ISSN 1451 - 9372(Print) ISSN 2217 - 7434(Online) JULY-SEPTEMBER 2013 Vol.19, Number 3, 321-460 www.ache.org.rs/ciceq Journal of the Association of Chemical Engineers of Serbia, Belgrade, Serbia EDITOR-In-Chief Vlada B. Veljković Faculty of Technology, University of Niš, Leskovac, Serbia E-mail: veljkovicvb@yahoo.com ASSOCIATE EDITORS Branko Bugarski Jonjaua Ranogajec Srđan Pejanović Department of Chemical Engineering, Faculty of Technology and Metallurgy, University of Belgrade, Belgrade, Serbia Faculty of Technology, University of Novi Sad, Novi Sad, Serbia Department of Chemical Engineering, Faculty of Technology and Metallurgy, University of Belgrade, Belgrade, Serbia Milan Jakšić ICEHT/FORTH, University of Patras, Patras, Greece EDITORIAL BOARD (Serbia) Đorđe Janaćković, Sanja Podunavac-Kuzmanović, Viktor Nedović, Sandra Konstantinović, Ivanka Popović Siniša Dodić, Zoran Todorović, Olivera Stamenković, Marija Tasić, Jelena Avramović ADVISORY BOARD (International) Dragomir Bukur Ljubisa Radovic Texas A&M University, College Station, TX, USA Pen State University, PA, USA Milorad Dudukovic Peter Raspor Washington University, St. Luis, MO, USA University of Ljubljana, Ljubljana, Slovenia Jiri Hanika Constantinos Vayenas Institute of Chemical Process Fundamentals, Academy of Sciences of the Czech Republic, Prague, Czech Republic University of Patras, Patras, Greece Maria Jose Cocero Xenophon Verykios University of Valladolid, Valladolid, Spain University of Patras, Patras, Greece Tajalli Keshavarz Ronnie Willaert University of Westminster, London, UK Vrije Universiteit, Brussel, Belgium Zeljko Knez Gordana Vunjak Novakovic University of Maribor, Maribor, Slovenia Columbia University, New York, USA Igor Lacik Dimitrios P. Tassios Polymer Intitute of the Slovak Academy of Sciences, Bratislava, Slovakia Denis Poncelet ENITIAA, Nantes, France National Technical University of Athens, Athens, Greece Hui Liu China University of Geosciences, Wuhan, China FORMER EDITOR (2005-2007) Professor Dejan Skala University of Belgrade, Faculty of Technology and Metallurgy, Belgrade, Serbia Journal of the Association of Chemical Engineers of Serbia, Belgrade, Serbia Vol. 19 Belgrade, July-September 2013 Chemical Industry & Chemical Engineering Quarterly (ISSN 1451-9372) is published quarterly by the Association of Chemical Engineers of Serbia, Kneza Miloša 9/I, 11000 Belgrade, Serbia Editor: Vlada B. 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Box 3503, 11120 Belgrade, Serbia Abstracting/Indexing: Articles published in this Journal are indexed in Thompson Reuters products: Science Citation TM Index - Expanded - access via Web of ® SM Science , part of ISI Web of Knowledge No. 3 CONTENTS Hassan Golmohammadi, Abbas Rashidi, Seyed Jaber Safdari, Prediction of ferric iron precipitation in bioleaching process using partial least squares and artificial neural network ............................................................................... 321 A.C. Arvadiya, P.P. Dahivelker, Development and validation of novel RP-UPLC method for estimation of atropine sulphate in pharmaceutical dosage form ........................... 333 Arkan Jasim Hadi. Ghassan Jasim Hadi, Ghazi F. Najmuldeen, Iqbal Ahmed, Syed F. Hasany, Gas–liquid equilibrium prediction of system CO2-aqueous ethanol at moderate pressure and different temperatures using PR-EOS .............................................................................. 339 S.E. Moradi, J. Khodaveisy, R. Dashti, Removal of anionic surfactants by sorption onto aminated mesoporous carbon................................................................................. 347 Xiao-Qin Xiong, Ke-Jing Huang, Chun-Xuan Xu, Chun-Xue Jin, Qiu-Ge Zhai, Glassy carbon electrode modified with poly(taurine)/TiO2-graphene composite film for determination of acetaminophen and caffeine ................... 359 Jelena Đ. Marković, Nataša Lj. Lukić, Aleksandar I. Jokić, Bojana B. Ikonić, Jelena D. Ilić, Branislava G. Nikolovski, 2D simulation and analysis of fluid flow between two sinusoidal parallel plates using lattice Boltzmann method................................................................................ 369 S. Ramesh, R. Muthuvelayudham, R. Rajesh Kannan, T. Viruthagiri, Response surface optimization of medium composition for xylitol production by Debaryomyces hansenii var. hansenii using corncob hemicellulose hydrolysate ......................................................................... 377 Saša Ž. Drmanić, Jasmina B. Nikolić, Aleksandar D. Marinković, Gavrilo M. Šekularac, Bratislav Ž. Jovanović, The effects of solvents and structure on the electronic absorption spectra of the isomeric pyridine carboxylic acid N-oxides ...................................................................... 385 Hadi Baseri, Ali Haghighi-Asl, Mohammad Nader Lotfollahi, thermodynamic modeling of solid solubility in supercritical carbon dioxide: comparison between mixing rules .................................................................................... 389 S. Nadeem, Arshad Riaz, R. Ellahi, Peristaltic flow of a Jeffrey fluid in a rectangular duct having compliant walls ................ 399 Mohammad Ramezani, Navid Mostoufi, Mohammad Reza Mehrnia, Effect of hydrodynamics on kinetics of gluconic acid enzymatic production in bubble column reactor ................................................................................. 411 Contents continued Wei Li, Jinhui Peng, Shenghui Guo, Libo Zhang, Guo Chen, Hongying Xia, Carbothermic reduction kinetics of ilmenite concentrates catalyzed by sodium silicate and microwave-absorbing characteristics of reductive products .............................................................................. 423 Yu Sun, Shuangshuang Xu, Yanling Geng, Xiao Wang, Tianyou Zhang, Isolation and purification of lignans from Schisandra chinensis by combination of silica gel column and high-speed counter-current chromatography ................................................................................. 435 Husein Dibaei Asl, Majid Abdouss, Mahmoud Torabi Angaji, Aminoddin Haji, Surface and mechanical properties of polypropylene/clay nanocomposite ..................................... 441 A. Abdallah El Hadj, C. Si-Moussa, S. Hanini, M. Laidi, Application of PC-SAFT and cubic equations of state for the correlation of solubility of some pharmaceutical and statin drugs in sc-CO2......................................................... 