Next Article in Journal
Tailoring Variations in the Microstructures, Linear/Nonlinear Optical, and Mechanical Properties of Dysprosium-Oxide-Reinforced Borate Glasses
Next Article in Special Issue
The Effect of Metals of the 2nd and 12th Groups on the Productivity and Selectivity of Cumene Oxidation—The First Stage of the Technological Chain for the Production of Polymer Composites
Previous Article in Journal
Biochar Derived from Rice by-Products for Arsenic and Chromium Removal by Adsorption: A Review
Previous Article in Special Issue
Study of the Effects of Alkali Treatment and Fiber Orientation on Mechanical Properties of Enset/Sisal Polymer Hybrid Composite
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

The Effect of Ca, Sr, and Ba Chloride Complexes with Dibenzo-18-Crown-6 Ether as Catalysts on the Process Criteria for the Efficiency of Cumene Oxidation (the First Stage in the Chain of Polymer Composite Production)

by
Nikolai V. Ulitin
1,*,
Nikolay A. Novikov
1,
Yana L. Lyulinskaya
1,
Daria A. Shiyan
1,
Konstantin A. Tereshchenko
1,
Natalia M. Nurullina
1,
Marina N. Denisova
1,
Yaroslav O. Mezhuev
2,3,* and
Kharlampii E. Kharlampidi
1
1
Department of General Chemical Technology, Kazan National Research Technological University, Karl Marks Str., 68, 420015 Kazan, Russia
2
Department of Biomaterials, Mendeleev University of Chemical Technology of Russia, Miusskaya Square, 9, 125047 Moscow, Russia
3
A.N. Nesmeyanov Institute of Organoelement Compounds of Russian Academy of Sciences, Vavilova Str., 28, 119334 Moscow, Russia
*
Authors to whom correspondence should be addressed.
J. Compos. Sci. 2023, 7(2), 60; https://doi.org/10.3390/jcs7020060
Submission received: 14 December 2022 / Revised: 27 January 2023 / Accepted: 2 February 2023 / Published: 6 February 2023
(This article belongs to the Special Issue Progress in Polymer Composites, Volume II)

Abstract

:
A study was made on the effect of Ca, Sr, and Ba chloride complexes with dibenzo-18-crown-6 ether as catalysts on the process criteria of the efficiency of industrial cumene oxidation using kinetic modeling. It is the first stage in the process chain of polymer composite production. The kinetic scheme of the process is made of classical reactions of the radical chain mechanism (reactions of initiation, chain propagation, and chain termination), molecular reactions, reactions of formation of intermediate adducts “component of the reaction mixture—catalyst” and their decomposition, as well as reactions that take into account the specifics of the catalyst used: (1) formation of planar catalyst complexes with various substances; (2) formation of acetophenone along the catalytic path; (3) hydration of the intermediate adduct “α-methylstyrene—catalyst” to the required alcohol. It is shown that the kinetic model fully reproduces the experimental time dependencies of the cumene hydroperoxide concentration in the cumene oxidation and cumene hydroperoxide decomposition. Using the kinetic model, computational experiments were carried out, as a result of which the following conclusions were made: (1) among the considered catalysts, the complex of Sr chloride with dibenzo-18-crown-6 ether should be recognized as the best, provided that it is used at temperatures of 393–413 K and an initial concentration < 2 mmol/L; (2) to ensure selectivity comparable to the selectivity of a non-catalytic process, it is necessary to conduct the catalytic process at a lowest possible initial concentration of any of the considered catalysts.

1. Introduction

Cumene begins the process chain of the polymer composite production, which is as follows: (1) cumene oxidation (obtained by alkylation of benzene with propylene) with air oxygen is the production of cumene hydroperoxide [1,2]; (2) cumene hydroperoxide decomposition into phenol and acetone (the catalyst is sulfuric acid) [1,2]; (3) production of precursors from phenol; (4) production of oligomers and polymers (epoxy resins [3], phenol-formaldehyde resins [4], polycarbonates [5], polysulfones [6], polyamides [7]) from precursors; (5) composite production [8,9] based on oligomers and polymers. It is obvious that the productivity of the first stage in this process chain (the stage of cumene oxidation) will have an effect on the productivity of all its other stages. As a rule, cumene oxidation is carried out in bubble column reactors at 353–403 K and 0.1–0.7 MPa until the cumene conversion reaches 10–25%, while the selectivity is 85–90% [10]. Industrial cumene oxidation is carried out without a catalyst, but the interest of researchers in catalysts that allow for accelerating the process while maintaining selectivity at the level of non-catalytic oxidation continues unabated. It is caused by the economic feasibility of intensifying this large-scale process. Significant progress has currently been made in the field of homogeneous and heterogeneous catalysis of cumene oxidation [11,12,13,14,15,16,17,18,19]. It is important to note that the effect of catalysts on the technological significance of the process (reagent conversion, selectivity, productivity) is studied in conditions far from industrial conditions, which does not allow catalysts to be used beyond the laboratories. This problem can be solved by modeling according to the following algorithm:
(1)
carrying out the experimental kinetic studies;
(2)
based on the experimental and theoretical prerequisites, a kinetic scheme of the process was proposed where the kinetic model is created using the mass action law;
(3)
the kinetic model is verified using experimental data (at this stage, the kinetic scheme and values of the model parameters can be revised); the kinetic model is basic, but often it is enough for preliminary calculations (the kinetic model can be made into a more complicated macrokinetic model to take into account the hydrodynamics of the reactor or can be built-in into the chemical process model which is implemented in a universal modeling program such as Aspen Hysys);
(4)
the computational experiments are carried out using the model, reproducing the industrial conditions of the process; according to the results of computational experiments, the catalyst can be either recommended or not recommended for use in industrial conditions.
The objects of study were complexes of Ca, Sr, and Ba chloride with dibenzo-18-crown-6 ether, which are used as catalysts for cumene oxidation and cumene hydroperoxide decomposition. Complexes of this kind have proven to be homogeneous catalysts readily soluble in alkylaromatic hydrocarbons [18]. The purpose of this work was to study the catalytic abilities of stable complexes of Ca, Sr, and Ba chlorides with dibenzo-18-crown-6 ether and to determine the prospects for their industrial use in cumene oxidation to cumene hydroperoxide using kinetic modeling.

