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. 2021 Jan 22;73:105469. doi: 10.1016/j.ultsonch.2021.105469

Acoustic cavitation events and solvation power of ionic liquid in a novel hybrid technique: A concept proposal toward a green pathway for cellulose decomposition

Kaouther Kerboua a,, Oualid Hamdaoui b,, Abdulaziz Alghyamah b
PMCID: PMC7848641  PMID: 33524725

Highlights

  • A novel US/ILs hybrid concept is investigated numerically toward cellulose decomposition.

  • Acoustic cavitation threshold is higher in terms of power in the ionic liquid.

  • The oscillation dynamics is limited by the viscosity of [C4mim][CH3COO].

  • The temperature in the boundary layer attains 1000 K at the mid-width.

  • High cellulose decomposition and anhydrocellulose emergence rates are recorded.

Keywords: Hybridization, Ionic liquid, Solubility, Sonication, Acoustic cavitation, Cellulose decomposition

Abstract

The present paper reports a numerical investigation of the feasibility of a hybrid concept associating the 1-Butyl-3-methylimidazolium Acetate [C4mim][CH3COO] to sonication, in terms of cavitation formation and generated extreme conditions allowing cellulose decomposition in the second reactivity site. The results of the proposed model revealed an acoustic power threshold of 1.8 atm, in order to expect a transient cavitation in the ionic liquid, leading to harsh conditions of 1559.8 K and 49 bar within the bulk volume of the acoustic cavitation bubble. The spatial and temporal variation of the temperature was simulated within the bulk volume of the bubble as well as in the thermal boundary layer jointly with the chemical kinetics. The first stage of the polymerization reduction was clearly attained and demonstrated through the decomposition rate of cellulose and the molar rate of emergence of anhydrocellulose, reaching the respective orders of magnitude of 1.71 × 104 mol/m3⋅s and 7.91 × 104 mol/m3⋅s.

Nomenclature

Greek symbols

ξ

Thermal layer width (m)

λ

Thermal conductivity (W/m⋅K)

ϑki

Stoichiometric coefficient related to the kth species in the ith reaction in the left side of the chemical reaction

ϑ'ki

Stoichiometric coefficient related to the kth species in the ith reaction in the right side of the chemical reaction

ρL

Density of liquid (kg/m3)

σ

Surface tension (N/m)

μ

Dynamic viscosity (Pa⋅s)

Latin symbols

Ai

Pre-exponential factor (m3/mol.s) for two body reaction and (m6/mol2⋅s) for a three-body reaction

c

Sound celerity (m/s)

ck

Molar concentration of the kth species within the single acoustic cavitation bubble (mol/m3)

c0

Initial concentration (mol/m3)

Ei

Activation energy (J/mol)

f

Frequency (Hz)

n

Total molar yield (mol)

nk

Molar yield of the kth species within the single acoustic cavitation bubble (mol)

n0

Initial molar yield (mol)

PA

Acoustic amplitude (Pa)

Pi

Partial pressure (Pa)

Pg

Pressure of gas (Pa)

Pg0

Initial pressure of gases (Pa)

Pv

Saturating pressure (Pa)

P

Ambient pressure (Pa)

R

Bubble radius (m)

R˙

Bubble wall velocity (m/s)

R¨

Bubble wall acceleration (m/s2)

Rg

Ideal gas constant (J/mol⋅K)

R0

Initial bubble radius (m)

T

Temperature within the bubble (K)

Ti

Median temperature in the thermal boundary layer (K)

T0

Initial bulk temperature (K)

t

Time (s)

T

Ambient temperature (K)

V

Volume of the bubble (m3)

Vi

Volume of the thermal boundary layer (m3)

Subscript

k

Refers to the kth species

i

Refers to the ith reaction

1. Introduction

Cellulose is the most abundant natural polysaccharide, it constitutes the major proportion of biomass material and forms the framework of its cell walls [1]. Structurally speaking, cellulose is formed from repetitive D-glucose units, which are linked through β (1 → 4)-glycosidic bonds [2]. It has crystalline and amorphous zones according to whether the microfibrils are periodically or randomly distributed along the orientation of cellulose fibrils [3], [4].

Owing to its exceptional structural and physical properties, but also its biocompatibility, biodegradability, thermal and chemical stability, cellulose and its derivatives have nowadays a large scope of applications in polymer, paper and paints industries [5]. Solvents are usually needed for the dissolution of cellulose in order to enable homogeneous phase reactions without prior derivatization. However, the multiple extensive intra and inter molecular hydrogen bonding interactions within the cellulose structure result in a semicrystalline polymer containing highly structured crystalline regions, which induces its high tensile strength [6]. Thus, cellulose is insoluble in water and most common organic solvents [7]. The few solvents which are classically used, such as carbon disulfide and phosphoric acid, pose serious environmental issues with fatal drawbacks. For instance, the Kraft process, which produces viscose rayon from cellulose xanthate and carbon disulfide, requires high temperature, pH control, and results in the release of organic sulfur in water and presents a risk of the lignin and hemicellulose destruction during the separation and purification of the biomass [8]. Hence, more benign strategies are needed, by excluding the utilization of toxic and non-recyclable chemicals and substituting them by environmental-friendly and more efficient solvents.

