. https://doi.org/10.1016/j.hazl.2022.100069.
  11. ^ Xu, Yifan, Sergey Komarov, Takuya Yamamoto, et Takaaki Kutsuzawa. « Enhancement and Mechanism of Rhodamine B Decomposition in Cavitation-Assisted Plasma Treatment Combined with Fenton Reactions ». Catalysts 12, nᵒ 12 (décembre 2022): 1491. https://doi.org/10.3390/catal12121491.