449 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 321−331 (2013) HASSAN GOLMOHAMMADI1 ABBAS RASHIDI2 SEYED JABER SAFDARI1 1 Nuclear Science and Technology Research Institute, AEOI, Tehran, Iran 2 Department of Chemical Engineering, Faculty of Engineering, University of Mazandaran, Babolsar, Iran SCIENTIFIC PAPER UDC 66:004.8 DOI 10.2298/CICEQ120403066G CI&CEQ PREDICTION OF FERRIC IRON PRECIPITATION IN BIOLEACHING PROCESS USING PARTIAL LEAST SQUARES AND ARTIFICIAL NEURAL NETWORK A quantitative structure-property relationship (QSPR) study based on partial least squares (PLS) and artificial neural network (ANN) was developed for the prediction of ferric iron precipitation in bioleaching process. The leaching temperature, initial pH, oxidation/reduction potential (ORP), ferrous concentration and particle size of ore were used as inputs to the network. The output of the model was ferric iron precipitation. The optimal condition of the neural network was obtained by adjusting various parameters by trial-and-error. After optimization and training of the network according to back-propagation algorithm, a 5-5-1 neural network was generated for prediction of ferric iron precipitation. The root mean square error for the neural network calculated ferric iron precipitation for training, prediction and validation set were 32.860, 40.739 and 35.890, respectively, which were smaller than those obtained by the PLS model (180.972, 165.047 and 149.950, respectively). The obtained results reveal the reliability and good predictivity of the neural network model for the prediction of ferric iron precipitation in bioleaching process. Keywords: quantitative structure-property relationship; ferric iron precipitation; bioleaching process; partial least squares; artificial neural network. Bioleaching employs the oxidation ability of bacteria to dissolve metal sulphides and help the extraction and recovery of valuable and base metals from main ores and concentrates [1,2]. Metal-winning processes derived from the activity of microorganisms propose a possibility to attain metal ions from mineral resources not available by traditional techniques. Microbes such as bacteria and fungi change metal compounds into their water-soluble types and are biocatalysts of this process called microbial leaching or bioleaching [3,4]. Recently, Acidithiobacillus ferrooxidans were believed to be the common significant microorganisms in the bioleaching of metal ions from ores [5]. Acidithiobacillus ferrooxidans is an acidophilic chemolithoautotrophic proteobacterium that achieves Correspondence: H. Golmohammadi, Nuclear Science and Technology Research Institute, AEOI, P.O. Box 11365-3486, Tehran, Iran. E-mail: Hassan.gol@gmail.com Paper received: 3 April, 2012 Paper revised: 20 June, 2012 Paper accepted: 20 June, 2012 its energy from the oxidation of ferrous iron, elemental sulfur, or partially oxidized sulfur compounds [6]. Owing to its capacity of oxidation, Acidithiobacillus ferrooxidans has abundant industrial appliances in biohydrometallurgy. The most important applications can be established in the field of mining [7] where the oxidative effects are utilized for the bioleaching of different metals such as copper from minerals like pyrite or chalcopyrite [8,9] or even uranium [10]. The mechanism of uranium extraction assisted by the indirect oxidation purpose of this microbe is probably as follows: UO2 + Fe2(SO4)3 → UO2SO4 + 2FeSO4 4+ 3+ 6+ U + 2Fe → U + 2Fe 2+ (1) (2) Uranium is barely soluble in an aqueous environment when it is in the +4 oxidation state; however, in an acidic medium the ferric iron oxidizes U4+ to U6+, which is easily dissolved. As a conjugate reaction to the oxidation of U4+, the ferric iron reduces to ferrous iron and through the oxidation function of Acidithiobacillus ferrooxidans it is re-oxidized back to the ferric state which is then able to continue oxidizing U4+ to U6+. 321 H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… Temperature and pH of leaching solution can vary widely in the completeness of time. In addition, as the values of this parameter increase, ferric iron precipitation increases and consequently the leaching efficiency reduce. Therefore, it is very important to predict ferric iron concentration recycled by a comprehensive model for the design, monitoring and organization of bioleaching operations. As an alternative to physical models, artificial neural networks (ANNs) are a valuable estimate tool. Up to now, numerous applications of ANN models in the engineering area were reported. For example, Laberge et al. applied ANN to predict the metal (Cu, Zn and Cd) solubilization percentages in municipal sludge treated with a continuous bioleaching process [11]. Jorjani et al. used ANN to estimate the effects of operational parameters on the organic and inorganic sulfur removal from coal by sodium butoxide [12]. Acharya and co-workers developed a neural network to model the extent of sulphur removal from three types of coal using native cultures of Acidithiobacillus ferrooxidans [13]. Diamond et al. utilized ANN for the Study of pH on the fungal treatment of red mud [14]. Nikhil et al. employed ANN for prediction of H2 production rates in a sucrose-based bioreactor system [15]. They also modeled the performance of a biological Fe2+ oxidizing fluidized bed reactor (FBR) by a popular neural network-back-propagation algorithm under different operational conditions [16]. Yetilmezsoy and Demirel used a three-layer artificial neural network (ANN) model to predict the efficiency of Pb(II) ions removal from aqueous solution by Antep pistachio (Pistacia vera L.) shells based on 66 experimental sets obtained in a laboratory batch study [17]. Daneshvar et al. employed an artificial neural network (ANN) to model decolorization of textile dye solution containing C.I. Basic Yellow 28 by electrocoagulation process [18]. Sahinkaya and co-workers developed an artificial neural network model for estimation of the performance of a fluidized-bed reactor (FBR) based sulfate reducing bioprocess and control the operational conditions for improved process performance [19]. Sahinkaya also modeled the biotreatment of zinc-containing wastewater in a sulfidogenic CSTR by using artificial neural network [20]. Thus, to successfully extract the costly metals from the minerals, the suitable process and control of bioleaching purposes have become very essential. In relation to recent considerations, the dissolution of metals happens only chemically with the assist of ferric ions, which operate as oxidizing agents. Superior control of bioleaching may be acquired by using a strong model to predict convinced key factors derived 322 CI&CEQ 19 (3) 321−331 (2013) from past surveillances [21]. Models rooted in ANNs may be efficiently employed in bioleaching applications and very helpful at arresting the nonlinear correlations