Swatloski et al. [9] first discovered the ability of some ionic liquids to dissolve cellulose. They demonstrated that ionic liquid, as a non-derivatizing solvent, strongly dissolve cellulose by disrupting and breaking the intramolecular hydrogen-bonding network. Ionic liquids have emerged afterwards as effective and green solvents [5], [10], [11], mainly due to their high thermal and chemical stability, nonflammable nature and miscibility with many other solvent systems [12].

The dissolution of cellulose in ionic liquid was described by several authors who presented various mechanistic explanations. Most of them agreed that cellulose was dissolved when anions formed hydrogen bonds with the cellulose [13], while some others demonstrated that dissolution of cellulose in the ionic liquids occurs when the anion and cation form hydrogen bonds with the cellulose’s hydrogen and oxygen atoms, mainly taking place between C6 and C3 hydroxyl groups of neighborhood cellulose chain [14]. These mechanisms are coherent with the findings of Swatloski et al. [9] who demonstrated that the presence of water in the ionic liquid, even in a small proportion of 1% wt., significantly decreases the solubility of cellulose, presumably through competitive hydrogen-bonding to the cellulose microfibrils, which inhibits solubilization.

Among the ionic liquids known nowadays, the Acetate-based ILs, such as the 1-Butyl-3-methylimidazolium Acetate, are supposed to form N-heterocyclic carbine ligands, which makes possible the ring opening reaction leading to the formation of covalent bonds between cellulose and imidazolium core [1]. The 1-Butyl-3-methylimidazolium Acetate [C4mim][CH3COO] is indeed one of the most powerful solvents of cellulose according to several studies [6], [14], [15] and particularly offers high dissolution rates at near room temperature, it displayed for instance 23 g/mol solubility at 40 °C [10].

Most of experiments of cellulose dissolution in ILs aim to disrupt its highly crystalline structure, reduce its degree of polymerization, and enlarge the surface of the substrate which is accessible for further reaction such as lysis, making it more susceptible to transform into less complex units. Most of the reactions following the dissolution are of enzymatic [16] or catalytic [17] nature. However, it is important to mention that cellulose is known to thermally decompose into tar, char and gases [2], [18] as proven in cellulose pyrolysis studies. Interestingly, sonication, through the acoustic cavitation phenomenon [19], is susceptible to reproduce pyrolysis conditions in a wide range of applications such as aromatic and naphthenic hydrocarbons [20] and methanol decomposition [21]. In case of cellulose, most of researches associating the dissolution in ILs and the sonication are about harnessing the physical effects of ultrasound rather than the chemical ones. To illustrate, Liu et al. [22] attributed the improvement in the dissolution of cellulose in 1-allyl-3-methylimidazolium when submitted to sonication to the enhanced diffusion of the ionic liquid into the structure of the dissolved samples. Grabber et al. [23] reported the combination of ball-milling and ultrasound for dissolution of holocellulose in 1-n-butyl-3-methylimidazolium chloride, they demonstrated seven fold reduction in dissolution time with no changes in the chemical structure of the holocellulose. Both examples relied on the physical effects of ultrasound and showed no sign of “hot spot” effects induced by sonication, nevertheless, some other researches exhibited chemical changes in the dissolved cellulose following sonication. Lan et al. [24] reported for instance an FTIR peak from anti-symmetric stretching of carboxylic anions after exposing cellulose dissolved in 1-n-butyl-3-methylimidazolium chloride to ultrasounds. This observation indicates that ultrasound with high power (75 W in this case) may result in the oxidative degradation of cellulose dissolved in ILs that actually refers to the occurrence of “hot spot” events and thermal effects of acoustic cavitation, which triggered us to investigate numerically the occurrence of the sonolytic cellulose oxidative decomposition when dissolved in IL. The present paper proposes a novel hybrid concept which takes benefit of the solvation power of [C4mim][CH3COO] toward cellulose and the thermal effects induced by the acoustic cavitation bubble evolving in the ionic liquid, and examines the opportunity to thermally decompose the dissolved cellulose using ultrasound. The hybrid concept US/IL is approached numerically through the modeling of the single acoustic cavitation bubble oscillating in [C4mim][CH3COO] after the selection of appropriate acoustic conditions leading to the hot spot event. The effect on cellulose chemical structure is then investigated through the modeling of the kinetics evolving around the oscillating bubble, in respect to the two-site model of sonochemical reactivity [25]. The results of the present numerical investigation would initiate a novel conceptualization of the thermal decomposition of cellulose using ultrasound, based on the solvation power of ILs, which would suggest a practical alternative to severe temperature conditions and hazardous solvents used in conventional processes of cellulose decomposition.

2. Theoretical approach

In the present model, the 1-Butyl-3-methylimidazolium Acetate [C4min][CH3COO] was selected among the ionic liquids for its high cellulose solvation power [6], [10]. The ionic liquid [C4min][CH3OO] is supposed saturated with argon, and though very few studies dealt with the solubility of argon in ionic liquids [26], [27], [28], [29], the reported solubility rates are considered acceptable to create gaseous inclusions and induce acoustic cavitation when sufficient tensile strength is applied [30]. The main novelty of the model lies in the fact that it allows both the determination of adequate ultrasonic conditions conducting to hot spot occurrence in [C4min][CH3OO] and the examination of the chemical kinetics of decomposition of dissolved cellulose at the thermal boundary layer of acoustic cavitation bubble.