2. Materials and Methods

2.1. Materials

In the experiments, the following substances were used:
(1)
cumene produced by PJSC Kazanorgsintez;
(2)
cumene hydroperoxide with the content of the main substance being 99.4% wt.;
(3)
air oxygen as an oxidizing agent;
(4)
Ca, Sr, and Ba chloride complexes with dibenzo-18-crown-6 ether are the catalysts for cumene oxidation and cumene hydroperoxide decomposition: they were synthesized by reacting a solution of Ca (or Ba) chloride in n-butanol or a solution of Sr chloride in ethanol with a solution dibenzo-18-crown-6 ether in acetone (stirring in a flask under reflux at a temperature of 343–348 K for 1–1.5 h); the resulting complexes in the form of white crystalline substances were filtered off, washed with n-butanol (Ca, Ba) or ethanol (Sr), and dried in air (the formation of complexes with a composition of 1:1 was proved by the molar mass of the complex, determined by cryoscopy: M(Ca) = 482.98 g/mol, M(Sr) = 527.55 g/mol, M(Ba) = 571.61 g/mol);
(5)
chlorobenzene is a solvent in the decomposition of cumene hydroperoxide.

2.2. Cumene Oxidation

Cumene ([RH]0 = 6.44 mol/L) mixed with a catalyst ([Cat]0 = 5 mmol/L) was used to fill a bubble column (diameter 36 mm, length 500 mm); thereafter the cumene was oxidized with air at a temperature of 393 K and pressure P = 1 atm. The air, preliminarily treated from mechanical impurities and dried, was continuously supplied by a compressor (flow rate G = 0.6 L/min) down the reactor. The distribution of air in the liquid was carried out using a distribution grid with holes about 1 mm in diameter located at the bottom of the reactor. Samples of the reaction mixture were taken every hour through a valve on the side of the reactor. The quantitative content of cumene hydroperoxide in the sample was determined by iodometry method, and by-products were determined by gas–liquid chromatography (Chromatec Crystal 5000 chromatograph, the manufacturer is JSC SDO “CHROMATEC”, Yoshkar-Ola, Russia; capillary column: sol–gel wax (polyethylene glycol) with a polar phase). The process was carried out for 6 h.

2.3. Cumene Hydroperoxide Decomposition

Glass ampoules were filled with a mixture of cumene hydroperoxide ([ROOH]0 = 1 mol/L) and catalyst ([Cat]0 = 5 mmol/L), sealed, then immersed in a thermostat heated to a temperature T = 403 K, and the shaking device was turned on. At certain intervals, the ampoules were removed one at a time, and the reaction was stopped by cooling the ampoules in ice water; the composition of the reaction mixture was analyzed in the same way as in the case of cumene oxidation (see Section 2.2). The process was carried out for 6 h.