existing between variables in complex systems like bioleaching. The main aim of this investigation is using this aptitude of artificial neural network for prediction of ferric iron precipitation in bioleaching process. In this study, an artificial neural network method using the back-propagation algorithm was proposed for the prediction of ferric iron precipitation in uranium bioleaching process under different operational conditions. MATERIAL AND METHODS Uranium ores The uranium ores used in the experiments was supplied by the Nuclear Science and Technology Research Institute, AEOI. The ore was ground using mortar and then sieved. The particle size of the sieved material ranged from 70 to 500 µm, with an average particle size of 100±10 µm. Microorganism and culture The medium for Acidithiobacillus ferrooxidans growth was 9K medium which is a mixture of mineral salts ((NH4)2SO4, 3.0 g/l, K2HPO4, 0.5 g/l, MgSO4⋅7H2O, 0.5 g/l, KCl, 0.1 g/l and Ca(NO3)2, 0.01g/l). FeSO4⋅7H2O was added as energy source. The pH of the medium was adjusted to 2.0 using 2.0 M H2SO4. The culture was cultivated at 35 °C for 2-3 days before centrifugation. The yield cells of Acidithiobacillus ferrooxidans were suspended in a fresh solution of the mineral salt medium for the preparation of the bacterial concentrate [22]. Bioleaching experiments The experiments were performed in 250 ml Erlenmeyer flasks containing 5 g of ore and 100 ml of 9K medium. Erlenmeyer flasks covered with hydrophobic cotton to admit oxygen but reduce water loss through evaporation. Control experiments were carried out without bacteria and with 2% bactericide agent (formaldehyde). The concentrations of Fe were 2 and 4 g/l using FeSO4⋅7H2O. Each experiment was accomplished twice under same standard conditions at 30-40 °C, 180 rpm shaking speed and pH 2.0 [23]. A known amount of sample was drawn at 6 days interval for analysis of Iron. The pH of the leach solution was maintained daily with 2 M sulfuric acid. The oxidation/reduction potential (ORP) was measured against saturated calomel electrode (SCE). H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… Analytical procedures Total iron was analyzed using the PG T80+ UV/Vis spectrometer according to Karamanev method [24]. The ferrous iron concentration was determined using PG T80+ UV/Vis spectrometer by the modified colorimetric orthophenantroline method [25]. A Metrohm pH meter (model 827) with a combined glass electrode was used for pH measurements. The changes in oxidation/reduction potential (ORP) were monitored using an ORP meter (Metrohm model 827). Partial least squares model for the prediction of ferric iron precipitation PLS is a familiar multivariate method [26-28], which provides a stepwise solution for a regression model. It extracts principal component-like latent variables from original independent variables (predictor variables) and dependent variables (response variables), respectively. Assume that X characterizes independent variables (X is a matrix) and Y represents dependent variables (Y is a vector). Then a brief description of computations is given as follows: X = TPT + E T Y = QS + F (3) (4) The matrices E and F include residual for X and Y, respectively. T and P are score and loading matrices associated with the X, Q and S are the score and loading of Y and superscript T indicates the transposed matrix. The relationship between scores and dependent variable is obtained from: Y = TBQT + F (5) where B is the matrix of the regression coefficient achieved by a least squares procedure. The PLS algorithm used in this study was the singular value decomposition (SVD)-based PLS. This algorithm was proposed by Lobert et al. in 1987 [29]. A concise discussion of the SVD-based PLS algorithm can be found in the literature [30-32]. The program of PLS modeling based on SVD was written with MATLAB 7 in our laboratory [33]. Artificial neural network model for the prediction of ferric iron precipitation An artificial neural network is a kind of artificial intelligence that emulates some purpose of the human brain. Neural networks are general-purpose computing techniques that can solve complex nonlinear problems. The network comprises abundance of simple processing elements linked to each other by weighted connections along with a specified architecture. These networks learn from the training data by CI&CEQ 19 (3) 321−331 (2013) altering the connection weights [34]. A detailed explanation of the theory behind a neural network has been sufficiently described elsewhere [35-37]. Therefore, only the points related to this work are illustrated here. An essential procession element of an ANN is a node. Each node has a series of weighted inputs, Wij, and performs as a summing point of weighted input signals. The summed signals pass through a transfer function that may be in sigmoidal form. The output of node j, Oj , is given by Eq.(6): Oj = 1/(1 + exp(-X)) (6) where X is defined by the following equation: X = W ij Oi + B j (7) In Eq. (7), Bj is a bias term, Oi is the output of the node of the previous layer and Wji represents the weight between the nodes of i and j. A feed-forward neural network consists of three layers. The first layer (input layer) consists of nodes and operates as an input buffer for the data. Signals introduced to the network, with one node per element in the sample data vector, pass through the input layer to the layer called the hidden layer. Each node in this layer sums the inputs and forwards them through a transfer function to the output layer. These signals are weighted and then pass to the output layer. In the output layer the processes of summing and transferring are repeated. The output of this layer now signifies the calculated value for the node k of the network. As well as the network topology, a significant constituent of nearly all neural networks is a learning rule. A learning rule permits the network to alter its connection weights so as to correlate given inputs with corresponding outputs. The training of the network has been performed by using a back-propagation algorithm, in which the network reads inputs and outputs from an appropriate data set (training set) and iteratively calculates weights and biases to facilitate decrease the sum of squared dissimilarities between predicted and target values. The training is stopped when the error in prediction achieves a preferred level of accuracy. However, if the network is gone to train too long, it will overtrain and misplace the aptitude to prediction. In order to avoid overtraining, the predictive recital of the trained ANN is controlled by running the back-propagation algorithm on a data set not used