Literature DB >> 33817488

Hydrodynamic Cavitation of Creosote Oil in the Presence of a Ni2+ Initiator Results in an Increase in Its Overall Naphthalene Content.

Yu-Fang Ye1, Ying Zhu1, Zhi Su1, Feng-Yun Ma1, Ting Liang1.   

Abstract

Hydrodynamic cavitation (HC) of aromatic hydrocarbons present in creosote oil obtained from coal tar in the presence of 0.3% (w/w) Ni2+ as an inducer increased its naphthalene and phenanthrene content by 7.3 and 2.6%, respectively. An optimal procedure was developed based on the use of an upstream pressure of 2.6 MPa, an immersing height (H) for the cavitator of 105 mm, 10% H2O content, use of a NiSO4 solution at pH 4.0, and an operating temperature of 75 °C. Enrichment of the naphthalene and phenanthrene components is caused by hydroxyl and hydrogen radicals generated in the reaction inducing aromatic components to undergo a series of radical demethylation/methylation reactions to produce new product ratios. The observed increases in naphthalene and phenanthrene content using Ni2+ as a radical inducer are in contrast with the previous results using Fe2+ under similar conditions, which led to the enrichment of the acenaphthalene fraction of creosote oil.
© 2021 The Authors. Published by American Chemical Society.

Entities:  

Year:  2021        PMID: 33817488      PMCID: PMC8015093          DOI: 10.1021/acsomega.0c06357

Source DB:  PubMed          Journal:  ACS Omega        ISSN: 2470-1343


Introduction

More than 500 different types of organic compounds have been identified in coal tar, with many of its components being extremely useful as raw materials for the production of plastics, synthetic rubbers, synthetic fibers, dyes, pesticides, and medicines.[1] Furthermore, some of the polycyclic and heterocyclic compounds that it contains are difficult to obtain from other sources or cannot be prepared economically using synthetic routes. Therefore, coal tar represents a precious natural organic hydrocarbon source from which existing/new chemicals can be isolated. The creosote oil fraction accounts for around 9% of coal tar, which is a mixture of volatile components that boil over a range from 218 to 340 °C that are mainly comprised of bicyclic and tricyclic aromatic hydrocarbons.[2] Creosote oil is a complex mixture containing over 50 types of aromatic hydrocarbons, including naphthalene, quinoline, methyl naphthalene, biphenyl, dimethyl naphthalene, acenaphthene, dibenzofuran, fluorene, and anthracene (phenanthrene).[3] However, the abundance of individual components in creosote oil is generally low, with 2-methyl-naphthalene having the highest content at 20%, and only 11 other compounds exceeding 1%. Therefore, it is difficult to economically separate creosote oil into its pure constituents using the commonly available industrial separation technologies. Hydrodynamic cavitation (HC) refers to the process of formation, growth, and collapse of cavities (cavitation) caused by the change in the liquid pressure field during a liquid flow.[4] A large number of small holes in the liquid generated shock waves and microjets in the process of collapse, resulting in a strong collision and mixing between liquid particles so that different components of the liquid can be fully mixed, especially in the liquid–liquid heterogeneous system, which can achieve the emulsion state. Thanekar et al.[5] studied the combination of HC and oxidant in the treatment of industrial wastewater. The optimal pretreatment method of HC + O3 can reduce the chemical oxygen demand (COD) by 40%, and the further activation of the sewage treated by the HC + O3 process can reduce COD by about 89.5% after sludge treatment. The biodegradation index increased from 0.35 to 0.75 by the HC + O3 pretreatment. Yi et al.[6] studied the decomposition of Rhodamine B (RHB) by hydrodynamic method (HC) and acoustic method (AC) and the combination of the two methods. Both hydrodynamic and acoustic degradation can be carried out in the same space. The effects of initial concentration, inlet pressure, solution temperature, and ultrasonic power were studied and discussed. A clear synergy has been found in this process. Under the condition of ultrasonic power of 220 W and treatment time of 30 min, the highest conversion rate of the hydraulic ultrasonic cavitation system can reach 119%, which greatly increases the degradation efficiency of the hydraulic cavitation. Cai et al.[7] explored the dewatering of waste-activated sludge by integrated hydrodynamic cavitation (HC) and Fenton reaction and revealed the synergism of the HC/Fenton treatment. The results indicate a three-step mechanism, namely, the HC fracture of different extracellular polymeric substances (EPSs) in sludge flocs, Fenton oxidation of the released EPS, and Fe(III) reflocculation, which is responsible for the synergistically enhanced sludge dewatering. Boczkaj et al.[8] studied the combination of HC and other oxidation processes (O3/H2O2/Peroxone) for the treatment of asphalt production wastewater (initial COD was in the range of 8000–12 000 mg/L). The results showed that the maximum reduction rates of COD and biological oxygen demand (BOD) were 40 and 60%, respectively. The goal of this research project was to present a systematic study of the HC process focusing on the increase in the naphthalene content of creosote oil to improve its overall value in an efficient and economical manner.