The ionic liquid is irradiated with an ultrasonic wave of a frequency of 200 kHz and an amplitude of 1.8 atm. This acoustic amplitude was selected after preliminary simulations which allowed the determination of the lowest acoustic amplitude and operating temperature permitting the achievement of the acoustic cavitation phenomenon and the expected chemical effects. The argon gaseous inclusions are responsible of heterogeneous nucleation giving rise for single bubbles of 5 µm of ambient radius. Each bubble oscillates according to the Keller-Miksis equation expressed in Eq. 1.

R¨=c+R˙ρLcR-R˙R+4μPg-26R-4μR˙R-P+Pasin2πft+Rc+RρLcR-R˙R+4μPg˙+26R˙R2+4μR˙2R2-ρL3c-R˙R˙22ρLcR-RR˙+4μ (1)

The operating temperature is set to 353 K in order to attain an acceptable value of dynamic viscosity of the ionic liquid. The physical properties of the 1-Butyl-3-methylimidazolium Acetate are given in function of temperature by Safarov et al. [31], we report on Table 1 the surface tension σ, the dynamic viscosity μ, the density ρL and the celerity of sound c at 353 K.

Table 1.

The physical properties of 1-Butyl-3-methylimidazolium Acetate at 353 K.

Properties σ(mN/m) ρL(kg/m3) μ(mPa⋅s) c(m/s)
Values 36 1019.28 24.4 1521.92

The vapor pressure of the 1-Butyl-3-methylimidazolium Acetate is negligible [32], thus, the bubble content is only due to the presence of argon. The initial pressure of gas inside the bubble is given by Eq. 2 , in accordance with the mechanical equilibrium.

Pg0=P+2σR0 (2)

The energy balance applied to the single acoustic cavitation bubble during its oscillation is expressed in Eq. 3.

T˙=1nCV(T)(-Pg4πR2R˙-φ(t)) (3)

φ(t) represents the heat flow across the thermal boundary layer of width ξ, its expression relies on the continuity of the thermal flow across the bubble interface at each instant t.

φ(t)=4πRR-ξξTT(t)λ(T)dT (4)

In Eqs. 3 and 4, CV(T) and λ(T) represent, respectively, the isochoric molar heat capacity and the thermal conductivity of argon, varying in function of the temperature. Both are given as polynomial functions as indicated in Ref. [33].

The pressure of gases inside the bubble volume is simply deduced using the Van der Waals state equation as indicated below.

Pg+n2aV2V-nb=nRgT (5)

The width of the thermal boundary layer ξ is situated in the gaseous side owing to the order of magnitude of the thermal conductivity of the ionic liquid [34], [35], almost 10 times higher than that of argon. The resistance to thermal diffusion is then deemed concentrated in the gaseous side and consequently, the boundary layer of thermal diffusion is considered there. The width ξ is given by Eq. 6 [36].

ξ=minRκR˙,Rπ (6)

In this equation, κ represents the thermal diffusivity, which depends of the density, heat capacity and thermal conductivity of argon and is consequently temperature dependent.

The resolution of Eq. 3 allows the determination of the temperature in the bulk volume of the single acoustic cavitation bubble. The temperature is assumed to be spatially uniform within this volume except for the thin boundary layer of the width ξ [37]. The radial distribution of the temperature across the thermal boundary layer is determined by resolving for each value of r, comprised between 0 and ξ, the Eq. 7, resulting of the integration of Eq. 4 with the polynomial form of λT, and giving the value of T(R-r).

1.79435×105TR-r2+6.81277×10-3TR-r-4.6408=rφt4πRR-r (7)

According to the two-site model [38], the thermal boundary layer constitutes the seat of chemical reactions due to the thermal effect induced by the hot spots at the bubble interface. When the bulk temperature is high enough, the surrounding temperature is sufficient to initiate pyrolysis reactions, the cellulose is expected to thermally decompose according to the mechanism proposed by Diebold [39] and presented in Table 2.

Table 2.

Mechanism of the thermal decomposition of cellulose.

Reaction Pre-exponential constant (s−1) Activation energy (kJ/mol)
Cellulose  H2O + char 6.7 × 105 110
Cellulose  Active cellulose 2.8 × 1019 240
Active cellulose  Primary vapors 6.79 × 109 140
Active cellulose  H2O + char 1.3 × 1010 150
Active cellulose  Secondary gases 3.6 × 1011 200
Primary vapors  Secondary gases 3.6 × 1011 200
Primary vapors  Secondary tars 1.8 × 103 61

Owing to the chemical inertia of the bubble content, the sonochemical kinetics is attributed to the thermal effect generated inside the thermal boundary layer, i.e., the second reactivity site. The chemical kinetics taking place there is modeled according to Table 2 as a chain mechanism of first order reactions, where the molar yield of each species k is governed by Eq. 8.

dnkdt=Vri=17(ϑ'ki-ϑki)Aie-EiRgTrk=1Kckϑki (8)

In this equation, Tr represents the effective temperature affecting the chemical kinetics of cellulose decomposition, and since it is spatially evolving in function of r, as shown in Eq. 7, the median value is considered to approximate the conditions of the thermal decomposition of cellulose. The molar concentrations ck of each species k are reported to the boundary layer volume Vr given in Eq. 9.

Vr=43πR3-R-minRκR˙,Rπ3 (9)

The system of non-linear and dependent differential equations composed of Eqs. 1, 3 and 8 is simultaneously resolved with the non-linear equations 4, 5, 6, 7 and 9 using appropriate numerical algorithms, and accounting for the initial conditions reported in Table 3.

Table 3.

Initial conditions adopted in the studied system.