in training. Neural networks are rooted in the principle that an extremely unified system of effortless processing elements can learn intricate interrelationships between independent and dependent variables. The perfor- 323 H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… mance and properties of such a network is reliant on the computational elements, especially the weights and the transfer function, in addition to the net topology. Usually the network topology and the transfer function are particular in advance and are kept fixed, so just the weights of the synaptic connections and the number of neurons in the hidden layer need to be evaluated. The error function should be minimized so that the neural network accomplishes the finest performance. Dissimilar algorithms have been grown to minimize the error function. The most traditional is the so-called back-propagation (BP) algorithm, which belongs to the group of supervised learning methods. The error at the output layer in a BP neural network propagates rearward to the input layer during the hidden layer in the network to acquire the final beloved output. The gradient descent technique is employed to compute the weights of the network and regulate the weights of interconnections to minimize the output error. In this work, multi layered feed forward neural networks were used, which utilized the algorithm of back-propagation of errors and a gradient-descent technique, known as the “delta rule” [38,39] for the adjustment of the connection weights (further called BP networks). BP networks include one input layer, one (or possibly several) hidden layer(s) and an output layer. The number of nodes in the input and output layers are described by the difficulty of the problem being solved. The input layer collects the experimental information and the output layer encloses the response sought. The hidden layer codes the information attained from the input layer, and transports it to the output layer. The number of nodes in the hidden layer may be considered as an adjustable factor. In the present work, an ANN program was written with MATLAB 7. This network was feed-forward fully connected and had three layers with tangent sigmoid transfer function (tansig) at the hidden layer and linear transfer function (purelin) at the output layer. The operational conditions of the bioleaching process were used as inputs of the network and its output signal represents the ferric iron precipitation. Therefore, this network has five nodes in input layer and one node in output layer. The value of each input was divided into its mean value to bring them into the dynamic range of the sigmoidal transfer function of the network. The initial values of weights were randomly selected from a uniform allocation that ranged between -0.3 to +0.3 and the initial values of biases were set to be 1. These values were optimized during the network training. The back-propagation algorithm was used for the training of the network. Before training, the network parameters would be 324 CI&CEQ 19 (3) 321−331 (2013) optimized. These parameters are: number of nodes in the hidden layer, weights and biases learning rates and the momentum. Procedures for the optimization of these descriptors were reported elsewhere [38,39]. Then the optimized network was trained using a training set for adjustment of weights and biases values. To maintain the predictive authority of the network at an enviable level, training was stopped when the value of error for the prediction set started to increase. Since the prediction error is not a good evaluation of the generalization error, the prediction potential of the model was assessed on a third set of data, named validation set. Experiments in the validation set were not used during the training process and were reserved to evaluate the predictive power of the generated ANN. Evaluation of the predictive ability of a QSPR model For the optimized QSPR model, numerous parameters were chosen to test the prediction capability of the model. A real QSPR model may have a high predictive aptitude, if it is close to ideal one. This may involve that the correlation coefficient R between the experimental (actual) y and predicted y properties must be close to 1 and regression of y against y or y against y through the origin, i.e., y r 0 = ky and y r 0 = k ' y , respectively, should be illustrated by at least either k or k ' close to 1 [40]. Slopes k and k ' are calculated as follows: k = y i yi yi2 (8) y i yi y i2 (9) k'= The criteria formulated above may not be adequate for a QSPR model to be really predictive. Regression lines through the origin defined by y r 0 = ky and y r 0 = k ' y (with the intercept set to one) should be close to optimum regression lines y r = ay + b and y r = a ' y + b ' (b and b ' are intercepts). Correlation coefficients for these lines R 02 and R '02 are calculated as follows: R02 = 1 − ( yi − y ir 0 )2 ( yi − y )2 (10) R '02 = 1 − ( y i − yir 0 )2 ( y i − y )2 (11) where y and y are the average values of the observed and predicted properties, respectively, and the summations are over all n compounds in the validation set. H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… A difference between R2 and R 02 values ( Rm2 ) desires to be studied to examine the prediction potential of a model [41]. This term was defined in the following manner: Rm2 = R 2 (1− R 2 − R02 ) (12) Finally, the following criteria for evaluation of the predictive ability of QSPR models should be considered: 1. High value of cross-validated R2 (q2 > 0.5). 2. Correlation coefficient R between the predicted and actual properties from an external test set close to 1. R 02 or R '02 should be close to R2. 3. At least one slope of regression lines (k or k') through the origin should be close to 1. 