3. Results

In Table 1 the cumene oxidation data are shown in the presence of various catalysts studied in this work and in [9,20,21]. Among the catalysts considered in this work, the Sr complex with dibenzo-18-crown-6 ether should be recognized as the best (Figure 1a): the reaction mass accumulates the largest amount of the target oxidation product, cumene hydroperoxide (1.43 mol/L).
It is known that the initiation of the oxidation chain reaction runs due to free radicals formed during the cumene hydroperoxide decomposition [22]. As a rule, the cumene hydroperoxide decomposition is preceded by its activation in the “cumene hydroperoxide—catalyst” adduct [19]. Therefore, the acceleration of cumene oxidation in the presence of complexes of the chlorides Ca, Sr, and Ba with dibenzo-18-crown-6 ether runs due to the acceleration of the cumene hydroperoxide decomposition (Figure 2a). These data confirm the participation of the ROOH·Cat intermediate adduct in the formation of free radicals according to reaction (8). The high rate of cumene hydroperoxide accumulation in the presence of the Sr complex with dibenzo-18-crown-6 ether compared to other catalysts (Figure 1a) is due to the fact that cumene hydroperoxide decomposes faster in the presence of this complex compared to Ca and Ba complexes with dibenzo-18-crown-6 ether (Figure 2a).
As a general kinetic scheme of cumene oxidation (when the oxygen concentration change rate in the reaction mixture due to its dissolution in it does not equal zero) and the cumene hydroperoxide decomposition (when the oxygen concentration change rate in the reaction mixture due to its dissolution in it is equal to zero) in the presence of Ca, Sr, and Ba chloride complex with dibenzo-18-crown-6 ether as catalysts, a set of reactions (1–50) was considered. Reactions (1–4), (6–45) are similar to the reactions proposed by us in [19] for the general kinetic scheme of cumene oxidation and cumene hydroperoxide decomposition in the presence of Zn, Cd, and Hg 2-ethylhexanoate as catalysts. Since Zn, Cd, and Hg and Ca, Sr, and Ba are metals incapable of valence transformations, and they can catalyze the cumene oxidation through the formation of intermediate adducts with the components of the reaction mixture [23], it is obvious that reactions (1–4) and (6–45) should be in the general mechanism of cumene oxidation and cumene hydroperoxide decomposition in the presence of Zn, Cd, and Hg 2-ethylhexanoate and Ca, Sr, and Ba chloride complexes with dibenzo-18-crown-6 ether. In addition, the scheme of reactions (1–4) and (6–45) was supplemented with the following reactions:
(1)
reaction (5) is written by analogy with reaction (1);
(2)
reaction (46), which describes the decomposition of the intermediate ROH·Cat adduct to acetophenone (the formation of acetophenone also runs without the participation of a catalyst, which was experimentally shown in [24]; in the mechanism, the non-catalytic pathway for the formation of acetophenone is represented by reactions (21) and (44); however, much more acetophenone is formed in catalytic processes than in non-catalytic processes, which also indicates the catalytic pathway of its formation);
(3)
reaction (47) is shown by analogy with [25];
(4)
reaction (48) describes the formation of a planar complex of phenol with a catalyst since such compounds are characterized by the formation of planar complexes [26]; reaction (48) is irreversible since crown ethers are strong adsorbing agents, in particular, for phenol [26];
(5)
reaction (49) is shown by analogy with [27];
(6)
reaction (50) probably runs due to the ability of unsaturated hydrocarbons to be hydrated under the action of catalysts into the corresponding alcohols [28].
Formation of intermediate adducts:
RH + Cat k 1 k 1 RH Cat ,
ROOH + Cat k 2 k 2 ROOH Cat ,
ROH + Cat k 3 k 3 ROH Cat ,
HC ( O ) H + Cat k 4 HC ( O ) H Cat .
  C 6 H 5 C ( CH 3 ) = CH 2 + Cat k 5 k 5   C 6 H 5 C ( CH 3 ) = CH 2 Cat .
Chain initiation:
RH + O 2 k 6 R + O OH ,
RH Cat + O 2 k 7 R + O OH + Cat ,
ROOH k 8 RO + O H ,
ROOH Cat k 9 RO + O H + Cat ,
2 ROOH k 10 ROO + RO + H 2 O ,
2 ROOH Cat k 11 RO + ROO + H 2 O + 2 Cat .
Chain propagation:
R + O 2 k 12 ROO ,
RH + ROO k 13 R + ROOH ,
RH Cat + ROO k 14 R + ROOH + Cat ,
RH + RO k 15 ROH + R ,
RH Cat + RO k 16 ROH + R + Cat ,
RH + O H k 17 R + H 2 O ,
RH Cat + O H k 18 R + H 2 O + Cat ,
ROOH + RO k 19 ROO + ROH ,
ROOH Cat + RO k 20 ROO + ROH + Cat ,
RO k 21 C 6 H 5 C ( O ) CH 3 + CH 3 ,
2 ROO k 22 2 RO + O 2 ,
CH 3 + O 2 k 23 CH 3 OO ,
CH 3 OO + RH k 24 CH 3 OOH + R ,
CH 3 OO + RH Cat k 25 CH 3 OOH + R + Cat ,
C 6 H 5 OH + ROO k 26 C 6 H 5 O + ROOH .
Chain termination:
2 R k 27 RR ,
R + ROO k 28 ROOR ,
CH 3 · + O H k 29 CH 3 OH ,
2 ROO k 30 ROOR + O 2 ,
CH 3 OO + ROO k 31 ROH + HC ( O ) H + O 2 ,
C 6 H 5 O + ROO k 32 C 6 H 5 OH + O 2 + C 6 H 5 C ( CH 3 ) = CH 2 ,
C 6 H 5 O + ROO k 33 C 6 H 5 OOR + 0 . 5 O 2 ,
R + O OH k 34 ROOH .
Molecular reactions:
ROH k 35 C 6 H 5 C ( CH 3 ) = CH 2 + H 2 O ,
ROH Cat k 36 C 6 H 5 C ( CH 3 ) = CH 2 + H 2 O + Cat ,
HC ( O ) H Cat + 0.5 O 2 k 37 HCOOH + Cat ,
ROOH k 38 C 6 H 5 OH + CH 3 C ( O ) CH 3 ,
ROOH Cat k 39 C 6 H 5 OH + CH 3 C ( O ) CH 3 + Cat ,
ROOH + ROH k 40 2 ROH + 0.5 O 2 ,
ROOH Cat + ROH k 41 2 ROH + 0.5 O 2 + Cat ,
ROOH + HCOOH k 42 k 42 ROOH HCOOH ,
ROOH HCOOH k 43 C 6 H 5 OH + CH 3 C ( O ) CH 3 + HCOOH ,
C 6 H 5 C ( CH 3 ) = CH 2 + O 2 k 44 C 6 H 5 C ( O ) CH 3 + HC ( O ) H ,
Cat k 45 Cat ,
ROH Cat k 46 C 6 H 5 C ( O ) CH 3 + CH 4 + Cat ,
ROOH Cat + C 6 H 5 C ( CH 3 ) = CH 2 k 47 ROH + C 6 H 5 C ( CH 3 ) ( O ) ( CH 2 ) + Cat ,
C 6 H 5 OH + Cat k 48 C 6 H 5 OH Cat ,
2 ROOH Cat + RH k 49 ROH + ROOR + H 2 O + Cat ,
  C 6 H 5 C ( CH 3 ) = CH 2 Cat + H 2 O k 50 ROH + C a t .
where RH is cumene (C6H5CH(CH3)2), Cat is the catalyst, RH·Cat is a “cumene—catalyst” intermediate adduct, ROOH is cumene hydroperoxide, ROOH·Cat is a “cumene hydroperoxide—catalyst” intermediate adduct, ROH is dimethylphenylcarbinol, ROH·Cat is a “dimethylphenylcarbinol—catalyst” intermediate adduct, HC(O)H is formaldehyde, HC(O)H·Cat is a “formaldehyde—catalyst” intermediate adduct, C6H5C(CH3) = CH2 is α-methylstyrene, C6H5C(CH3) = CH2·Cat is a “α-methylstyrene—catalyst” intermediate adduct, O2 is oxygen, R is a cumyl radical, OOH is a hydroperoxide (hydroperoxyl) radical, RO is a cumyloxyl radical, OH is a hydroxyl radical, ROO is a cumyl peroxyl radical, H2O is water, C6H5C(O)CH3 is acetophenone, CH3 is a methyl radical, CH3OO is a methyl peroxyl radical, CH3OOH is methyl hydroperoxide, C6H5OH is phenol, C6H5O is benzoyloxy radical, RR is dicumyl, ROOR is dicumyl peroxide, CH3OH is methanol, C6H5OOR is benzylcumonoate, HCOOH is formic acid, CH3C(O)CH3 is acetone, ROOH·HCOOH is a “cumene hydroperoxide—formic acid” intermediate adduct, Cat’ is the deactivated catalyst, CH4 is methane, C6H5C(CH3)(O)(CH2) is 2-methyl-2-phenyloxirane, C6H5OH·Cat is a planar complex of phenol with a catalyst.
Then, based on the scheme consisting of reactions (1–50), the kinetic model was written as a system of nonlinear differential equations, which describes, according to the mass action law, the rate of change of the concentrations of all reaction mixture species. The reaction rate coefficients in the kinetic model were set as functions of temperature according to the Arrhenius equation. To determine the values of the pre-exponential factor and the activation energy for each Arrhenius temperature dependence on the reaction rate coefficient, an inverse kinetic problem was solved. The inverse kinetic problem is the problem of determining such model parameters for which the discrepancy between the data calculated using the model and the experimental data is minimal [29]. The inverse kinetic problem was solved by the method of direct search of the zero order [30]. A comparison of experimental data and data calculated by the kinetic model with the found parameters (Table 2) is shown in Figure 1 and Figure 2. The kinetic model, within the average relative error of 25%, satisfactorily described laboratory experimental data of cumene oxidation and cumene hydroperoxide decomposition.
Further, using the kinetic model, we carried out computational experiments simulating the cumene oxidation under industrial conditions (the initial concentrations of species were set in accordance with the composition of the flow charge from [29]). (It should be noted that in this article, the cumene oxidation was experimentally studied running in a bubble column reactor. The following approximations were included in the kinetic model: the reactor is a batch reactor in terms of the liquid phase and a plug flow reactor in terms of air. Various designs of cumene oxidation reactors are used in industry; therefore, in this case, computational experiments are close to industrial conditions only in terms of the composition of the reaction mixture.) The results of computational experiments and their discussion are shown below.