Experimental Section

Properties of the Creosote Oil Sample

The creosote oil sample from coal tar was a mixture of fractions collected over a range of boiling points from 218 to 340 °C, whose major components were bicyclic or tricyclic aromatic hydrocarbons. The creosote oil was supplied by Xinlian coal chemical company, Xinjiang, China. Table lists the boiling points and the relative ratios of the components in the oil sample, which had an initial naphthalene content of 10.42%.
Table 1

Properties and Relative Content of the Components in the Oil Sample

no.componentsretention time (min)boiling point (°C)relative content (%)
1naphthalene19.00421810.42
2quinoline19.9672372.54
32-methyl-naphthalene21.04724122.25
41-methyl-naphthalene21.3652469.62
5biphenyl22.4112565.18
61,7-dimethyl-naphthalene22.8942632.80
71,6-dimethyl-naphthalene23.148265–2663.92
8acenaphthene24.33727815.98
9dibenzofuran24.81428710.57
10fluorene25.8612938.90
11phenanthrene28.8753407.81

Experimental Setup

The HC setup used in these experiments is shown schematically in Figure , which comprised of a cavitator, gear pump, pipe, and vertical tank with a height of 500 mm and a diameter (D) of 132 mm. The cavitator was tubular with a length (L) of 150 mm and a diameter (d1) of 30 mm, which was fitted with a venture tube that contained a throat with a diameter (d2) of 18 mm. It contained two orifice plates that were 5 mm thick, with diameters of 30 mm, which contained eight holes of 2 mm diameter (d3). The cavitator was fitted with an upstream pressure gauge and a turbine flowmeter to monitor the stability and flow rates of the reaction. A bimetallic thermometer in the tank functioned to determine the reaction temperature, which was cooled to −15 °C to reduce the rate of reaction and prolong the reaction time (Figure ).
Figure 1

Schematic representation of the hydrodynamic cavitation reactor setup.

Figure 2

Schematic representation of the cavitating device.

Schematic representation of the hydrodynamic cavitation reactor setup. Schematic representation of the cavitating device.

Choice of Inducing Agent

Previous work has shown that inducers can have a significant influence on the outcome of the HC treatments of creosote oil.[9] For example, Fe2+ ions have been used as an inducer to produce H• radicals that react with naphthalene, 1-methyl-naphthalene, 1,7-dimethyl-naphthalene, dibenzofuran, and phenanthrene to selectively produce acenaphthene. In this work, Ni2+, Co2+, (Mo7O24)6–, and 1:1 mixtures of Ni2+/Mo6+ salts were screened as potential inducers.