4. Rm2 should be greater than 0.5. Diversity validation The essential investigated theme in chemical database analysis is the diversity of sampling [42]. The diversity problem involves defining a different division of representative compounds. In this study, diversity analysis was done on the data set to make sure that the structures of the training, prediction or validation sets can characterize those of the whole ones. We consider a database of n experiments m generated from m highly correlated variable {Χ J } . j =1 Each experiment, Xi, is represented as following vector: Χ i = ( x i 1, x i 2 , x i 3 ,...x im ) for i = 1,2,..., n n d j =1 ij CI&CEQ 19 (3) 321−331 (2013) di = n −1 , i = 1,2,..., n (16) Then the mean distances were normalized within the interval of zero to one. In order to calculate the values of mean distances in accordance with Eqs. (15) and (16), a MATLAB program was written that combines maximum dissimilarity search algorithms and general multi-dimensional measurements of chemical similarity rooted in different experiments. The closer to one the distance is, the more diverse to each other the compound is. The mean distance of experiments were plotted against ferrous iron precipitation (EXP) (Figure 1), which shows the diversity of the experiments in the training, prediction and validation sets. As can be seen from this figure, the experiments are diverse in all sets and the training set with a broad representation of the chemistry space was adequate to ensure the model’s stability and the diversity of prediction and validation sets can prove the predictive capability of the model. (13) where xij indicates the value of variable j of experiN ment Xi. The collective database Χ = {Χ i } is i =1 represented a n×m matrix of X as follows: x11 x 12 x x 21 22 T X = (X 1, X 2 ,..., X N ) = x n1 x n 2 ... x 1m ... x 2m ... x nm (14) Figure 1. Scatter plot of experiments for training, prediction and validation sets. where the superscript T represents the vector/matrix transpose. A distance score, dij, for two different experiments, Xi and Xj, can be measured by the Euclidean distance norm: d ij = Χ i − Χ j = m (x k =1 ik − x jk )2 (15) The mean distances of one experiment to the remaining ones were computed as: RESULTS AND DISCUSSION PLS Modeling The descriptive statistics of corresponding observed PLS and ANN predicted values of ferric iron precipitation of all experiments studied in this work are shown in Table 1. The independent variables of leaching temperature, initial pH, oxidation/reduction potential (ORP), ferrous iron concentration and particle size of uranium ore were used in the develop- 325 H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… CI&CEQ 19 (3) 321−331 (2013) Table 1. Descriptive statistics of observed and predicted values of ferric iron precipitation (mg/l); EXP refers to experimental; PLS refers to partial least squares; ANN refers to artificial neural network Set n Minimum Maximum Mean Standard deviation Training (EXP) 40 317 2514 1282 572 Training (PLS) 40 304 2489 1308 556 Training (ANN) 40 314 2498 1279 568 Prediction (EXP) 20 506 2327 1298 586 Prediction (PLS) 20 381 2271 1306 565 Prediction (ANN) 20 512 2310 1296 582 Validation (EXP) 20 486 2421 1207 607 Validation (PLS) 20 392 2377 1213 558 Validation (ANN) 20 492 2415 1206 600 ment of PLS method. By interpreting the variables in the models, it is possible to gain some insight into factors that are probable related to ferric iron precipitation. For assessment of the relative importance and donation of each variable in the model, the value of mean effect (ME) was calculated for each variable by the following equation: β j n d ij ME j = m i =n1 β d j j i =1 ij (17) where MEj is the mean effect for considered variable j, βj is the coefficient of variable j, dij is the value of interested variables for each experiment, and m is the number of variables in the model. The calculated values of MEs are represented in the last column of Table 2 and are also plotted in Figure 2. Table 3 represents the correlation matrix for these variables. The value and sign of mean effect demonstrates the relative contribution and direction of influence of each variable on the ferric iron precipitation. As shown in Table 2, the most relevant variables based on their mean effects are pH and leaching temperature. The positive coefficient of these variables mean as the value of this variables increase, the values of ferric iron precipitation increase. These results are in accordance with those we have obtained in bioleaching experiments. Figure 2. Plot of descriptor's mean effects. Neural network modeling The next step was the production of ANN and training of it. Input and output data normalization is a significant feature of training the network and performed to avoid problems with saturation of the neuron transfer function. Input and output data are typically normalized in the range (0,1) or (-1,+1). The type of normalization is problem dependent and may have Table 2. The partial least squares regression coefficients Variable Leaching temperature Notation Coefficient Mean effect 1345.67 t 38.75 pH 732.43 1432.27 Oxidation/reduction potential ORP -2.28 -1173.20 Ferrous iron concentration Fe (II) -1.16 945.13 PS -8.50 -765.00 – 13666.56 – Initial pH Particle size Constant 326 H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… CI&CEQ 19 (3) 321−331 (2013) Table 3. Correlation matrix between selected variables t pH t pH ORP Fe (II) PS 1 -0.029 0.213 -0.124 0.144 1 -0.668 0.750 0.196 1 -0.642 0.251 1 -0.097 ORP Fe (II) PS 1 some effects on how well the ANN trains. Here we use Scaled normalization to bring the data into dynamic range of the tangent sigmoid transfer function of the network. Before training the ANNs, the parameters of network including the number of nodes in the hidden layer, weights and biases learning rates and momentum values were optimized. In order to determine the optimum number of nodes in hidden layer several training sessions were conducted with different number of hidden nodes. The values of standard error of training (SET) and standard error of prediction (SEP) were calculated after each 1000 iterations and calculation was stopped when overtraining began, then SET and SEP values were recorded. The recorded values of SET and SEP were plotted against the number of nodes in hidden layer, and the number of hidden nodes with minimum values of SET and SEP was chosen as the optimum one (Figure 3). It can be seen from this figure that 6 nodes in the hidden layer were sufficient for a good performance of the network. Learning rates of weights and biases and also momentum values were optimized in a similar way and the results are shown in Figures 4-6, res- pectively. As can be seen, the optimum values of the weights and biases learning rates and momentum were 0.2, 0.2 and 0.3, respectively. The generated ANN was then trained by using the training set for the optimization of weights and biases. However, training was stopped when overtraining began. For the evaluation of the prediction power of network, trained ANN was used to simulate the ferric iron precipitation included in the prediction set. Table 4 shows the architecture and specification of the optimized network. After optimization of the network parameters, the network was trained by using training set for adjustment of the weights and biases values by back-propagation algorithm. It is recognized that the neural network can become overtrained. An overtrained network has usually learned completely the