4. Discussion

The concentration of cumene hydroperoxide accumulates over time up to a certain maximum value, after which it reduces (Figure 3). The reduction of the cumene hydroperoxide concentration after the maximum value (Figure 1a and Figure 3) is associated with the cumene hydroperoxide decomposition, which results in the formation of dimethylphenylcarbinol ROH (Figure 1b), α-methylstyrene C6H5C(CH3) = CH2 (Figure 1c), acetophenone C6H5C(O)CH3 (Figure 1d), and phenol C6H5OH (Figure 1e). The concentration of cumene hydroperoxide grows linearly with an increase in the oxidation time until the maximum value is reached (Figure 1a). The time dependencies of the concentrations of dimethylphenylcarbinol ROH (Figure 1b), α-methylstyrene C6H5C(CH3) = CH2 (Figure 1c), and acetophenone C6H5C(O)CH3 (Figure 1d) also have a form close to a linear one, which indicates the first-order versus cumene hydroperoxide of the reactions of cumene hydroperoxide decomposition with the formation of these compounds. The concentration of phenol C6H5OH in time grows non-linearly with acceleration (Figure 1e), which, according to the kinetic scheme used by us, can only be explained by the accumulation of formic acid in the reaction system, which catalyzes the cumene hydroperoxide decomposition according to reactions (42,43).
This maximum value in the case of the presence of Sr and Ca is reached much earlier compared to the non-catalytic process and that in the presence of Ba, and after an increase of the cumene oxidation temperature, the time to reach the maximum concentration of cumene hydroperoxide decreases (Figure 3 and Figure 4).
Obviously, it is expedient to carry out the industrial cumene oxidation to the maximum achievable concentration of cumene hydroperoxide. Moreover, to ensure reasonable times for reaching the maximum concentration of cumene hydroperoxide, the cumene oxidation must be carried out at fairly high temperatures (under the process conditions shown in Figure 4, for a process in the presence of Sr or Ca, these are temperatures of 393–403 K, for a non-catalytic process and a process in the presence of Ba these are temperatures of 403–407 K).
The following criterion was used as a criterion reflecting the productivity of cumene oxidation at the moment of reaching the maximum concentration of cumene hydroperoxide and taking into account the cumene conversion and selectivity achieved in this case:
C = [ R O O H ] m a x t max ( 1 ( [ R H ] t max / [ R H ] 0 ) ) [ R O O H ] m a x [ R O O H ] 0 [ R H ] 0 [ R H ] t max ,
where [ROOH]max is the maximum concentration of cumene hydroperoxide, mol/L; tmax is the time to reach the maximum concentration of cumene hydroperoxide, h; [ROOH]0 is the initial concentration of cumene hydroperoxide, mol/L; [RH]tmax is the cumene concentration at time tmax, mol/L; [RH]0 is the initial concentration of cumene, mol/L; 1 − ([RH]tmax/[RH]0) is the cumene conversion at time tmax; ([ROOH]max − [ROOH]0)/([RH]0 − [RH]tmax) is the selectivity.
When the temperature increases, the C criterion grows to a maximum value (the maximum lies in the region of 393–413 K), after which it falls (Figure 5a). Catalysts, based on the value of the maximum criterion C, can be arranged in the following order (in the order of growth of this criterion): 1. Without the catalyst, Sr, and Ca; 2. Ba (Figure 5a). [ROOH]max and cumene conversion also pass through a maximum in the range of 393–413 K. Catalysts based on the value of the maximum [ROOH]max can be arranged in the following order (in the order of growth of this criterion): 1. Ba; 2. Ca; 3. Sr; 4. Without catalyst (Figure 5b). Catalysts based on the value of the maximum conversion of cumene can be placed in the following order (in the order of growth of this criterion): 1. Ba, Ca; 2. Without catalyst; 3. Sr (Figure 5c).
The temperature dependence of the selectivity in the range of 393–413 K has the form of a plateau. Catalysts based on the value of selectivity at the peak of this plateau can be placed in the following order (in the order of growth of the selectivity): 1. Without catalyst; 2. Ca; 3. Ba, Sr (Figure 5d).
At a constant temperature (406 K) chosen from the range of 393–413 K, at low initial concentrations of the [Cat]0 catalyst (<2 mmol/L), criterion C is maximum and falls in the row Sr > Ca > Ba (Figure 6a). At [Cat]0 > 2 mmol/L (Figure 6a):
(1)
criterion C for Sr has a minimum in the range [Cat]0 = 2–4 mmol/L, and at [Cat]0 > 4 mmol/L it reaches a plateau, the value of which is comparable to the value of criterion C at [Cat]0 < 2 mmol/L;
(2)
criterion C for Ca and Ba falls with growing [Cat]0 and reaches a plateau at [Cat]0 = 7 mmol/L;
(3)
criterion C falls in the row Sr >> Ca >> Ba.
The time to reach the maximum concentration of cumene hydroperoxide at [Cat]0 < 2 mmol/L lies in the range of 7–8 h. Catalysts based on the time to reach the maximum concentration of cumene hydroperoxide can be arranged in the following order (in the order of growth of this indicator): 1. Ca, Sr; 2. Ba (Figure 6b). At concentrations [Cat]0 > 2 mmol/L, the tmax for Ba is the same as at [Cat]0 < 2 mmol/L, and tmax for Sr decreases with the growth of [Cat]0 reaching the plateau at [Cat]0 = 5–6 mmol/L; tmax for Ca monotonically decreases with the growth of [Cat]0.
[ROOH]max for Ca and Ba reduces with the growth of [Cat]0 from 0 to 10 mmol/L, and [ROOH]max for Sr reduces with the growth of [Cat]0 up to 3 mmol/L and reaches a plateau (Figure 6c).
The cumene conversion for Ca with the growth of [Cat]0 to 7 mmol/L holds on a plateau (about 55%), after which it reduces; the cumene conversion for Ba with the growth of [Cat]0 from 0 to 10 mmol/L reduces from 55% to 40%; the cumene conversion for Sr first grows with the growth of [Cat]0, passing through a maximum (70%) at [Cat]0 = 2 mmol/L, after which it reduces until reaching the plateau (50%) at [Cat]0 = 6 mmol/L (Figure 6d). The dependencies of the selectivity for Ca and Sr versus [Cat]0 are mirror-like with respect to the similar dependence of the conversion; the dependence of the selectivity for Ba is the same as the similar dependence of the cumene conversion (Figure 6e,d). To ensure selectivity comparable with the selectivity of a non-catalytic process, it is necessary to carry out the catalytic process at the lowest possible initial concentration of any of the considered catalysts (Figure 6e).