Parameter R0 R˙0 n0(Argon) c0(Cellulose) Pg0 T0
Value 5 µm 0 m/s 2.064 × 10−14 mol 1 mM 115700 Pa 353 K

3. Results and discussion

The simulation of the dynamics of bubble oscillation in the 1-Butyl-3-methylimidazolium Acetate was preceded by several preliminary trials under an acoustic frequency of 200 kHz. These preliminary simulations were conducted by incrementing the acoustic amplitude from an initial value of 1.2 atm, with a step of 0.1 atm, until reaching the lowest acoustic amplitude allowing the achievement of a nonlinear bubble oscillation with a subsequent violent collapse and abrupt increase in temperature and pressure of the gaseous phase inside the bubble volume. The initial acoustic amplitude, i.e. 1.2 atm, was selected as a minimum value that slightly exceeds the pressure to which the ionic liquid is submitted, i.e. 1 atm, and hence is susceptible to break the liquid molecules cohesion in the presence of liquid germs, and lead to the apparition of non-linear oscillation of the bubble as indicated by the Blake Threshold [40]. The step 0.1 atm was set in order to obtain a reasonable balance of accuracy and number of iteration, until reaching the minimum acoustic pressure allowing the occurence of transient cavitation [41].

The harsh and abrupt increase of pressure and temperature inside the bubble was only achieved when reaching an acoustic amplitude of 1.8 atm, in fact, the high viscosity of the ionic liquid, almost 60 times higher than that of water, prevented any noticeable bubble dynamics when applying lower acoustic powers. This was highlighted by Hernoux-Villière et al. [42] who employed a low power ultrasonic bath to irradiate ionic liquid containing dissolved cellulose, they noticed the absence of even physical effects and explained their observation by the highly viscous system requiring intense acoustic power and direct sonication mode. Fig. 1 reports the oscillation dynamics results as well as the width of the thermal boundary layer evolving with the bubble oscillation.

Fig. 1.

Fig. 1

Evolution of the radius and the thermal boundary layer width (a) and the bubble wall velocity (b) of a single acoustic cavitation bubble oscillating in [C4mim][CH3COO] versus time under 1.8 atm and 200 kHz, during one acoustic cycle.

Fig. 1 (a) demonstrates that the bubble expansion leads to a maximum radius of 12.8 µm, i.e., 2.56-fold the initial radius, the abrupt collapse occurs afterwards at a velocity reaching 36.5 m/s toward the bubble center. The bubble contraction stops when the bubble radius attains 2.39 µm, a rebound is then observed at a velocity that suddenly reaches 20.04 m/s, as shown in Fig. 1(b). The compression ratio is estimated in this case at 5.36, this value is by far lower than the usual orders of magnitude reported for acoustic cavitation bubble oscillating in water [43]. However, since the studied system is completely different in terms of bubble content (no vapor, and only inert gas), the examination of the energy balance result is required to estimate the thermal outcome of the transient bubble oscillation, this is carried out in Fig. 2. In the other hand, the width of the thermal boundary layer, which is directly dependent of the bubble oscillation dynamics, reveals a slight variation around the strong collapse between the values 0.76 and 1.45 µm. This range is particularly important as it defines the volume of the second reacting site in the two-site model of sonochemical reactivity adopted in the present paper.

Fig. 2.

Fig. 2

Evolution of the temperature and pressure in the bulk volume of a single acoustic cavitation bubble (a) and the median temperature and thermal flow across its thermal boundary layer (b) versus time, when oscillating in [C4mim][CH3COO] under 1.8 atm and 200 kHz, during one acoustic cycle.

Fig. 2(a) reports both temperature and pressure evolution inside the bulk volume of the bubble, as announced previously, while Fig. 2(b) presents the thermal flow passing through the boundary layer and the resulting temperature value at the mid-width across this layer. Fig. 2(a) indicates that the maximum temperature attained within the bulk volume is 1559.8 K, while the maximum pressure does not exceed 49 bar. Looking to the few works that dealt with the modeling of the acoustic cavitation evolving in ionic liquids, we surprisingly notice divaricated orders of magnitude of pressure and temperature values reported in the bulk volume of the bubble. In an attempt to critically observe the obtained values, we suggest to closely inspect the physical properties and conditions of the considered (ionic liquid–gas) matrix. Kanthale et al. [44] presented a very interesting work measuring via the methyl radical recombination method the temperature of acoustic cavitation generated in the 1-Ethyl-3-methylimidazolium-ethyl sulfate (EMIS) using a plate transducer operating at 213 kHz and 40 W of acoustic power (measured calorimetrically). The authors noted that though acoustic cavitation in ionic liquid, being a nonvolatile liquid, is expected to generate a significantly higher temperature compared to that generated in water (or volatile solvents), the temperatures measured in pure EMIS were in the range of 3000–5000 K, thus, in the same order as those observed in volatile solvents. The most plausible explanation to such an observation is the weaker oscillation dynamics of acoustic cavitation bubbles, as shown in Fig. 1. Elder and Calvisi [45] developed a finite element model to describe the oscillation of an acoustic cavitation bubble in the 1-butyl-3-methylimidazolium tetrafluoroborate having a dynamic viscosity of 99.2 mPa⋅s at 293.15 K, which is the considered working temperature. They demonstrated that bubbles with bigger initial radius tend to reach higher temperatures and pressure when submitted to lower frequencies. Yet, the bubble equilibrium radius is hardly expected to attain values higher than in water, under similar acoustic conditions, owing to the high viscosity of the ionic liquid. When considering an acoustic frequency of 200 kHz and an equilibrium radius of 5 µm while adopting the conditions of Elder and Calvisi [45], the bulk and surface temperature and pressure are almost undetectable unless lowering the viscosity by increasing the operating temperature. If the dynamic viscosity is decreased below 10 mPa⋅s, Elder and Calvisi [45] report a bulk temperature exceeding 1200 K and a bulk pressure exceeding 12 bar. Overall, though transient cavitation can be formed in ionic liquid, the extreme collapse conditions are not as spectacular as in water; the viscosity of the ILs is the principal reason for this observation.

