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IVESTIGATION OF THE PROCESS OF TARTARIC ACID SEPARATION ON AMBERLITE XAD2 IMPREGNATED WITH AMBERLITE LA-2 ¶1

Tartaric acid is one of the most valuable compounds that can be obtained from secondary wine products. The last are accumulating in big quantities at winemaking factories from Moldova. This work describes an investigation of the process of reactive ion-exchange separation of tartaric acid from model systems with macroreticular resin Amberlite XAD2 impregnated with liquid ion-exchanger Amberlite LA-2 in batch equipment. The condition of Amberlite XAD2 impregnation process was investigated. Freudlich and Langmuir equations were verified and values of enthalpy, entropy and Gibbs energy were calculated.

Chemistry Journal of Moldova. General, Industrial and Ecological Chemistry. 2012, 7 (2), 116-123 IVESTIGATION OF THE PROCESS OF TARTARIC ACID SEPARATION ON AMBERLITE XAD2 IMPREGNATED WITH AMBERLITE LA-2¶1 Natalia S. Marchitan Department of Industrial and Ecological Chemistry, Faculty of Chemistry and Chemical Technology, Moldova State University, 60 A. Mateevici str., MD 2009, Chisinau, Republic of Moldova e-mail: n_marchitan@yahoo.com, te/faxl: +373 22 737165 Abstract. Tartaric acid is one of the most valuable compounds that can be obtained from secondary wine products. The last are accumulating in big quantities at winemaking factories from Moldova. This work describes an investigation of the process of reactive ion-exchange separation of tartaric acid from model systems with macroreticular resin Amberlite XAD2 impregnated with liquid ion-exchanger Amberlite LA-2 in batch equipment. The condition of Amberlite XAD2 impregnation process was investigated. Freudlich and Langmuir equations were verified and values of enthalpy, entropy and Gibbs energy were calculated. Key words: reactive sorption, tartaric acid, Freudlich equation, Langmuir equation, thermodynamic constants. Introduction Classical technologies of organic compounds separation from aqueous streams possess several difficulties, which can be solved by application of reactive sorption. This procedure is a combination of reactive extraction and adsorption [1-5]. Impregnated ion-exchangers are obtained by physical incorporation of a selective extraction reagent into a porous adsorbent. The impregnated extractants manifest strong affinity towards polymeric resins, but, also, maintain its extractive properties (capacity and selectivity) as in liquid state [6-8]. The separation of the polar organic substance is performed during the contact between aqueous solution and impregnated ionites. It is obtained the complex between the solute and extractant. The reaction takes place in the pores of the resin, where the products remain [1-5]. In comparison to the reactive extraction, this procedure involves simpler technological equipment and operations, allows reduction of the total process time, does not need intensive agitation for increase the contact surface, avoids the emulsion formation, and can be used in case of small concentrations of the solute. Moreover, it is overcame basic disadvantage – low selectivity [5]. Impregnated resins with selective extractants were initially used for the separation of the metals from waste waters [2, 7, 9-10]. Later, this procedure was applied in water purification from organic compounds, and, finally, for their separation from other aqueous solutions [5, 11-14]. Besides, studies of organic acids recovery are of strong interest [3, 4, 15-17]. This work presents the study of the impregnation procedure of nonionic macroreticular resin Amberlite XAD2 with the solution of the secondary amine Amberlite LA-2 in organic solvent, and thermodynamic study of the reactive sorption of the tartaric acid on the obtained impregnated anionite. Experimental Section Materials The aqueous