5. Conclusions

Using kinetic modeling, a study was performed on the effect of Ca, Sr, and Ba chloride complexes with dibenzo-18-crown-6 ether as catalysts on the process criteria of the efficiency of industrial cumene oxidation using kinetic modeling. It is the first stage in the process chain of polymer composite production: (1) cumene oxidation (obtained by alkylation of benzene with propylene) with air oxygen is the production of cumene hydroperoxide; (2) cumene hydroperoxide decomposition into phenol and acetone; (3) production of precursors from phenol; (4) production of oligomers and polymers from precursors; (5) composite production based on oligomers and polymers. The kinetic scheme of the process is made of classical reactions of the radical chain mechanism (reactions of initiation, chain propagation, and chain termination), molecular reactions, reactions of formation of intermediate adducts “component of the reaction mixture—catalyst” and their decomposition, and reactions that take into account the specifics of the catalyst used: (1) formation of planar catalyst complexes with various substances; (2) formation of acetophenone along the catalytic path; (3) hydration of the intermediate adduct “α-methylstyrene—catalyst” to the required alcohol. It is shown that the kinetic model reproduces the experimental time dependencies of the cumene hydroperoxide concentration in the cumene oxidation and of cumene hydroperoxide decomposition within the error (25%). Using the kinetic model, computational experiments were carried out, as a result of which the following conclusions were made: (1) among the considered catalysts, the complex of Sr chloride with dibenzo-18-crown-6 ether should be recognized as the best, provided that it is used at temperatures of 393–413 K and an initial concentration < 2 mmol/L since the maximum value of the criterion reflecting the productivity of cumene oxidation at the moment of reaching the maximum concentration of cumene hydroperoxide and taking into account the cumene conversion and selectivity achieved in this case is reached in a relatively short time (7–8 h) with a cumene conversion of 60–70% and selectivity of 40–60%; (2) to ensure selectivity comparable to the selectivity of a non-catalytic process, it is necessary to conduct the catalytic process at a lowest possible initial concentration of any of the considered catalysts. Further research involves a more detailed study of the kinetic patterns and mechanism of the process under consideration (identification of limiting stages and reaction paths that make the greatest contribution to the kinetics of the process).

Author Contributions

N.V.U.: Funding acquisition, Project administration, Conceptualization, Methodology, Data curation, Formal analysis, Writing—original draft, Writing—review and editing; N.A.N.: Investigation, Visualization; Y.L.L.: Investigation, Visualization; D.A.S.: Investigation, Writing—original draft, Writing—review and editing; K.A.T.: Methodology, Data curation, Formal analysis, Writing—original draft, Writing—review and editing; N.M.N.: Investigation; M.N.D.: Investigation; Y.O.M.: Formal analysis; Writing—review and editing; Supervision, K.E.K.: Investigation; Data curation. All authors have read and agreed to the published version of the manuscript.

Funding

The study was funded by the Russian Science Foundation No. 22-13-00461, https://rscf.ru/project/22-13-00461 (accessed on 9 June 2022).