motivation pattern it has seen but cannot give precise forecasting for unobserved stimuli, and it would no longer be capable to generalize. There are various methods for overcoming this problem. One method is to utilize a prediction set to assess the prediction power of the network during its training. In this method, after each 1000 training iterations, the Figure 3. The values of SET and SEP versus number of nodes in hidden layer. Figure 4. The values of SET and SEP versus weight learning rate. 327 H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… q 2 = 1− network was used to calculate ferric iron precipitation included in the prediction set. To preserve the predictive power of the network at an enviable level, training was stopped when the value of errors for the prediction set started to increase. CI&CEQ 19 (3) 321−331 (2013) ( y i − yˆ i )2 (18) (y i − y ) 2 where y i and yˆ i , respectively are the measured and predicted values of the dependent variable (ferric iron precipitation), y is the averaged value of dependent variable of the training set and the summations cover all the compounds. The calculated value of q 2 was 0.996. Table 4. Architecture and specifications of optimized ANN model Parameter Value Number of nodes in the input layer 5 Number of nodes in the hidden layer 6 Number of nodes in the output layer 1 Weights learning rate 0.2 Biases learning rate 0.2 Momentum 0.3 Transfer function (hidden layer) Tangent sigmoid Transfer function (output layer) Linear Table 1 shows the descriptive statistics of observed and predicted values of ferric iron precipitation for the training, prediction and validation sets. The statistical parameters obtained by ANN and PLS models for these sets are shown in Table 5. The standard errors of training, prediction and validation sets for the PLS model are 180.972, 165.047 and 149.950, respectively, which would be compared with the values of 32.860, 40.739 and 35.890, respectively, for the ANN model. Comparison between these values and other statistical parameters in Table 5 discloses the superiority of the ANN model over PLS ones. The key power of neural networks, unlike regression analysis, is their aptitude to supple mapping of the selected features by manipulating their functional dependence implicitly. The statistical values of validation set for the ANN model was characterized by q2 = 0.996, R2 = = 0.996 (R = 0.998), R 02 = 0.996 , Rm2 = 0.988 and k = = 1.002. These values and other statistical parameters (Table 5) reveal the high predictive ability of the model. Figure 7 shows the plot of the ANN predicted versus experimental values for ferric iron precipitation of all of the experiments in data set. The residuals of the ANN calculated values of the ferric iron precipi- Figure 5. The values of SET and SEP versus biases learning rate. Figure 6. The values of SET and SEP versus momentum. The predictive power of the ANN models developed on the selected training sets are estimated on the predictions of validation set chemicals, by calculating the q2 that is defined as follow: Table 5. Statistical parameters obtained using the ANN and PLS models; R is the correlation coefficient, SE is standard error and F is the statistical F value Model SET SEP SEV RT RP RV FT FP FV ANN 32.860 40.739 35.890 0.998 0.997 0.998 10400 3517 4727 PLS 180.972 165.047 149.950 0.943 0.957 0.966 306 197 254 328 H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… tation are plotted against the experimental values in Figure 8. The propagation of the residuals on both sides of the zero line signifies that no systematic error exists in the constructed QSPR model. CI&CEQ 19 (3) 321−331 (2013) oxidation/reduction potential, ferrous concentration and particle size of uranium ore provide some information related to different experiments which can affect the ferric iron precipitation. The good agreement between experimental results and predicted values verifies the validity of obtained models. The calculated statistical parameters of these models reveal the superiority of ANN over PLS model. The results show that the ANN model can accurately describe the relationship between the operational conditions of bioleaching process and ferric iron precipitation. Nomenclature QSPR ANN PLS ORP PS Figure 7. Plot of calculated ferric iron precipitation against experimental values. CONCLUSIONS Results of this study disclose that ANN can be used successfully in development of a QSPR model to predict the ferric iron precipitation in uranium bioleaching process. Variables appearing in this QSPR model such as leaching temperature, initial pH, R ME t SE F FBR W O B k EXP q SCE X Y T Quantitative structure-property relationship Artificial neural network Partial least squares Oxidation/reduction potential Particle size Correlation coefficient Mean effect Leaching temperature Standard error Statistical F value Fluidized bed reactor Weight signal Output of the node Bias term Slope of regression line Experimental Cross validated coefficient Saturated calomel electrode Predictor (independent) variable Response (dependent )variable Score of X Figure 8. Plot of residual versus experimental values of ferric iron precipitation. 329 H. GOLMOHAMMADI, A. RASHIDI, S.J. SAFDARI: PREDICTION OF FERRIC IRON… P Q S E F BP d SET SEP SEV Loading of X Score of Y Loading of Y Residual for X Residual for Y Back-propagation Distance score Standard error of training Standard error of prediction Standard error of validation CI&CEQ 19 (3) 321−331 (2013) [18] N. Daneshvar, A.R. Khataee, N. Djafarzadeh, J. Hazard. Mater. 137 (2006) 1788-1795 [19] E. Sahinkaya, B. Ozkaya, A.H. Kaksonen, J.A. Puhakka, Biotechnol. Bioeng. 97 (2006) 780-787 [20] E. Sahinkaya, J. Hazard. Mater. 164 (2009) 105-113 [21] K. Yetilmezsoy, B. Ozkaya, M. Cakmakci, Neural Network World 31 (2011) 193-218 [22] K.D. Mehta, B.D. Pandey, T.R. Mankhand, Miner. Eng. 16 (2003) 523–527 [23] M.S. Choi, K.S. Cho, D.S. Kim, H.W. Ryu, J. Microbiol. Biotechnol. 21 (2005) 377-380 REFERENCES [24] D.G. Karamanev, L.N. Nilolov, V. Mamatarkova, Miner. Eng. 15 (2002) 341-346 [1] K. Bosecker, FEMS Microbiol. Rev. 20 (1997) 591–604 [25] [2] D. Holmes, Chem. Ind. 1 (1999) 20–24 L. Herrera, P.R. Ruiz, J.C. 