phase was prepared by dissolving tartaric acid (Reahim, Russia) in distilled water. Several solvents were used as inert diluents for amine organic phase – chloroform, butyl acetate, hexane (all from Reahim, Russia). The organic phase for impregnation was prepared by dissolving amine: Amberlite LA-2, tri-n-octylamine, tri-iso-octylamine (Sigma-Aldrich, Germany) and synthesized amines (N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(1methylenpirazyl)dodecylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(1-methylen-1,2,4-triazyl)dodecylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(4-methylenmorpholyl)dodecylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)N-(1-methylenpyrrolidyl)dodecylamine, N-(N,N-diethylamino-N-methylen)-N-(2,2,4,4,6,6-hexamethylhexanyl) dodecylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(1-methylenpyridyl)-dodecylamine, N-(N,N-dimethylaminoN-methylen)-N-(2,2,4,4,6,6-hexamethylhexanyl)dodecylamine, N,N,N-tri-iso-octylamine chloride, N-hydroxyethylN,N,N-trioctylammonium chloride and N,N,N,N-tetramethylheptylammonium bromide) in diluent. The synthesized tertiary amine and ammonium salts were obtained from commercial ones in laboratory of Organic Synthesize of Institute of Chemistry of ASM. Glacial acetic acid (Reactivul, Romania) and sodium metavadanate (Reahim, Russia) were used for determination of tartaric acid concentration. Methods Concentration determination of tartaric acid was realized by photometric method on spectrophotometer PD303 (APEL, Japan). For measurements 5 cm3 of analyzed solution were passed into 50 cm3 flask, 4 cm3 of sodium ¶ This article is an extended abstract of a communication presented at the Conference Ecological Chemistry 2012 116 Marchitan N./Chem. J. Mold. 2012, 7 (2), 116-123 metavanadate solution (5%) and 1 cm3 of glacial acetic acid were added, then flask was fitted with distilled water. Obtained solution is left for 15-20 min at dark for the formation of the stable color during 24 h. Measurements were done at 525 nm wave length (green filter) against a blank similarly prepared without tested solution [18]. Procedure The experimental procedure of the impregnation of the Amberlite XAD2 with Amberlite LA-2 consists of several stages. Initially, solid anionite is washed with acetone and distilled water to eliminate organic and inorganic impurities. Liquid amines are used without additional purification. Impregnation consists in immersion of the solid resin in solution of the liquid anionite in organic solvent. After 24 h, necessary to fulfill impregnation process, the excess of the organic substance is removed by addition of the distilled water to the obtained anionite and its exposition to the ultrasound with the frequency 35 kHz in ultrasound bath Sonica 1200M (Soltec, Italy) during 5 min. Another possibility is to pour out remained amine solution by washing of the impregnated anionite with the same solvent, used for the preparation of the amine solution. Anionites obtained by both methods do not differ by their properties. For further experiments dry ionexchanger was used. Determination of the reactive sorption performance of tartaric acid from model solution on obtained impregnated anionite was done as follows: 1 g of impregnated anionite is stirred with universal stirrer WU-4 (Premed, Poland) or agitator AVU-6s (Russia) with 50 cm3 of tartaric acid solution till the equilibrium is reached, and concentration of the tartaric acid is determined in the final solution [18]. Conditions of the impregnation process were determined from investigation of the next parameters: type of the amine (Amberlite LA-2, tri-n-octylamine, tri-iso-octylamine and synthesized amines), type of the solvent (hexane, chloroform, butylacetate), amine concentration in the impregnation solution, the volume of the solvent used in preparation of the impregnation