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Global Cumene Market Size study, By Production (Zeolite, Solid phosphoric acid, Aluminum chloride), By Application (Phenol, Acetone, Others), and Regional Forecasts. Available online: https://www.giiresearch.com/report/bzc1090047-global-cumene-market-size-study-by-production.html (accessed on 9 June 2022).
  2. Hock, H.; Lang, S. Autoxydation von Kohlenwasserstoffen, IX. Mitteil.: Über Peroxyde von Benzol-Derivaten. Ber. Dtsch. Chem. Ges. 1944, 77, 257–264. [Google Scholar] [CrossRef]
  3. Michelena, A.H.; Summerscales, J.; Graham-Jones, J.; Hall, W. Sustainable manufacture of natural fibre reinforced epoxy resin composites with coupling agent in the hardener. J. Compos. Sci. 2022, 6, 97. [Google Scholar] [CrossRef]
  4. Purse, M.; Holmes, B.; Sacchi, M.; Howlin, B. Simulating the complete pyrolysis and charring process of phenol–formaldehyde resins using reactive molecular dynamics. J. Mater. Sci. 2022, 57, 7600–7620. [Google Scholar] [CrossRef]
  5. Brunella, V.; Rossatto, B.G.; Mastropasqua, C.; Cesano, F.; Scarano, D. Thermal/Electrical properties and texture of carbon black PC polymer composites near the electrical percolation threshold. J. Compos. Sci. 2021, 5, 212. [Google Scholar] [CrossRef]
  6. Khvatov, A.V.; Brevnov, P.N.; Shilkina, N.G.; Lomakin, S.M. Thermal and physical and mechanical properties of polysulfone composites with carbon nanotubes. Russ. J. Phys. Chem. B 2019, 13, 519–524. [Google Scholar] [CrossRef]
  7. Kim, J.; Cho, D. Effects of alkali-treatment and feeding route of henequen fiber on the heat deflection temperature, mechanical, and impact properties of novel henequen Fiber/Polyamide 6 composites. J. Compos. Sci. 2022, 6, 89. [Google Scholar] [CrossRef]
  8. Mehrdoost, A.; Yengejeh, R.J.; Mohammadi, M.K.; Haghighatzadeh, A.; Babaei, A.A. Adsorption removal and photocatalytic degradation of azithromycin from aqueous solution using PAC/Fe/Ag/Zn nanocomposite. Environ. Sci. Pollut. Res. 2022, 29, 33514–33527. [Google Scholar] [CrossRef]
  9. Mehrdoost, A.; Yengejeh, R.J.; Mohammadi, M.K.; Babaei, A.A.; Haghighatzadeh, A. Comparative analysis of UV-assisted removal of azithromycin and cefixime from aqueous solution using PAC/Fe/Si/Zn nanocomposite. J. Health Sci. Surveill. Syst. 2021, 9, 39–49. [Google Scholar] [CrossRef]
  10. Weber, M.; Daldrup, J.-B.G.; Weber, M. Noncatalyzed radical chain oxidation: Cumene hydroperoxide. In Liquid Phase Aerobic Oxidation Catalysis; Stahl, S.S., Alsters, P.L., Eds.; Wiley-VCH Verlag GmbH & Co. KgaA: Weinheim, Germany, 2016; pp. 15–31. [Google Scholar] [CrossRef]
  11. Kuznetsova, N.I.; Babushkin, D.E.; Zudin, V.N.; Koscheeva, O.S.; Kuznetsova, L.I. Low-temperature oxidation of isopropylbenzene mediated by the system of NHPI, Fe(acac)3 and 1,10-phenanthroline. Catal. Commun. 2021, 149, 106218. [Google Scholar] [CrossRef]
  12. Turovskij, N.; Raksha, E.; Berestneva, Y.; Eresko, A. Anion effect on the cumene hydroperoxide decomposition in the presence of Cu(II) 1,10-phenanthrolinates. J. Organomet. Chem. 2020, 922, 121371. [Google Scholar] [CrossRef]
  13. Nowacka, A.; Briantais, P.; Prestipino, C.; Llabrés i Xamena, F.X. Selective aerobic oxidation of cumene to cumene hydroperoxide over mono- and bimetallic trimesate metal-organic frameworks prepared by a facile “green” aqueous synthesis. ACS Sustain. Chem. Eng. 2019, 7, 7708–7715. [Google Scholar] [CrossRef]
  14. Matienko, L.I.; Binyukov, V.I.; Mil, E.M.; Zaikov, G.E. Supramolecular macrostructures in the mechanisms of catalysis with nickel or iron heteroligand complexes. Curr. Organocatalysis. 2019, 6, 36–43. [Google Scholar] [CrossRef]
  15. Mu, C.H.; Cao, Y.; Wang, H.; Yu, H.; Peng, F. A kinetics study on cumene oxidation catalyzed by carbon nanotubes: Effect of N-doping. Chem. Eng. Sci. 2018, 177, 391–398. [Google Scholar] [CrossRef]
  16. Lu, Q.; Shi, G.; Zhou, H.; Yuan, E.; Chen, C.H.; Ji, l. A highly efficient transformation from cumene to cumyl hydroperoxide via catalytic aerobic oxidation at room temperature and investigations into solvent effects, reaction networks and mechanisms. Appl. Catal. A Cen. 2022, 630, 118441. [Google Scholar] [CrossRef]
  17. Lu, Y.; Sheng, X.; Zhang, J.; Wang, Y.; Du, L.; Zhu, J. Cumene autooxidation to cumene hydroperoxide based on a gas-liquid microdispersion strategy. Chem. Eng. Process. 2022, 174, 108861. [Google Scholar] [CrossRef]
  18. Matienko, L.I.; Mosolova, L.A.; Zaikov, G.E. Selective catalytic oxidation of hydrocarbons. New prospects. Russ. Chem. Rev. 2009, 78, 211–230. [Google Scholar] [CrossRef]
  19. Ulitin, N.V.; Kharlampidi, K.E.; Tereshchenko, K.A.; Novikov, N.A.; Shiyan, D.A.; Nurmurodov, T.S.; Nurullina, N.M.; Ziyatdinov, N.N.; Miroshkin, N.P. The cumene oxidation and cumene hydroperoxide decomposition in the presence of Zn, Cd or Hg 2-ethylhexanoate: Kinetic model and analysis of its sensitivity. Mol. Catal. 2021, 515, 111886. [Google Scholar] [CrossRef]
  20. Liao, S.; Peng, F.; Hao, Y.; Wang, H. Carbon nanotubes as catalyst for the aerobic oxidation of cumene to cumene hydroperoxide. Appl. Catal. A Gen. 2014, 478, 1–8. [Google Scholar] [CrossRef]