Analysis and Preparation of Feedstock

A Karl–Fischer moisture meter was used to determine the water content of the samples. NiSO4·6H2O (0.8% (V/V)), CoSO4·6H2O, (NH4)6Mo7O24·4H2O, or FeSO4·7H2O were weighed in accordance with the amount of Ni2+, Co2+, (Mo7O24)6–, or Fe2+ required, respectively. The NiSO4 solutions were prepared by dissolving NiSO4 in water, and H2SO4 (1 M) was used to adjust the pH of solutions to the desired value before they were mixed with oil samples.

Experimental Process and Sample Analysis

Experiments were carried out using natural cooling, external cooling from the start of the reaction, or external cooling to keep the reaction temperature below 30 °C, respectively. Figure shows the conversion rates for the three different temperature conditions over time, with external cooling resulting in longer reaction times (see Table ). The circulation of the feedstock was driven by a gear pump until the reaction was complete, with the feedstock then transferred to a tank and cooled to 0 °C through the action of a cooling trap under an upstream pressure at 2.6 MPa with an immersion height of the cavitator being 105 mm. A control experiment revealed that no change in the composition of the oil samples occurred in the absence of ultrasonic agitation.
Figure 3

Temperature curve with the time of cavitation under different types of cooling.

Table 2

Temperature Rates by Piecewise Regression

curvetime (min)functionR2function
(A)≤3T = 13t + 140.99heating
3–10T = 4.3t + 370.99reacting
(B)≤3T = 5.5t + 140.99heating
3–10T = 4.1t + 190.99reacting
10–16T = 2.65t + 330.99
(C)≤3T = 15t + 20.94heating
3–10T = 3.2t + 300.97reacting
10–32T = 0.7t + 540.98
Temperature curve with the time of cavitation under different types of cooling. Oil samples were withdrawn from the reaction mixture and cooled to ambient temperature before their composition was determined by gas chromatography (GC) (GC-MS 2010, Shimadzu Corporation, Japan) analysis. The GC conditions using the following conditions: injection port at 280 °C and detector at 250 °C, the initial temperature of 50 °C for 1 min, followed by an increase to a maximum temperature of 280 °C at the rate of 8 °C/min. The elastic quartz capillary column was HB-5 with a neutral phase (60 m × 0.25 mm × 0.25 μm); other experimental details were identical to those reported previously.[9]

Results and Discussion

Hydraulic Features

The ratio (β) of the total flow area through the holes of the orifice (AN) to the upstream pipe surface (AP) can be written as follows According to the distributions along fraction for water at 25 °C in the hydrodynamically cavitation flow field have been simulated with the help with the directions of axial and radial of pressure, velocity and vapor volume of κ-ε model in the computational fluid dynamic (CFD) (see Figure ). The results of these modeling studies for section S1–1 are shown in Figure a–c, with cylindrical coordinates established with reference to the center of the cavitator, and the quotient r/r0 defined as a normalized radius.
Figure 4

CFD simulation diagrams of cavitator. (a) Pressure distribution in cavitator, (b) water velocity at 25 °C, and (c) water vapor volume fraction at 25 °C.