solution and the time of impregnation. The impregnation performance was appreciated by determination of reactive sorption of the tartaric acid from model solution on impregnated anionite. In order to estimate equilibrium constants for the reactive sorption process of the tartaric acid on anionite Amberlite XAD2 impregnated with Amberlite LA-2, 0.5 g of the anionite were stirred with 50 cm3 of tartaric acid solution with the concentration between 0.33 g/dm3 and 6.99 g/dm3, with the magnetic stirrer for an hour (time enough to create equilibrium state). The contact between the phases was ensured in thermostat during the whole process till the equilibrium state. In this way there were estimated the isotherms of the sorption at 296 K, 300 K, 305 K and 313 K. Definition of Characteristic Parameters Reactive sorption at equilibrium qe (g/g) of the impregnated anionite is calculated by the formula: qe = (co − ce )⋅ V , (1) m where: m – mass of the dry ion-exchanger, g; V – tartaric acid solution volume, dm3; co – initial concentration of the tartaric acid in model solution, g/dm3; ce – concentration of the tartaric acid in model solution at equilibrium, g/dm3. The constants of equilibrium were determined applying Freundlich and Langmuir equations. For the determination of the constants KF and n, the data were used the Freundlich isotherm in logarithmic form: 1 ln qe = ln K F + ln ce n (2) where: KF – Freundlich equilibrium constant; n – empiric parameter of heterogeneity of the surface [19-24]. The reverse of the Langmuir equation takes linear dependency: 1 ce ce = + qe qm qm ⋅ K L (3) where: KL – Langmuir constant; qm – maximal specific adsorption (mg/g), correspondent to the space occupied by a monomolecular layer on the adsorbent surface [19-25]. The precision of the correlation was appreciated by correlation coefficient R2: 117 Chemistry Journal of Moldova. General, Industrial and Ecological Chemistry. 2012, 7 (2), 116-123 R =r 2 yx 2 yx 2 = i ( yi − y )(xi − x ) ( y i − y )2 i i 2 ( x i − x )2 (4) For the determination of the entropy and enthalpy through the graphic method was applied next form of the Van′t Hoff equation: ln K L = − Ho + RT So R (5) where: ΔHº – enthalpy, J/mol; ΔSº – entropy, J/(mol·K); R – universal constant of the ideal gas (8,314 J/(mol⋅K)), and T – temperature of the process realization [24, 26, 27]. q, mg/g Results and discussion The first stage of the determination of the conditions of impregnation process was amine selection. For this, there were prepared several impregnation solutions by dissolving 0.8 cm3 of amine in 3 cm3 of hexane. Next amines were used: Amberlite LA-2, tri-n-octylamine, tri-iso-octylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)-N(1-methylenpirazyl)dodecylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(1-methylen-1,2,4-triazyl)dodecylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(4-methylenmorpholyl)dodecylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)N-(1-methylenpyrrolidyl)dodecylamine, N-(N,N-diethylamino-N-methylen)-N-(2,2,4,4,6,6-hexamethylhexanyl) dodecylamine, N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(1-methylenpyridyl)dodecylamine, N-(N,N-dimethylamino-Nmethylen)-N-(2,2,4,4,6,6-hexamethylhexanyl)dodecylamine, N,N,N-tri-iso-octylamine chloride, N-hydroxyethyl-N,N,Ntrioctylammonium chloride and N,N,N,N-tetramethylheptylammonium bromide. One gram of Amberlite XAD2 were added to the amine solution, stirred and left for 24 h. 25 20 15 10 5 0 1 2 3 4 5 6 7 8 9 10 Amine Fig. 1. The effect of the nature of the amine used for the impregnation of Amberlite XAD2 on reactive sorption of the tartaric acid from aqueous solution (m(anionite) = 0.4 g; dp = 0.75 mm; V(AT) = 40 cm3; co(AT) = 3.46 g/dm3; τagit = 60 min; t = 23°C; n = 200 min-1) 1 – N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(1-methylenpirazyl)dodecylamine, 