The temperature in thermal boundary layer is the most important parameter in the present study, since it defines the conditions within the second reactivity site and hence, the opportunity for cellulose to thermally decompose around the acoustic cavitation bubble. Fig. 2(b) presents the thermal flow passing through the boundary layer in function of time during one acoustic cycle and clearly exhibits an abrupt increase to 3.15 mW at the instant of strong collapse. The harsh collapse manifests at its turn when the bubble contraction attains its extremum, which is simultaneously accompanied by a narrowing of the boundary layer width. Thus, the higher the heat flow, the narrower the width of the thermal layer and the higher the temperature attained inside the layer according to Fourier’s law. The noticed increase in the thermal flow is then systematically equivalent to higher temperature values attained inside the layer. Fig. 2(b) shows effectively a peak of the median temperature attaining 1000 K and lasting almost 30 ns per cycle. This order of magnitude of the temperature is reported in several studies of cellulose pyrolysis [3], [4], [18], [46], however, the punctual increase of temperature in the form of pulses during infinitesimal timeslots requires deeper examination of its effect on the cellulose decomposition kinetics, this is discussed later in Fig. 4.

Fig. 4.

Fig. 4

Evolution of the molar rates of cellulose decomposition and products emergence around a collapsing acoustic cavitation bubble oscillating in [C4mim][CH3COO], under 1.8 atm and 200 kHz.

Fig. 3 presents further details regarding the spatial and temporal evolution of temperature within the thermal boundary layer. In Fig. 3 (a), the radial variation of the temperature is shown at five selected instants preceding and following the harsh collapse, this latter occurs exactly at 3.62 µs. It is clearly observed how the rapid increase in temperature occurs between 3.6 µs, where it reaches at the mid-width a value of 645.6 K, and the instant of the strong collapse where a value of 1000 K is recorded, revealing an augmentation of almost 17.7 K/ns. The rapid cooling is also noticeable from the moment of the harsh collapse, until 3.8 µs, where the temperature returns to the equilibrium value, i.e., that of the ionic liquid, at an average cooling speed of 3.59 K/ns.

Fig. 3.

Fig. 3

Spatial evolution of the temperature across the thermal boundary layer at various instants (a) and evolution of the temperature at different positions within the thermal boundary layer versus time during one acoustic cycle (b) for a single acoustic cavitation bubble oscillating in [C4mim][CH3COO] under 1.8 atm and 200 kHz.

In the other hand, Fig. 3 (b) presents the evolution of temperature at five equidistant positions within the thermal boundary layer in function of time. At the instant of the strong collapse, the width of the thermal boundary layer is equal to 0.76 µm, Fig. 3(b) shows that at 0.152 µm from the gaseous side of the thermal layer, the temperature attains 1332.9 K, while it is estimated at the same distance from the liquid side at 623.3 K. The temporal variation indicates that no evolution is observed except during the timeframe surrounding the collapse. The sensitivity of the dissolved cellulose toward the temperature variation is studied by inspecting its decomposition kinetics, assuming an arbitrary initial concentration of 1 mM. The molar rates of cellulose decomposition and products emergence around the instant of collapse are reported in Fig. 4.

Fig. 4 demonstrates that starting from the bubble contraction phase, the first stage of cellulose decomposition begins with an increasing rate that attains 1.71 × 104 mol/m3⋅s at the instant of the strong collapse (3.62 µs). This first stage corresponds to the reduction of the degree of polymerization by the formation of the so called “anhydrocellulose” or “active cellulose” [4] at a rate that reaches 7.91 × 104 mol/m3⋅s. The decomposition rate decreases afterwards while the initiated chain mechanism gives rise to primary and secondary gases, mainly composed of CH4, CO2 and CO as detected by the TG-FTIR by Shen and Gu [4], as well as bio-oil (tars) composed of levoglucosan, pyruvaldehyde, hydroxyacetone and hydroxyacetaldehyde. The emergence of gases and tars remain limited during the simulation timeframe, Fig. 4 reveals a total emergence rate of gases that equals 5.68 × 10−2 mol/m3⋅s, and a production rate of bio-oil neighboring 2.59 × 10−10 mol/m3⋅s. This observation is explained by the predominance of the reaction: Cellulose  Active cellulose during short timeslots owing to its pre-exponential factor. However, it is believed that longer reacting time would lead to clearer insights into the yields of decomposition products and allow a quantitative appreciation of the US/ILs hybridization concept toward cellulose decomposition, especially when including the bubble population dimension in the modeling study. This track may define the perspective of this initial study.