CFD simulation diagrams of cavitator. (a) Pressure distribution in cavitator, (b) water velocity at 25 °C, and (c) water vapor volume fraction at 25 °C. Figure a shows that the pressure distribution reduced from 2.6 to 0 MPa along the axial direction, with the pressure reducing from 2.6 to 1.7MPa as the suspension flowed through the first orifice and from 1.7 to 0 MPa as the suspension flowed through the second orifice. After section S1–1 the pressure was 0.04 MPa for an r/r0 of 0 to 0.6, increasing to 0.76 MPa for a r/r0 of 0.6–1 in a radial direction. Figure b reveals that the water velocity reached the maximum value of 50.94 m/s within the holes of orifice 2. The velocity increases from 0.031 to 17.0 m/s flowing through the first orifice to 40.3 m/s near the wall through the second orifice in an axial direction. After the second orifice, the velocity increases in turn with the radial direction from 0.031 to 12.76 m/s for r/r0 = 0 to 0.4; from 19.12 to 33.97 m/s for r/r0 = 0.4 to 0.6, and from 36.08 to 40.33 m/s for r/r0 = 0.6 to 1. Figure c shows that the S1–1 vaporization section reaches a maximum value of 98.7% at r/r0 = 0 and then reduces from 98.7 to 0% for r/r0 equal to 1. Hydraulic characteristics of the cavitator were calculated from the cavitation number (Cv), which is a dimensionless number that describes the cavitation efficiency in hydraulic devices.[10−12] This number is obtained using the following equationwhere p2 is the fully recovered downstream pressure, pv is the saturated vapor pressure of the water at 0.0385 MPa, v0 is the water velocity as it exits orifice 2, and ρ is the water density of 924 kg/m3. Figure shows the effect of r/r0 and the cavitation number (Cv) on the downstream pressure (Figure a), water velocity (Figure b), and water vapor volume (Figure c) values at orifice 2, respectively. These results reveal that larger r/r0 values lead to increased pressures and water velocities while the water vapor volume fraction decreased with an increase in r/r0. Changes in the cavitation number follow an upward parabolic curve with increasing r/r0, with a minimum value of 0.2 at r/r0 = 0.7 visible in Figure a–c. Cavities were only produced in large numbers when Cv ≤ 1; therefore, effective cavitation is only produced for r/r0 values ranging from 0.24 to 1 in this device.
Figure 5

Relationship among r/r0 of cavitator, cavitation number (Cv) and downstream pressure (a), water velocity (b), and water vapor volume (c) after orifice 2, respectively.

Relationship among r/r0 of cavitator, cavitation number (Cv) and downstream pressure (a), water velocity (b), and water vapor volume (c) after orifice 2, respectively.

Effect of H2O Content on Product Distribution

The effect of water on the amount of naphthalene content produced in the cavitation process was explored by conducting experiments with 5, 7, 10, and 15% water content (see Figure ), which revealed a maximum 5.77% increase in naphthalene for the water content of 10%. The ultrasonic cavitation of water in the system results in its homolytic cleavage to afford hydrogen and hydroxyl radicals (e.g., H2O → H• + HO•),[13] with the biphasic reaction being efficiently mixed to form an emulsified colloidal system as it flows through the cavitator. The relatively high boiling range of 218–340 °C of the aromatics (see Table ) in the cavitator means that a highly emulsified and dispersed colloidal water/oil (W/O) and vapor/liquid (V/L) systems are generated. The vaporization rate of water in the cavitator exceeds 98% at 25 °C, meaning that all of the water in the material is essentially vaporized, which results in an increase in pressure when the oil feedstock meets the swirling interface that results in all of the vapor bubbles rapidly collapsing under such high pressure.[14]
Figure 6

Effect of the initiator H2O amount on the component content change of product.

Effect of the initiator H2O amount on the component content change of product. This results in very strong shock waves and microjets being produced, which provide sufficient energy to the system for the aromatic components to be equilibrated to produce a greater proportion of lower-energy aromatics.[15] The sonication process produces shock waves reaching 140–170 MPa with a frequency of 100–1000 Hz, which results in the homolytic dissociation of H2O and O2, which produces highly active H•, HO•, and O• radicals, respectively. The impact energy depends on the literature.[16] There is almost no heat transmission resistance or mass transfer resistance when the bubbles collapse;[17] however, bubble collapse promoted a more intense contact between the oil components and H•, HO•, and O• radicals to promote the overall reactivity of the system.[18,19]

Effect of the Reaction Time on Naphthalene Yield

Monitoring the cavitation reaction of creosote under constant conditions over time (10–90 min) revealed that the maximum yield of naphthalene obtained was 5.77%, when the reaction time crossed 32 min, with its yield then declining slowly over the next 60 min. The maximally increased phenanthrene was 2.60 after 60 min, with its yield then declining slowly over the next 30 min (see Figure ). Because the reaction to produce phenanthrene needs more energy than that to produce naphthalene. Therefore, there is a need for a longer reaction time.
Figure 7

Effect of reaction time on the component content change of product.