  21. Nowacka, A.; Vismara, R.; Mercuri, G.; Moroni, M.; Palomino, M.; Domasevitch, K.V.; Nicola, C.; Di Pettinari, C.; Giambastiani, G.; Llabrés i Xamena, F.X.; et al. Cobalt(II) Bipyrazolate Metal—Organic Frameworks as Heterogeneous Catalysts in Cumene Aerobic Oxidation: A Tag-Dependent Selectivity. Inorg. Chem. 2020, 59, 8161–8172. [Google Scholar] [CrossRef]
  22. Denisov, E.T.; Afanas’ev, I.B. Oxidation and Antioxidants in Organic Chemistry and Biology; Taylor & Francis Group: Boca Raton, FL, USA, 2005; 1024p. [Google Scholar]
  23. Masters, C. Homogeneous Transition-Metal Catalysis; Chapman and Hall: London, UK, 1981. [Google Scholar]
  24. Kharlampidi, K.E.; Tereshchenko, K.A.; Nurmurodov, T.S.; Shiyan, D.A.; Miroshkin, N.P.; Ziyatdinov, N.N.; Ziganshina, A.S.; Nurullina, N.M.; Khursan, S.L.; Ulitin, N.V. The kinetic modeling of cumene oxidation taking into account oxygen mass transfer. Chem. Eng. J. 2020, 392, 123811. [Google Scholar] [CrossRef]
  25. Dumbre, D.K.; Choudhary, V.R.; Patil, N.S.; Uphade, B.S.; Bhargava, S.K. Calcium oxide supported gold nanoparticles as catalysts for the selective epoxidation of styrene by t-butyl hydroperoxide. J. Colloid Interface Sci. 2014, 415, 111–116. [Google Scholar] [CrossRef] [PubMed]
  26. Yang, Z.; Wei, C.; Chai, Y.; Zhang, J.; Ji, H. Dibenzo-18-crown-6-functionalized organic nanotubes for the synergistic adsorption of dyes and phenols from aqueous solutions. J. Water Process Eng. 2022, 50, 103213. [Google Scholar] [CrossRef]
  27. Zawadiak, J.; Gilner, D.; Mazurkiewicz, R. Copper salt—Crown ether systems as catalysts for the oxidation of cumene with 1-methyl-1-phenylethylhydroperoxide to bis(1-methyl-1-phenylethyl)peroxide. Tetrahedron Lett. 1999, 40, 4059–4062. [Google Scholar] [CrossRef]
  28. Bianchini, E.; Pietrobon, L.; Ronchin, L.; Tortato, C.; Vavasori, A. Trifluoroacetic acid promoted hydration of styrene catalyzed by sulfonic resins: Comparison of the reactivity of styrene, n-hexene and cyclohexene. Appl. Catal. A Gen. 2019, 570, 130–138. [Google Scholar] [CrossRef]
  29. Kharlampidi, K.E.; Nurmurodov, T.S.; Ulitin, N.V.; Tereshchenko, K.A.; Miroshkin, N.P.; Shiyan, D.A.; Novikov, N.A.; Stoyanov, O.V.; Ziyatdinov, N.N.; Lapteva, T.V.; et al. Design of cumene oxidation process. Chem. Eng. Process. 2021, 161, 108314. [Google Scholar] [CrossRef]
  30. Dolan, E.D.; Lewis, R.M.; Torczon, V. On the local convergence of pattern search. SIAM J. Optim. 2003, 14, 567–583. [Google Scholar] [CrossRef]
Figure 1. The dependencies of the component concentrations of the reaction mixture in cumene oxidation versus time: dots are the experimental data, and lines are the calculation by the model; (a) ROOH; (b) ROH; (c) C6H5C(CH3) = CH2; (d) C6H5C(O)CH3; (e) C6H5OH.
Figure 1. The dependencies of the component concentrations of the reaction mixture in cumene oxidation versus time: dots are the experimental data, and lines are the calculation by the model; (a) ROOH; (b) ROH; (c) C6H5C(CH3) = CH2; (d) C6H5C(O)CH3; (e) C6H5OH.
Jcs 07 00060 g001aJcs 07 00060 g001b
Figure 2. The dependencies of the component concentrations of the reaction mixture in cumene hydroperoxide decomposition versus time: dots are the experimental data, and lines are the calculation by the model; (a) ROOH; (b) ROH; (c) C6H5C(CH3) = CH2; (d) C6H5C(O)CH3; (e) C6H5OH.
Figure 2. The dependencies of the component concentrations of the reaction mixture in cumene hydroperoxide decomposition versus time: dots are the experimental data, and lines are the calculation by the model; (a) ROOH; (b) ROH; (c) C6H5C(CH3) = CH2; (d) C6H5C(O)CH3; (e) C6H5OH.
Jcs 07 00060 g002aJcs 07 00060 g002b
Figure 3. The dependencies of cumene hydroperoxide accumulation versus time. Without catalystCa Sr Ba. G = 0.6 L/min, T = 393 K, P = 1 atm, [RH]0 = 6.19 mol/L, [ROOH]0 = 0.15 mol/L, [ROH]0 = 0.08 mol/L, [HCOOH]0 = 0.018 mol/L, [C6H5C(O)CH3]0 = 0.024 mol/L, and [Cat]0 = 1 mmol/L.
Figure 3. The dependencies of cumene hydroperoxide accumulation versus time. Without catalystCa Sr Ba. G = 0.6 L/min, T = 393 K, P = 1 atm, [RH]0 = 6.19 mol/L, [ROOH]0 = 0.15 mol/L, [ROH]0 = 0.08 mol/L, [HCOOH]0 = 0.018 mol/L, [C6H5C(O)CH3]0 = 0.024 mol/L, and [Cat]0 = 1 mmol/L.
Jcs 07 00060 g003
Figure 4. Time to reach the maximum concentration of cumene hydroperoxide depending on the temperature of cumene oxidation. Without catalystCa Sr Ba. G = 0.6 L/min, P = 1 atm, [RH]0 = 6.19 mol/L, [ROOH]0 = 0.15 mol/L, [ROH]0 = 0.08 mol/L, [HCOOH]0 = 0.018 mol/L, [C6H5C(O)CH3]0 = 0.024 mol/L, and [Cat]0 = 1 mmol/L.
Figure 4. Time to reach the maximum concentration of cumene hydroperoxide depending on the temperature of cumene oxidation. Without catalystCa Sr Ba. G = 0.6 L/min, P = 1 atm, [RH]0 = 6.19 mol/L, [ROOH]0 = 0.15 mol/L, [ROH]0 = 0.08 mol/L, [HCOOH]0 = 0.018 mol/L, [C6H5C(O)CH3]0 = 0.024 mol/L, and [Cat]0 = 1 mmol/L.
Jcs 07 00060 g004
Figure 5. The dependencies of criterion C (a), [ROOH]max (b), cumene conversion at tmax (c), and selectivity at tmax (d) versus cumene oxidation temperature. Without catalyst Ca Sr Ba. G = 0.6 L/min, P = 1 atm, [RH]0 = 6.19 mol/L, [ROOH]0 = 0.15 mol/L, [ROH]0 = 0.08 mol/L, [HCOOH]0 = 0.018 mol/L, [C6H5C(O)CH3]0 = 0.024 mol/L, and [Cat]0 = 1 mmol/L.