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SAFDARI: PREDICTION OF FERRIC IRON… HASSAN GOLMOHAMMADI ABBAS RASHIDI SEYED JABER SAFDARI Nuclear Science and Technology Research Institute, AEOI, Tehran, Iran NAUČNI RAD CI&CEQ 19 (3) 321−331 (2013) PREDVIĐANJE PRECIPITACIJE FERI JONA U PROCESU BIOLUŽENJA PRIMENOM PARCIJALNIH NAJMANJIH KVADRATA I VEŠTAČKE NEURONSKE MREŽE Razvijena je kvanitativna zavisnost između strukture i svojstava zasnovana na parcijalnim najmanjim kvadratima i veštačkoj neuronskoj mreži u cilju predviđanja precipitacije gvožđe(III) jona u procesu bioluženja. Ulazne promenljive bile su: temperatura luženja, početni pH, oksido-redukcioni potencijal, koncentracija gvožđe(II) i veličina čestica rude. Izlaz iz modela je bila precipitacija gvožđe(III) jona. Optimalni uslov veštačke neuronske mreže je dobijen podešavanjem različitih parametara metodom probe i greške. Posle optimizovanja i učenja mreže pomoću algoritma sa povratnom propagacijom, generisana je neuronska mreža 5-5-1 radi predviđanja precipitacije gvožđe(III) jona. Vrednosti korena srednje kvadratne greške za učenje, predviđanje i validaciju neuronske mreže bile su 32,860; 40,739 i 35,890, redom, koje su manje od onih dobijenih modelom parcijalnih najmanjih kvadrata (180,972; 165,047 i 149,950, redom). Dobijeni rezultati pokazuju pouzdanost i dobru prediktivnost neuronske mreže za predviđanja precipitacije gvožđe(III) jona u procesu bioluženja. Ključne reči: kvanitativna zavisnost struktura-svojstvo, precipitacija gvožđe(III) jona, proces bioluženja, parcijalni najmanji kvadrati, veštačka neuronska mreža. 331 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 333−337 (2013) A.C. ARVADIYA P.P. DAHIVELKER R.C. Patel Institute of Pharmaceutical Education and Research, Shirpur, Dist. Dhule (M.S.), India SCIENTIFIC PAPER UDC 543.2/.9:615 DOI 10.2298/CICEQ120319068A CI&CEQ DEVELOPMENT AND VALIDATION OF NOVEL RP-UPLC METHOD FOR ESTIMATION OF ATROPINE SULPHATE IN PHARMACEUTICAL DOSAGE FORM A simple, precise, accurate, sensitive and repeatable RP-UPLC method was developed for quantitative determination of atropine sulphate in pharmaceutical dosage form. The method was developed by using a C18 column Hiber HR Purospher Star (100 mm×2.1 mm id, 2 µm particle size) as stationary phase with phosphate buffer:acetonitrile (87:13, v/v) as a mobile phase; pH was adjusted to 3.5 by orthophosphoric acid at a flow rate of 0.5 mL/min and the column temperature was maintained at 30 °C. Quantification of the eluted compound was achieved with a PDA detector at 210 nm. Atropine sulphate followed linearity in concentration range of 2.5-17.5 µg/mL with r2 = 0.9998 (n = 6). Limit of detection (LOD) and limit of quantification (LOQ) values were 0.0033 and 0.0102 µg/mL for atropine sulphate. The validation study was carried out as per International Conference on Harmonization (ICH) guidelines. This method was successfully applied for the estimation of atropine sulphate in pharmaceutical formulation. Keywords: atropine sulphate, method validation, reversed phase ultra pressure liquid chromatography. Tropane alkaloid (atropine) is extracted from deadly nightshade (Atropa belladonna), jimsonweed (Datura stramonium), mandrake (Mandragora officinarum) and other plants of the family Solanaceaeare widely used as parasympatolytic, anticholinergic and antiemetic drugs [1]. Atropine sulphate is (RS)(1R,3r,5S)-3-tropoyloxytropanium sulphate monohydrate (Figure 1). Figure 1. Structure of atropine sulphate. Atropine sulphate injection is official in Indian pharmacopeia, British Pharmacopeia and United States Pharmacopeia. Some methods for the determination of tropane alkaloids appearing in the literature are based on TLC [2-3], gas chromatography [4], LC-MS [5,6], high performance liquid chromatography [7– -12], capillary zone electrophoresis [13,14], chiral separation [15], with fluorescence detection [16], with conductometric detection [17], cation exchange [18], ion-pair high performance chromatography [19]. To the best of our knowledge, there is no RP-UPLC method reported in literature for determination of atropine suphate. Therefore, the aim of the present work is to develop a simple, rapid, accurate and precise RP-UPLC method for determination of atropine sulphate in pharmaceutical formulation. EXPERIMENTAL Apparatus Correspondence: P.P. Dahivelker, R.C. Patel Institute of Pharmaceutical Education and Research, Shirpur, Dist: Dhule (M.S.) India 425 405. E-mail: raj17579@rediffmail.com Paper received: 19 March, 2012 Paper revised: 25 June, 2012 Paper accepted: 26 June, 2012 The chromatography was performed on a Water (Acquity) RP-UPLC instrument equipped with a PDA detector and Em-power 2 software. The column “Hiber HR Purospher Star C18” (100 mm×2.1 mm id, 2 µm particle size, Merck, Germany) was used. An 333 A.C. ARVADIYA, P.P. DAHIVELKER: DEVELOPMENT AND VALIDATION OF NOVEL RP-UPLC… analytical balance (Mettler Toledo, Germany) and ultrasonic cleaner (Frontline FS 4, India) were used in the preparation process. Reagents and materials The active pharmaceutical ingredient standard and sample were supplied by Nirlife, Healthcare division of Nirma, Ahmedabad, India. The commercial product was procured from the local market. The HPLC grade Acetonitrile and KH2PO4 were purchased from Finar Reagent (Ahemedabad, India). The filter paper was Whatmann filter paper No. 41 (Whatmann International Ltd., England). Preparation of mobile phase To prepare the buffer solution, 6.8 gm potassium dihydrogen orthophosphate was weighed and dissolved in 1000 mL HPLC grade water. The buffer solution and HPLC grade actonitrile were mixed in a 1000 mL volumetric flask to make a mobile phase ratio buffer:acetonitrile (87:13, v/v), and the pH was adjusted to 3.5 by using orthophosphoric acid. The mobile phase was filtered and degassed in an ultrasonic bath. Chromatographic condition The flow rate of mobile phase was adjusted to 0.5 mL/min and the injection volume was 2 µl. The column temperature was maintained at 30 °C, while the detection wavelength was 210 nm (Figure 2). CI&CEQ 19 (3) 333−337 (2013) by dissolving 50 mg of atropine sulphate and then diluted to volume with mobile phase as a diluent. Preparation of standard atropine sulphate injection solution (500 µg/mL) An atropine sulphate injection standard solution at concentration of 500 µg/mL was prepared in a 1000 mL volumetric flask by dissolving 1 mL of atropine sulphate injection from marketed formulation (Brand Name: atronir, label: atropine sulphate - 500 mg/mL) and diluted to volume with mobile phase. Preparation of calibration curve A calibration curve was plotted over concentration range of 2.5-17.5 µg/mL. Aliquots (0.5, 1, 1.5, 2, 2.5, 3, and 3.5 mL) of standard stock solution were transferred in a series of 100 mL volumetric flasks and diluted with mobile phase. Each solution was injected under the operating chromatographic condition as described above and areas were recorded. A regression equation was obtained for the calibration curve by plotting the peak area versus the concentration. Analysis of atropine sulphate Injection (500 mg/mL) Atropine