Effect of reaction time on the component content change of product.

Effect of the Inducing Agents

The effect of using different inducing agents (at a 0.3% level) in the ultrasonic reactions of creosote oil was investigated using 10% H2O, 10% at an operating temperature of 75 °C (see Figure ).
Figure 8

Effect of different inducing agents on the component content change of product.

Effect of different inducing agents on the component content change of product. Similar product profiles over time were observed for Co2+, [Mo7O24]6–, and Ni/Mo = 1:1 and Ni2+ catalysts (e.g., increased naphthalene and phenanthrene content), which were different from those obtained by the use of Fe2+ catalysts (e.g., increased acenaphthalene content). When Ni2+, Co2+, [Mo7O24]6–, and Ni/Mo = 1:1 were used as inducers, the contents of naphthalene, 1-methyl-naphthalene, and phenanthrene in creosote were found to increase, whereas the amounts of 2-methyl-naphthalene, acenaphthene, dibenzofuran, and fluorene were decreased. The greatest increase in the naphthalene content of 6.17 percentage points was achieved when Ni2+ was used as an inducer, with the naphthalene yield using Ni2+ > [Mo7O24]6– > Ni/Mo = 1:1 > Co2+. The result of Fe2+ as the inducer has been published by our team in the previous work.[11] The reason for this result might be that Ni2+, Co2+, [Mo7O24]6–, and Ni/Mo = 1:1 were inducers of common hydrogenation. However, Fe2+ might react with HO• under these conditions, which was the Fenton reaction; therefore, more strong oxidizing free radicals were released. In ref (8), the acenaphthalene content of Fe2+ is increased at 75 °C. However, the naphthalene yield of Fe2+ is relatively increased at 90 °C and that of acenaphthalene decreased. The results of the two experiments were that the methyl metathesis reactions of the aromatic components occurred under thermodynamic control, except that the rate of the Ni2+ reaction was faster than that of the Fe2+ reaction. Therefore, although neither reaction fully reached an equilibrium, the Ni2+ reaction with more naphthalene and phenanthrene (stable) is closer to equilibrium than the Fe2+ reaction that contains more acenaphthalene (less stable). Neither reaction reached a full equilibrium, which is why the naphthalene intermediate reacts further for extended reaction times.

Effect of Ni2+ Dosage

The effect of varying amounts of Ni2+ as an inducer was investigated over a range from 0 to 0.6 (wt %) using 10% H2O at 75 °C, with an optimal loading of Ni2+ of 0.3% (see Figure ). When Ni2+ was higher than 0.3%, the surface tension increased. The largest surface tension caused the number of cavitation bubbles produced by cavitation to decrease, but the size of the grown bubble was increased and the energy released by the bubble collapse was enhanced.
Figure 9

Effect of the amount of inducer of Ni2+ on the change in naphthalene.

Effect of the amount of inducer of Ni2+ on the change in naphthalene.

Effect of pH of NiSO4 Solution

pH effects were explored over a range from 1.0 to 6.0 using H2SO4 (1 M) to adjust the pH levels, with a maximum increase in naphthalene content observed at pH 4.0, which is consistent with the hydroxyl radicals being produced by ultrasonication under acidic conditions (see Figure ). For example, Patil and Gogate[20] have reported that the HC degradation of aqueous solutions of methyl parathion was greatest at a pH value of 3, while Shriwas and Gogate[21] reported that its ultrasonic degradation rate was fastest at pH 2.5. A decrease in pH will promote ultrasonication-mediated homolytic dissociation of water into HO• and H• during the cavitation process, while an acidic environment will promote the formation of more stable oilwater emulsions that will enhance the mass transfer effects and increase the reaction rates. The stability of the emulsions isolated from these cavitation reactions increased significantly at lower pH, with emulsions observed to be stable for more than 30 days at pH ≤4 (see Figure ).
Figure 10

Content change of naphthalene with different pH of NiSO4 solution of the product.