2 – N-(2,2,4,4,6,6-hexamethylhexanyl)-N(1-methylen-1,2,4-triazyl) dodecylamine, 3 – N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(4-methylenmorpholyl)dodecylamine, 4 – N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(1-methylenpyrrolidyl) dodecylamine, 5 – N-(N,N-diethylamino-N-methylen)-N(2,2,4,4,6,6-hexamethylhexanyl) dodecylamine, 6 – N-(2,2,4,4,6,6-hexamethylhexanyl)-N-(1-methylenpyridyl) dodecylamine, 7 – N-(N,N-dimethylamino-N-methylen)-N-(2,2,4,4,6,6-hexamethylhexanyl)dodecylamine, 8 – N-(2,2,4,4,6,6-hexamethylhexanyl) dodecylamine (Amberlite LA-2), 9 – N,N,N-tri-iso-octylamine chloride, 10 – N-hydroxyethyl-N,N,N-trioctylammonium chloride Tests of the obtained anionites revealed that maximal performance of reactive sorption of the tartaric acid was received for anionites impregnated with Amberlite LA-2 and (N,N-dimethylamino-N-methylen)-N-(2,2,4,4,6,6hexamethylhexanyl)dodecylamine. During separation with anionites impregnated with tri-n-octylamine, tri-isooctylamine, and N,N,N,N-tetramethylheptylammonium bromide was detected formation of the emulsion during stirring, caused by transfer of the amines from resin to aqueous solution, so they were excluded from following investigations. Thus, it was proposed to use Amberlite LA-2 amine for the impregnation of Amberlite XAD2, because the synthesis of (N,N-dimethylamino-N-methylen)-N-(2,2,4,4,6,6-hexamethylhexanyl)dodecylamine involves extra expenses, though process performance was unchangeable. 118 q, mg/g Marchitan N./Chem. J. Mold. 2012, 7 (2), 116-123 24 23,5 23 22,5 22 21,5 hexane chloroform butylacetate Solvent Fig. 2. The effect of amine solution solvent on reactive sorption of the tartaric acid from aqueous solution (m(anionite) = 1.0 g; dp = 0.75 mm; V(AT) = 50 cm3; co(AT) = 3.48 g/dm3; τagit = 60 min; t = 28°C; n = 200 min-1) As solvents for impregnation were used: butylacetate, chloroform and hexane. According to the figure 2, amine solution preparation using butylacetate allows obtaining of the impregnated anionite with maximal sorption. Efficiency of the tartaric acid separation process with ion-exchanger prepared on basis of Amberlite LA-2 solution in chloroform was lower than in the case of other solvents. In addition, the separation process of the excess of impregnation solution becomes difficult, because chloroform has a higher density than water. Thus, hexane was used as solvent in the next experiments because the impregnated resins obtained from amine solution in hexane and from solution in butylacetate had nearly similar reactive sorption, but the separation of hexane was easier and faster, due to low boiling point (69°C). Amine concentration in impregnation solution varied from 5% to 60%. After, processing and testing of the impregnated anionite, there were obtained the results, presented in figure 3. q, mg/g 25 20 15 10 5 0 0 10 20 30 40 50 60 w, % 70 Fig. 3. The influence of the amine solution concentration used for impregnation on reactive sorption of tartaric acid by impregnated anionites (m(anionite) = 0.5 g; dp = 0.75 mm; V(AT) = 50 cm3; co(AT) = 0.8 g/dm3; τagit = 60 min; t = 28°C; n = 150 min-1) The increase of the amine solution concentration used for impregnation influenced positively anionite reactive sorption up to the concentration 30%, and then decreased it. The explication is that the quantity of the fixed amine closes the access of the aqueous solution of tartaric acid to the resin pores. The quantity of the solvent necessary for preparation of the amine solution also influenced the efficiency of the impregnation process and, further, of the tartaric acid separation. It was taken into account that the ration between amine content and resin weight must be constant, varying only solvent’s volume. The organic solution with following volume ratio between Amberlite LA-2 and hexane were prepared: 1:1, 1:2, 1:3, 1:4 and 1:5. They corresponded to the amine solutions with concentration 56.23%; 39.11%; 29.99%; 24.31% and 20.44%, respectively. The quantities of the solutions used for impregnation were different (0.754 g; 1.084 g; 1.414 g; 1.744 g and 2.074 g). 