4. Conclusion

The present paper suggests a numerical investigation of the feasibility of a US/ILs hybrid concept toward cellulose decomposition. The study of the acoustic cavitation bubble dynamics under 200 kHz demonstrated that a bubble of 5 µm requires an amplitude of 1.8 atm or higher to achieve a transient state, the relatively high power ultrasound is explained by the high viscosity of [C4mim][CH3COO]. Yet, the bubble oscillation did not manifest the extreme expansion and collapse ratios usually retrieved with bubble evolving in water, both were limited to 2.56 and 5.36, respectively.

Maximum temperature and pressure in the bulk volume of the bubble demonstrated moderated values of 1559.8 K and 49 bar, which was in perfect agreement with some previous experimental and modeling findings. At the instant of strong collapse, the bulk volume of the bubble was exclusively composed of an inert gas, argon, and hence, the reacting site was defined as the boundary layer surrounding the bubble, according to the two-site model of sonochemical reactions. The spatial and temporal evolution of the temperature within this layer exhibited a value of 1000 K at the mid-width and the instant of strong collapse (3.62 µs). The chemical kinetics of decomposition of dissolved cellulose at the thermal boundary layer revealed a maximum rate of cellulose decomposition of 1.71 × 104 mol/m3⋅s at 3.62 µs, mainly explained by the first stage of polymerization reduction of cellulose into anhydrocellulose, this latter showed an emergence rate reaching 7.91 × 104 mol/m3⋅s. This mechanism was accompanied of the apparition of primary and secondary gases as well as bio-oil at infinitesimal rates; however, it is believed that longer simulation time would be more telling on the outcomes of the concept toward cellulose decomposition. This is set as a perspective for the present study, along with introducing the bubble population dimension in the expected model.

CRediT authorship contribution statement

Kaouther Kerboua: Conceptualization, Methodology, Software, Formal analysis, Writing - original draft, Writing - review & editing. Oualid Hamdaoui: Project administration, Visualization, Supervision, Writing - review & editing. Abdulaziz Alghyamah: Visualization, Writing - review & editing.

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

The authors extend their appreciation to the Deputyship for Research & Innovation, “Ministry of Education” in Saudi Arabia for funding this research work through the project number IFKSUHI-1441-501.

Contributor Information

Kaouther Kerboua, Email: k.kerboua@esti-annaba.dz, kaouther.kerboua.esti@gmail.com.

Oualid Hamdaoui, Email: ohamdaoui@ksu.edu.sa.