Figure 11

Emulsion stability time with different pH after cavitation.

Content change of naphthalene with different pH of NiSO4 solution of the product. Emulsion stability time with different pH after cavitation.

Effect of Operating Temperature

The effect of temperature on naphthalene content was studied at different temperatures (60, 65, 70, 75, 80, and 95 °C) using 0.3% Ni2+ as inducer and H2O 10% at pH 4.0, which revealed that maximal naphthalene (7.33%) and phenanthrene (2.6%) content was produced between 75 and 80 °C (see Figure ). HC processes used for chemical modification normally have an optimal reaction temperature,[22] with gas solubilities generally decreasing as the temperature increases, which can result in reduced cavitation in the vaporization core of the ultrasonic process. Furthermore, an increase in the vapor pressure of liquid enhances evaporation but can weaken cavity collapse, with reductions in liquid viscosity leading to a decline in the disturbance and the rate of cavity collapse.[23]
Figure 12

Effect of operating temperature on the component content change of the product.

Effect of operating temperature on the component content change of the product.

Reaction Mechanism and Products Formed in the HC Reaction

Optimal conditions for the ultrasonication of the creosote oil were established based on the use of an upstream pressure at 2.6 MPa, an immersion height at 105 mm, use of 0.3% Ni2+ as an inducer, 10% H2O at pH 4.0, and an operating temperature of 75 °C. This reaction resulted in an increase in the amount of naphthalene present by 7.14% and an increase in phenanthrene content by 2.63% (see Table ), which is consistent with the series of radical chain reactions shown in Figure .
Table 3

Material Balance Values of the Radical Reactions, Measured Values, and Comparison of Both

no. of reactionreactantsreduce percentage points (w)productsP/R molecular weight ratiobalance value∑ balance valueincrease percentage points (w)relative error (%)
(2)2-methyl-naphthalene4.47naphthalene0.9014.037.147.332.59
1,6-dimethyl-naphthalene1.040.9000.94
acenaphthene2.610.8312.17
(3)dibenzofuran0.48phenanthrene1.0600.512.632.640.38
(4)fluorene1.981.0722.12
Figure 13

Reaction mechanism of creosote oil by hydrodynamic cavitation.

Reaction mechanism of creosote oil by hydrodynamic cavitation.

Evidence for the Production of HO• Radicals in the Hydrodynamic Sonication Reactions

The cavitation conditions induce homolytic cleavage of water to produce highly reactive H• and HO• radical reactions that are responsible for reforming the aromatic substrates in the colloidal oilwater mixture (see Figure ).[24] To verify the proposed mechanism, a solution of methyl violet (MV) (0.02 mmol/L) was sonicated in the cavitator system at rt for 13 min, which resulted in a final solution temperature of 60 °C. The absorption peak at a wavelength of 583 nm was found to decrease from 0.892 at the start of the reaction to 0.354 after cavitation, consistent with the HO• radicals reacting with methyl viologen to produce products with lower absorption values[25] (see Figure ).
Figure 14

UV of methyl violet solution before and after the cavitation.

UV of methyl violet solution before and after the cavitation.

Calculations of Bond Dissociation Energies of Water and Aromatic Compounds

Based on the reaction mechanism proposed in Figure , the bond dissociation energies of HO–H, C6H5–OH, C6H5–H, C10H7–H, C6H5–CH3, and C10H7–CH3 were computed using a B3LYP/6 density functional level, the results of which are shown in Table . The energy of the dissociation of H2O into H• and HO• was calculated as 497.1 kJ/mol, which was in good agreement with the previously reported value of 499.0 kJ/mol.[26] The bond dissociation energies calculated for C6H5–OH was 487.5 kJ/ mol, while C10H7–H and C6H5–H were both 473.3 kJ/mol and C10H7–CH3 and C6H5–CH3 were both 449.0 kJ/mol, respectively. These bond dissociation energy values were all less than the corresponding bond dissociation energies of H2O, so it is clear that cavitation provides enough energy for homolytic cleavage of the O–H and C–H bonds of these aromatic compounds to occur.
Table 4