Figure 5. The dependencies of criterion C (a), [ROOH]max (b), cumene conversion at tmax (c), and selectivity at tmax (d) versus cumene oxidation temperature. Without catalyst Ca Sr Ba. G = 0.6 L/min, P = 1 atm, [RH]0 = 6.19 mol/L, [ROOH]0 = 0.15 mol/L, [ROH]0 = 0.08 mol/L, [HCOOH]0 = 0.018 mol/L, [C6H5C(O)CH3]0 = 0.024 mol/L, and [Cat]0 = 1 mmol/L.
Jcs 07 00060 g005
Figure 6. The dependencies of criterion C (a), tmax (b), [ROOH]max (c), cumene conversion at tmax (d), and selectivity at tmax (e) versus initial catalyst concentration.
Figure 6. The dependencies of criterion C (a), tmax (b), [ROOH]max (c), cumene conversion at tmax (d), and selectivity at tmax (e) versus initial catalyst concentration.
Jcs 07 00060 g006
Table 1. Cumene oxidation in the presence of various catalysts ([RH]0 = 0 mol/L).
Table 1. Cumene oxidation in the presence of various catalysts ([RH]0 = 0 mol/L).
CatalystT, KOxidation Time, hCumene
Conversion, %
Selectivity of the
Process According to CHP, %
Acetylacetonate Fe Fe(acac)3/NHPI/Phen [9]3332.58.5–5850–95
Carbon nanotubes [20]353824.188.4
Ni metal–organic frameworks [21]3637691
Co metal–organic frameworks [21]36374969
Zn metal–organic frameworks [21]3637395
Ca, Sr, and Ba complexes with dibenzo-18-crown-6 ether (results of this work)393660–7040–60
Table 2. Pre-exponential factor A and activation energy E in the Arrhenius equation k = Ae - E RT . (R = 8.31 J/(mol K); T is temperature, K).
Table 2. Pre-exponential factor A and activation energy E in the Arrhenius equation k = Ae - E RT . (R = 8.31 J/(mol K); T is temperature, K).
kA,
1/s is for Monomolecular Reactions,
L/(mol × s) is for Bimolecular Reactions,
L2/(mol2 × s) is for Trimolecular Reactions
E, J/mol
CaSrBaCaSrBa
k14.63 × 1043.57 × 1067.64 × 101455,00058,900130,000
k1’3.97 × 1042.20 × 1051.65 × 10570,10074,70069,000
k21.37 × 1031.18 × 1031.73 × 101829,00023,000139,500
k2’1.35 × 10204.01 × 10121.68 × 1015123,80063,30089,400
k36.07 × 10141.72 × 1031.25 × 1018136,40039,000132,300
k3’8.36 × 10192.21 × 10161.05 × 103107,60079,00035,000
k48.49 × 1032.36 × 1034.25 × 10719,00024,40078,200
k51.30 × 1051.10 × 1031.91 × 10338,50022,20010,400
k5’1.25 × 1032.57 × 1031.55 × 10424,30024,90049,400
k66.14 × 106106,500
k75.23 × 1071.16 × 10101.02 × 1017290015,000103,100
k89.27 × 10695,700
k99.97 × 1056.27 × 10148.87 × 10627,00093,20037,800
k101.28 × 10694,700
k111.54 × 1098.36 × 1071.94 × 10946,10036,60046,700
k129.60 × 101121,700
k131.43 × 101495,900
k143.35 × 10101.91 × 10132.66 × 101323,10040,40068,800
k156.34 × 101042,000
k162.58 × 10142.78 × 10131.44 × 1012250060032,500
k175.96 × 101224,400
k187.64 × 1084.38 × 10102.82 × 101816,60027,30089,300
k191.20 × 1073700
k22.31 × 10106.77 × 1091.33 × 10102700160012,200
k215.83 × 101360,200
k225.04 × 1076700
k238.82 × 1098700
k244.50 × 10662,100
k255.47 × 10198.32 × 10169.02 × 108107,60086,70035,500
k263.58 × 101281,900
k272.33 × 10117700
k284.99 × 1010420
k297.60 × 101221,100
k302.26 × 101359,300
k317.41 × 101136,200
k321.65 × 101163,400
k334.89 × 101299,100
k344.39 × 1082020
k351.12 × 10789,100
k361.81 × 1091.93 × 10141.17 × 10985,600119,00086,300
k373.88 × 10191.11 × 1052.66 × 1018145,30042,60085,000
k381.21 × 10583,600
k391.73 × 1051.98 × 10101.05 × 10470,400109,00016,300
k406.38 × 108102,200
k415.38 × 1091.20 × 1031.83 × 101924,700920072,800
k425.99 × 10675,100
k42’2.34 × 1012113,600
k437.10 × 10788,900
k442.94 × 10658,500
k451.32 × 1031.20 × 10138.85 × 101162,000130,000116,400
k463.53 × 1091.87 × 10103.83 × 10463,10021,20068,800
k479.36 × 1089.63 × 10122.56 × 10463,20091,70068,800
k481.26 × 10128.39 × 10162.87 × 106117,200147,50058,000
k491.25 × 10101.91 × 10102.26 × 101185,10086,20088,800
k502.17 × 10108.19 × 1031.24 × 10376,70028,50012,900
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Ulitin, N.V.; Novikov, N.A.; Lyulinskaya, Y.L.; Shiyan, D.A.; Tereshchenko, K.A.; Nurullina, N.M.; Denisova, M.N.; Mezhuev, Y.O.; Kharlampidi, K.E. The Effect of Ca, Sr, and Ba Chloride Complexes with Dibenzo-18-Crown-6 Ether as Catalysts on the Process Criteria for the Efficiency of Cumene Oxidation (the First Stage in the Chain of Polymer Composite Production). J. Compos. Sci. 2023, 7, 60. https://doi.org/10.3390/jcs7020060

AMA Style

Ulitin NV, Novikov NA, Lyulinskaya YL, Shiyan DA, Tereshchenko KA, Nurullina NM, Denisova MN, Mezhuev YO, Kharlampidi KE. The Effect of Ca, Sr, and Ba Chloride Complexes with Dibenzo-18-Crown-6 Ether as Catalysts on the Process Criteria for the Efficiency of Cumene Oxidation (the First Stage in the Chain of Polymer Composite Production). Journal of Composites Science. 2023; 7(2):60. https://doi.org/10.3390/jcs7020060

Chicago/Turabian Style

Ulitin, Nikolai V., Nikolay A. Novikov, Yana L. Lyulinskaya, Daria A. Shiyan, Konstantin A. Tereshchenko, Natalia M. Nurullina, Marina N. Denisova, Yaroslav O. Mezhuev, and Kharlampii E. Kharlampidi. 2023. "The Effect of Ca, Sr, and Ba Chloride Complexes with Dibenzo-18-Crown-6 Ether as Catalysts on the Process Criteria for the Efficiency of Cumene Oxidation (the First Stage in the Chain of Polymer Composite Production)" Journal of Composites Science 7, no. 2: 60. https://doi.org/10.3390/jcs7020060

Article Metrics

Back to TopTop