119 q, mg/g Chemistry Journal of Moldova. General, Industrial and Ecological Chemistry. 2012, 7 (2), 116-123 30 25 20 15 10 5 0 1:1 1:2 1:3 1:4 1:5 V(amine):V(solvent), cm 3/cm 3 Fig. 4. The effect of the volume ratio between Amberlite LA-2 and hexane in impregnation solution on reactive sorption of the tartaric acid (m(anionite) = 0.5 g; dp = 0.75 mm; V(AT) = 50 cm3; co(AT) = 0.95 g/dm3; τagit = 15 min; t = 27°C; n = 150 min-1) q, mg/g From the analysis of the figure 4 it is observed that the most adequate volume ratio between the amine and the solvent in impregnation solution was 1:3, corresponding to the solution of Amberlite LA-2 with concentration 30%. This fact confirms once more experimental data received during determination of the impregnation solution concentration. Amberlite XAD2 was impregnated with 30% solution of Amberlite LA-2 for 1, 2, 4, 6, 8, 14, 16, 20 and 24 h. It was shown that for the finalization of the impregnation was necessary 2 h. The extension of procedure up to 12 h did not modify properties of the obtained anionite. Impregnation over 16 h led to insignificant decrease of obtained ion exchangers sorption, that can be explained by accumulation of the amine excess in resin pores (fig. 5). The anionite resulted after 24 h of Amberlite XAD2 impregnation did not differ by their properties from that obtained after 4 days of impregnation. 22 21 20 19 18 17 16 0 2 4 6 8 10 12 14 16 18 20 22 24 26 t, h Fig. 5. The influence of the time of impregnation process on tartaric acid sorption on impregnated anionite (m(anionite) = 0.5 g; dp = 0.75 mm; V(AT) = 50 cm3; co(AT) = 0.92 g/dm3; τagit = 60 min; t = 28°C; n = 150 min-1) Then, Freundlich and Langmuir isotherms for obtained anionite were verified. Isotherms of the reactive sorption of tartaric acid on Amberlite XAD2 impregnated with Amberlite LA-2 are present in figure 6. qe, g/g 0,03 0,025 0,02 0,015 T = 296 K T = 300 K 0,01 T = 305 K 0,005 T = 313 K 0 0 1 2 3 4 5 6 7 8 ce, g/l Fig. 6. Isotherms of reactive sorption of tartaric acid on Amberlite XAD2 impregnated with Amberlite LA-2 120 Marchitan N./Chem. J. Mold. 2012, 7 (2), 116-123 Experimental data were processed according to Freundlich and Langmuir equations, and the results were presented in table 1. In figures 7 and 9 was illustrated experimental validation of the Freundlich and Langmuir equations for the reactive sorption of tartaric acid on Amberlite XAD2 impregnated with Amberlite LA-2 at 296 K. In the same way were analyzed all isotherms. ln q e 3,5 y = 0,295x + 0,5231 R2 = 0,5944 3 2,5 2 1,5 1 4 5 6 7 8 9 ln ce 10 ce/q e, g/l Fig. 7. Experimental validation of the Freundlich equation for the reactive sorption of the tartaric acid on Amberlite XAD2 impregnated with Amberlite LA-2 at 296 K 400 y = 45,003x + 24,301 R2 = 0,9902 350 300 250 200 150 100 50 0 0 1 2 3 4 5 6 7 ce, g/l 8 Fig. 8. Experimental validation of the Langmuir equation for the reactive sorption of the tartaric acid on Amberlite XAD2 impregnated with Amberlite LA-2 at 296 K Table 1 Constants of Freundlich and Langmuir isotherms T, K 296 300 305 313 Freundlich n 3,3898 2,7809 2,1925 1,4575 KF 1,6872 1,1264 0,5044 0,0727 Langmuir R2 0,5944 0,6207 0,7096 0,9143 KL, L/g 1,8536 1,8079 1,0484 0,3253 qm, g/g 0,0222 0,0248 0,0270 0,0383 R2 0,9902 0,9807 0,9637 0,9259 Comparison of the values of the correlation coefficients demonstrated that Langmuir equation verify experimental data in a better way. The values of the maximal specific reactive sorption, calculated with the same equation, increased at the same time with the temperature, which meant the interaction between tartaric ions and impregnated resin was an endothermic process. Langmuir isotherm is mostly adequate for adsorption on energetic homogeneous surfaces, accompanied with the reaction [19-23]. Due to the established hypotheses, it allowed, after verification, determination of thermodynamic values ΔGº, ΔHº, ΔSº (table 2). 