Bonds Dissociation Energies for Six Molecule Models

Conclusions

Hydrodynamic cavitation (HC) of aromatic hydrocarbons present in creosote oil obtained from coal tar in the presence of 0.3% (w/w) Ni2+ as inducer increases its naphthalene and phenanthrene content by 7.7 and 2.6%, respectively. The following conclusions can be drawn to explain the increase in naphthalene content: Cavitation processes result in H2O being homolytically cleaved into HO• and H• radicals that combine with Ni2+ species to facilitate demethylation of methyl-naphthyl naphthalene species by hydrogen radicals to afford naphthalene. A 7.33% increase in the naphthalene content (70% increase overall) of creosote oil has been achieved through its ultrasonication in the presence of 0.3% NiSO4 and 10% H2O (pH 4.0) at 75 °C. Evidence that the ultrasonication-mediated homolytic cleavage of water to generate hydrogen and hydroxy radicals was achieved using methyl viologen as a control substrate that was shown to rapidly decompose under the cavitation conditions. The dissociation energies of water and six models of aromatic compounds were computed at a B3LYP/6 level, with the bond dissociation energies of the five aromatic compounds found to be less than that of the corresponding HO–H dissociation energy of H2O. This indicates that radical processes are likely to be responsible for the observed changes in aromatic content. Switching the initiator used in the ultrasonic reactions of creosote oil from Fe2+ to Ni2+ results in a change in product enrichment from acenaphthalene to naphthalene and phenanthrene.
  10 in total

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Journal:  Bull Environ Contam Toxicol       Date:  2008-04-04       Impact factor: 2.151

4.  Synergetic pretreatment of waste activated sludge by hydrodynamic cavitation combined with Fenton reaction for enhanced dewatering.

Authors:  Meiqiang Cai; Jianqiang Hu; Guanghu Lian; Ruiyang Xiao; Zhijun Song; Micong Jin; Chunying Dong; Quanyuan Wang; Dewen Luo; Zongsu Wei
Journal:  Ultrason Sonochem       Date:  2017-12-02       Impact factor: 7.491

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Authors:  Grzegorz Boczkaj; Michał Gągol; Marek Klein; Andrzej Przyjazny
Journal:  Ultrason Sonochem       Date:  2017-09-15       Impact factor: 7.491

6.  Decolorization of azo dyes Orange G using hydrodynamic cavitation coupled with heterogeneous Fenton process.

Authors:  Meiqiang Cai; Jie Su; Yizu Zhu; Xiaoqing Wei; Micong Jin; Haojie Zhang; Chunying Dong; Zongsu Wei
Journal:  Ultrason Sonochem       Date:  2015-08-06       Impact factor: 7.491

7.  Degradation of organic wastewater by hydrodynamic cavitation combined with acoustic cavitation.

Authors:  Chunhai Yi; Qianqian Lu; Yun Wang; Yixuan Wang; Bolun Yang
Journal:  Ultrason Sonochem       Date:  2018-01-11       Impact factor: 7.491

8.  The energy efficiency of formation of photons, radicals and ions during single-bubble cavitation.

Authors:  Yuri T Didenko; Kenneth S Suslick
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Authors:  Zhilin Wu; Haifeng Shen; Bernd Ondruschka; Yongchun Zhang; Weimin Wang; David H Bremner
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10.  Wastewater treatment: a novel energy efficient hydrodynamic cavitational technique.

Authors:  Manickam Sivakumar; Aniruddha B Pandit
Journal:  Ultrason Sonochem       Date:  2002-07       Impact factor: 7.491

  10 in total

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