References

  • 1.Mohd N., Draman S.F.S., Salleh M.S.N., Yusof N.B. Dissolution of cellulose in ionic liquid: A review. AIP Conf. Proc. 2017;1809 doi: 10.1063/1.4975450. [DOI] [Google Scholar]
  • 2.Poletto M., Ornaghi Jnior H.L., Zattera A.J. Wiley; 2015. Thermal Decomposition Of Natural Fibers: Kinetics and Degradation Mechanisms. doi:10.1002/9781119117711.ch21. [Google Scholar]
  • 3.Wooten J.B., Seeman J.I., Hajaligol M.R. Observation and characterization of cellulose pyrolysis intermediates by 13C CPMAS NMR. A new mechanistic model. Energy Fuels. 2004;18:1–15. doi: 10.1021/ef0300601. [DOI] [Google Scholar]
  • 4.Shen D.K., Gu S. The mechanism for thermal decomposition of cellulose and its main products. Bioresour. Technol. 2009;100:6496–6504. doi: 10.1016/j.biortech.2009.06.095. [DOI] [PubMed] [Google Scholar]
  • 5.Zhang J., Wu J., Yu J., Zhang X., He J., Zhang J. Application of ionic liquids for dissolving cellulose and fabricating cellulose-based materials: State of the art and future trends. Mater. Chem. Front. 2017;1:1273–1290. doi: 10.1039/c6qm00348f. [DOI] [Google Scholar]
  • 6.Xu A., Guo X., Xu R. Understanding the dissolution of cellulose in 1-butyl-3-methylimidazolium acetate+DMAc solvent. Int. J. Biol. Macromol. 2015;81:1000–1004. doi: 10.1016/j.ijbiomac.2015.09.058. [DOI] [PubMed] [Google Scholar]
  • 7.Stefanovic B., Rosenau T., Potthast A. Effect of sonochemical treatments on the integrity and oxidation state of cellulose. Carbohydr. Polym. 2013;92:921–927. doi: 10.1016/j.carbpol.2012.09.039. [DOI] [PubMed] [Google Scholar]
  • 8.Ahmad E., Pant K.K. Elsevier; 2018. Lignin Conversion: A Key To The Concept Of Lignocellulosic Biomass-Based Integrated Biorefinery. doi:10.1016/B978-0-444-63992-9.00014-8. [Google Scholar]
  • 9.Swatloski R.P., Spear S.K., Holbrey J.D., Rogers R.D. Dissolution of cellose with ionic liquids. J. Am. Chem. Soc. 2002;124:4974–4975. doi: 10.1021/ja025790m. [DOI] [PubMed] [Google Scholar]
  • 10.Isik M., Sardon H., Mecerreyes D. Ionic liquids and cellulose: Dissolution, chemical modification and preparation of new cellulosic materials. Int. J. Mol. Sci. 2014;15:11922–11940. doi: 10.3390/ijms150711922. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.Xu A., Wang J., Wang H. Effects of anionic structure and lithium salts addition on the dissolution of cellulose in 1-butyl-3-methylimidazolium-based ionic liquid solvent systems. Green Chem. 2010;12:268–327. doi: 10.1039/b916882f. [DOI] [Google Scholar]
  • 12.Oster K., Jacquemin J., Hardacre C., Ribeiro A.P.C., Elsinawi A. Further development of the predictive models for physical properties of pure ionic liquids: Thermal conductivity and heat capacity. J. Chem. Thermodyn. 2018;118:1–15. doi: 10.1016/j.jct.2017.10.010. [DOI] [Google Scholar]
  • 13.Ebner G., Schiehser S., Potthast A., Rosenau T. Side reaction of cellulose with common 1-alkyl-3-methylimidazolium-based ionic liquids. Tetrahedron Lett. 2008;49:7322–7324. doi: 10.1016/j.tetlet.2008.10.052. [DOI] [Google Scholar]
  • 14.Kosan B., Michels C., Meister F. Dissolution and forming of cellulose with ionic liquids. Cellulose. 2008;15:59–66. doi: 10.1007/s10570-007-9160-x. [DOI] [Google Scholar]
  • 15.Strechan A.A., Paulechka Y.U., Blokhin A.V., Kabo G.J. Low-temperature heat capacity of hydrophilic ionic liquids [BMIM][CF3COO] and [BMIM][CH3COO] and a correlation scheme for estimation of heat capacity of ionic liquids. J. Chem. Thermodyn. 2008;40:632–639. doi: 10.1016/j.jct.2007.11.004. [DOI] [Google Scholar]
  • 16.Klyosov A.A. Enzymatic conversion of cellulosic materials to sugars and alcohol - The technology and its implications. Appl. Biochem. Biotechnol. 1986;12:249–300. doi: 10.1007/BF02798425. [DOI] [Google Scholar]
  • 17.Deng W., Zhang Q., Wang Y. Catalytic transformation of cellulose and its derived carbohydrates into chemicals involving C-C bond cleavage. J. Energy Chem. 2015;24:595–607. doi: 10.1016/j.jechem.2015.08.016. [DOI] [Google Scholar]
  • 18.Várhegyi G., Szabó P., Mok W.S.L., Antal M.J. Kinetics of the thermal decomposition of cellulose in sealed vessels at elevated pressures. Effects of the presence of water on the reaction mechanism. J. Anal. Appl. Pyrolysis. 1993;26:159–174. doi: 10.1016/0165-2370(93)80064-7. [DOI] [Google Scholar]
  • 19.Lauterborn W., Mettin R. Elsevier; 2015. Acoustic Cavitation: Bubble Dynamics In High-Power Ultrasonic Fields. doi:10.1016/B978-1-78242-028-6.00003-X. [Google Scholar]
  • 20.Cataldo F. Ultrasound-induced cracking and pyrolysis of some aromatic and naphthenic hydrocarbons. Ultrason. Sonochem. 2000;7:35–43. doi: 10.1016/S1350-4177(99)00019-X. [DOI] [PubMed] [Google Scholar]
  • 21.Kerboua K., Hamdaoui O. Oxygen-argon acoustic cavitation bubble in a water-methanol mixture: Effects of medium composition on sonochemical activity. Ultrason. Sonochem. 2020;61 doi: 10.1016/j.ultsonch.2019.104811. [DOI] [PubMed] [Google Scholar]
  • 22.Liu L., Ju M., Li W., Hou Q. Dissolution of cellulose from AFEX-pretreated Zoysia japonica in AMIMCl with ultrasonic vibration. Carbohydr. Polym. 2013;98:412–420. doi: 10.1016/j.carbpol.2013.06.030. [DOI] [PubMed] [Google Scholar]
  • 23.Grabber J.H., Davidson C., Tobimatsu Y., Kim H., Lu F., Zhu Y., Opietnik M., Santoro N., Foster C.E., Yue F., Ress D., Pan X., Ralph J. Structural features of alternative lignin monomers associated with improved digestibility of artificially lignified maize cell walls. Plant Sci. 2019;287 doi: 10.1016/j.plantsci.2019.02.004. [DOI] [PubMed] [Google Scholar]