121 Chemistry Journal of Moldova. General, Industrial and Ecological Chemistry. 2012, 7 (2), 116-123 Table 2 Calculated thermodynamic constants ΔGº, J/mol ΔHº, J/mol -1518,83 -78850,18 -1477,09 -119,86 2922,59 T, K 296 300 305 313 ΔSº, J/(mol·K) -261,26 -257,91 -258,13 -261,25 ln K Graphic dependency between the constant of equilibrium and the temperature allows estimating enthalpy and entropy of the tartaric acid separation process on Amberlite XAD2 impregnated with Amberlite LA-2. 1 y = 9,9252x - 32,683 R2 = 0,9255 0,5 0 3,15 -0,5 3,2 3,25 3,3 3,35 3,4 1000/T, K-1 -1 -1,5 Fig. 9. The dependency of the natural logarithm of equilibrium constant (ln K) of the tartaric acid reactive sorption process on Amberlite XAD2 resin impregnated with Amberlite LA-2 on temperature (1000/T) Enthalpy value determined by graphic method was -82524.07 J/mol, while entropy value -271.75 J/(mol·K). Differences between the calculated and graphically determined results were 4.45 %. ΔGº represents modification of the free energy in standard state during the ion-exchange and sorption or desorption of the solvent and dissolved electrolyte [26, 27]. Negative value of Gibbs free energy modification denote spontaneous process of ion-exchange. But, increase of ΔGº along with temperature shows its negative effect on the stability of the bonds between tartaric acid and ion-exchanger, which was confirmed by the decrease of equilibrium constant. Negative value of the enthalpy variation indicates an exothermic process, which is an additional argument. The selectivity of the sorption process characterized by negative value of the thermodynamic potential, is determined by the significant decrease of the entropy. This process represents the increasing of the energy of interaction between selectively fixed ions on the ionite, in comparison to the interaction energy of ionite with concurrent substituted ions, thus the complex between tartaric acid ion and anionite became more ordered. System enthalpy variation in case of ion-exchange for diluted solutions was caused by the variation of the energy of interactions between contra-ions and ionite. Generally, bond energy between the ions of organic substances and ionexchangers is lower than between simple monovalent ions of hydrogen, chloride or metal ions (the influence of ion radius). Thus, the values of the thermodynamic potential, enthalpy and entropy support the existence of supplementary interactions, e.g., van der Waals bonds or hydrophobic interactions [27]. Conclusions The investigation revealed that for the impregnation of macroporous resin Amberlite XAD2 should be used Amberlite LA-2 amine, in following conditions: solvent – hexane, ratio between amine volume and solvent volume was 1:3, the concentration of amine solution in hexane 30% and impregnation time at least 2 h. Tartaric acid reactive sorption process on the obtained impregnated anionite verifies Langmuir equation with correlation higher than 0.92, and thermodynamic constants denotes the presence of exothermal process, associated with chemical reaction. References [1]. Warshawsky, A. South African Patent Application 71/5637, 1971. [2]. Tavlarides, L. L.; Bae, J. H.; Lee, C. K. Solvent extraction, membranes, and ion-exchange in hydrometallurgical dilute metals separation. Separation Science and Technology. 1987, 22(2-3); pp. 581-617. 122 Marchitan N./Chem. J. Mold. 2012, 7 (2), 116-123 [3]. [4]. [5]. [6]. [7]. [8]. [9]. [10]. [11]. [12]. [13]. [14]. [15]. [16]. [17]. [18]. 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