  • 24.Lan W., Liu C.F., Yue F.X., Sun R.C., Kennedy J.F. Ultrasound-assisted dissolution of cellulose in ionic liquid. Carbohydr. Polym. 2011;86:672–677. doi: 10.1016/j.carbpol.2011.05.013. [DOI] [Google Scholar]
  • 25.Suslick K.S. Sonoluminescence and sonochemistry. Proc. IEEE Ultrason. Symp. 1997;1:523–532. doi: 10.1016/b0-12-227410-5/00953-4. [DOI] [Google Scholar]
  • 26.Song T., Lubben M.J., Brennecke J.F. Solubility of argon, krypton and xenon in ionic liquids. Fluid Phase Equilib. 2020;504 doi: 10.1016/j.fluid.2019.112334. [DOI] [Google Scholar]
  • 27.Jacquemin J., Costa Gomes M.F., Husson P., Majer V. Solubility of carbon dioxide, ethane, methane, oxygen, nitrogen, hydrogen, argon, and carbon monoxide in 1-butyl-3-methylimidazolium tetrafluoroborate between temperatures 283 K and 343 K and at pressures close to atmospheric. J. Chem. Thermodyn. 2006;38:490–502. doi: 10.1016/j.jct.2005.07.002. [DOI] [Google Scholar]
  • 28.Lee B.-C., Outcalt S.L. Solubilities of Gases in the Ionic Liquid 1- n -Butyl-3-methylimidazolium Bis(trifluoromethylsulfonyl)imide. J. Chem. Eng. Data. 2006;51:892–897. doi: 10.1021/je050357o. [DOI] [Google Scholar]
  • 29.Anthony J.L., Anderson J.L., Maginn E.J., Brennecke J.F. Anion effects on gas solubility in ionic liquids. J. Phys. Chem. B. 2005;109:6366–6374. doi: 10.1021/jp046404l. [DOI] [PubMed] [Google Scholar]
  • 30.Apfel R.E. Acoustic cavitation. Methods Exp. Phys. 1981;19:355–411. doi: 10.1016/S0076-695X(08)60338-5. [DOI] [Google Scholar]
  • 31.Safarov J., Geppert-Rybczyńska M., Kul I., Hassel E. Thermophysical properties of 1-butyl-3-methylimidazolium acetate over a wide range of temperatures and pressures. Fluid Phase Equilib. 2014;383:144–155. doi: 10.1016/j.fluid.2014.10.015. [DOI] [Google Scholar]
  • 32.Valderrama J.O., Sanga W.W. 2nd Int. Symp. Biothermodynamics Febr. 2008, Frankfurt-Germany. 2008. Critical Properties and vapor pressure of twenty imidazolium based ionic liquids used in extraction bioprocesses; pp. 1–9. [Google Scholar]
  • 33.Yasui K., Tuziuti T., Kanematsu W. Extreme conditions in a dissolving air nanobubble. Phys. Rev. E. 2016;94:1–13. doi: 10.1103/PhysRevE.94.013106. [DOI] [PubMed] [Google Scholar]
  • 34.Fröba A.P., Rausch M.H., Krzeminski K., Assenbaum D., Wasserscheid P., Leipertz A. Thermal conductivity of ionic liquids: Measurement and prediction. Int. J. Thermophys. 2010;31:2059–2077. doi: 10.1007/s10765-010-0889-3. [DOI] [Google Scholar]
  • 35.Hezave A.Z., Raeissi S., Lashkarbolooki M. Estimation of thermal conductivity of ionic liquids using a perceptron neural network. Ind. Eng. Chem. Res. 2012;51:9886–9893. doi: 10.1021/ie202681b. [DOI] [Google Scholar]
  • 36.Sivasankar T., Moholkar V.S. Physical insights into the sonochemical degradation of recalcitrant organic pollutants with cavitation bubble dynamics. Ultrason. Sonochem. 2009;16:769–781. doi: 10.1016/j.ultsonch.2009.02.009. [DOI] [PubMed] [Google Scholar]
  • 37.Yasui K. Alternative model of single-bubble sonoluminescence. Phys. Rev. E - Stat. Physics, Plasmas, Fluids, Relat. Interdiscip. Top. 1997;56:6750–6760. doi: 10.1103/PhysRevE.56.6750. [DOI] [PubMed] [Google Scholar]
  • 38.Chatel G., Macfarlane D.R. Ionic liquids and ultrasound in combination: Synergies and challenges. Chem. Soc. Rev. 2014;43:8132–8149. doi: 10.1039/c4cs00193a. [DOI] [PubMed] [Google Scholar]
  • 39.Diebold J.P. A unified, global model for the pyrolysis of cellulose. Biomass and Bioenergy. 1994;7:75–85. doi: 10.1016/0961-9534(94)00039-V. [DOI] [Google Scholar]
  • 40.Kerboua K., Hamdaoui O. Sonochemistry in Green processes: modeling, experiments, and technology. Sustain. Green Chem. Process. Their Allied Appl. 2020:603. doi: 10.1007/978-3-030-42284-4. [DOI] [Google Scholar]
  • 41.Yasui K. Theor. Exp. Sonochemistry Involv. Inorg. Syst. National Institute of Advanced Industrial Science and Technology; Anagahora-Japan: 2011. Fundamentals of acoustic cavitation and sonochemistry; pp. 1–29. doi:10.1007/978-90-481-3887-6. [Google Scholar]
  • 42.Hernoux-Villière A., Lévêque J.M., Kärkkäinen J., Papaiconomou N., Lajunen M., Lassi U. Task-specific ionic liquid for the depolymerisation of starch-based industrial waste into high reducing sugars. Catal. Today. 2014;223:11–17. doi: 10.1016/j.cattod.2013.09.027. [DOI] [Google Scholar]
  • 43.Kerboua K., Hamdaoui O. Ultrasonic waveform upshot on mass variation within single cavitation bubble: Investigation of physical and chemical transformations. Ultrason. Sonochem. 2018;42:508–516. doi: 10.1016/j.ultsonch.2017.12.015. [DOI] [PubMed] [Google Scholar]
  • 44.Kanthale P.M., Ashokkumar M., Grieser F. Estimation of cavitation bubble temperatures in an ionic liquid. J. Phys. Chem. C. 2007;111:18461–18463. doi: 10.1021/jp710148k. [DOI] [Google Scholar]
  • 45.Elder R.M., Calvisi M.L. Thermal Effects in ultrasonic cavitation of ionic liquids. Proc. 10th Int. Symp. Cavitation. 2019:1041–1046. doi: 10.1115/1.861851_ch198. [DOI] [Google Scholar]
  • 46.Chatterjee P.K. Chain reaction mechanism of cellulose pyrolysis. J. Appl. Polym. Sci. 1968;12:1859–1864. doi: 10.1002/app.1968.070120807. [DOI] [Google Scholar]

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