sulphate injection sample solution of concentration 10 µg/mL was prepared in a 100 mL volumetric flask by diluting 2 mL of standard atropine sulphate injection solution with mobile phase. The solution was sonicated for 5 min and filtered through Whatmann filter paper No. 41. Sample solution (2 μL) was injected six times under the operating chromatographic condition as described above and areas were recorded. RESULTS AND DISCUSSION Optimization of chromatographic conditions Figure 2. UV Spectra of atropine sulphate. Preparation of standard stock Solution of atropine sulphate (500 µg/mL) Atropine sulphate standard solution containing 500 µg/mL was prepared in a 100 mL volumetric flask 334 The main objective of the chromatographic method was to quantify atropine sulphate. Atropine sulphate was eluted using different stationary phases such as C18, C8, phenyl, amino and cyano as well as different mobile phases containing buffers like phosphate, sulphate, and acetate with different pH (2–5) and using organic modifiers like acetonitrile, methanol and ethanol in the mobile phase. The peak shape of the atropine sulphate was found to be symmetrical at 210 nm wavelength. In optimized chromatographic conditions, atropine sulphate was separated with typical retention time of 2.76 min. Validation of method The method was validated with respect to linearity, limit of detection (LOD), limit of quantitation A.C. ARVADIYA, P.P. DAHIVELKER: DEVELOPMENT AND VALIDATION OF NOVEL RP-UPLC… (LOQ), accuracy, precision, ruggedness in compliance with ICH guidelines (Q2B) [20]. System suitability parameters The system suitability test of the proposed chromatographic method was performed before each validation run. Six replicate injections of standard solution containing 10 µg/mL atropine sulphate were injected to confirm column efficiency (theoretical plate) and tailing factor. System suitability parameters are summarized in Table 1. Table 1. System suitability data obtained from optimum condition Value±SD (n = 6) Parameter Retention time 2.76±0.006 Theoretical plates 11802±93.27 Tailing 1.49±0.01 Linearity A seven point calibration curve was obtained in the concentration range of 2.5-17.5 µg/mL for atropine sulphate. The response of the drug was found to be linear in the investigated range and the regression equation was found to be y = 10027x + 269 (n = 6) (Figure 3), with the correlation coefficient 0.9998 (n = 6), as listed in Table 2. CI&CEQ 19 (3) 333−337 (2013) three concentration levels of 80, 100 and 120% of the specified limit. The percentage recoveries of atropine sulphate were calculated with RSD range of 0.07-0.11% and the results are shown in Table 3. Table 3. Recovery data of atropine sulphate for the proposed method; initial amount: 5 µg/mL Amount added, % Recovery, % RSD / % (n = 3) 80 99.67 0.11 100 99.69 0.07 120 99.89 0.07 Precision The precision of the method was evaluated in terms of inter-day and intra-day by carrying out independent assays of three concentrations chosen from the high, medium and low range of the standard curves (5, 10 and 15 µg/mL) and the RSD of assay (inter-day and intra-day) was calculated. The results are shown in Table 4. The developed method was found to be precise as the RSD values for intra-day ranged from 0.06-0.44% and inter-day ranged from 0.13-0.61%. Table 4. Results of intraday and interday precision (amount found in µg/mL) c / µg mL-1 Intra-day Inter-day Mean RSD / % (n = 3) Mean RSD / % (n = 3) 5 4.98 0.08 4.97 0.13 10 10.03 0.44 10.03 0.61 15 14.99 0.06 15 0.34 Limit of detection and limit of quantification Figure 3. Linearity of atropine sulphate. Table 2. Linearity of atropine sulphate for proposed method Value (n = 6) Parameter Linearity 2.5-17.5 µg/mL Slope 10027 Intercept 269 2 Correlation coefficient (r ) 0.9998 Accuracy The accuracy of the method was determined by spiking of atropine sulphate to prequantified sample solutions of atropine sulphate (5 µg/mL) in triplicate at The limit of detection (LOD) and limit of quantitation (LOQ) of the method were evaluated by standard deviation of response and slope method. LOQ and LOD were calculated by the equations LOD = = 3.3N/B and LOQ = 10N/B, where N is the standard deviation of the peak areas of the drugs (n = 6), taken as a measure of noise, and B is the slope of the corresponding calibration curve. The limit of detection (LOD) and limit of quantitation (LOQ) were found to be 0.0033 and 0.0102 μg/mL, respectively. Ruggedness The ruggedness of the method was ascertained by repeatedly injecting (n = 6) standard solutions of atropine sulphate (10 μg/mL) without changing the chromatographic parameters with two analysts, on two different days and by using two equipment in same laboratory and calculated RSD. The result of ruggedness study is shown in Table 5. The developed 335 A.C. ARVADIYA, P.P. DAHIVELKER: DEVELOPMENT AND VALIDATION OF NOVEL RP-UPLC… CI&CEQ 19 (3) 333−337 (2013) method was rugged as the RSD was less than 2 for all condition. Validation parameters for the assay method are summarized in Table 5. to be 100.61% and RSD value was 0.55% by RPUPLC (Figure 4). Table 5. Summary of validation parameters for the proposed RP-UPLC method A new, reversed-phase UPLC method has been developed for estimation of atropine sulphate in pharmaceutical dosage forms. The method was validated by employment of ICH guidelines. The validation data is indicative of good precision and accuracy, and proves the reliability of the method. The developed method has been used to monitor the atropine sulphate content in production batches. Method parameter Result Linearity (correlation coefficient) 0.9998 Ruggedness, RSD / % (n = 6) Analyst-I 0.43 Analyst-II 0.21 Day 1 0.33 Day 2 0.53 Equipment 1 0.50 Equipment 2 0.47 Sensitivity Limit of detection, µg/mL 0.0033 Limit of quantitation, µg/mL 0.0102 Precision, RSD / % Intraday (n = 3) 0.06-0.44 Interday (n = 3) 0.13-0.61 Repeatability (n = 6) 0.52 Robustness Robust CONCLUSION Acknowledgement The authors are thankful to Nirlife HealthCare, Ahmedabad, India, for providing a sample and facilities for research. The authors are thankful to Dr. S.J. Surana, Principle, and Dr. H.S. Mahajan, Head of Quality Assurance Department, R.C. Patel Institute of Pharmaceutical Education & Research, Shirpur, Maharashtra, India, for them valuable remarks in carrying out the experimental. REFERENCES F.S.K Barar., Essentials of Pharmacotherapeutics, 4 ed., S. Chand and Xo. Ltd., New Delhi, 2007, pp. 246-247 [2] The British Pharmacopoeia, Vol. 3, the Pharmaceutical Press, London, 2009, pp. 8019-8020 [3] S. El-Masry, S.A.H. Khalil, J. Pharm. Sci. 62 (1973) 1332-1334 [4] P. Majlat, J. Chromatogr. 241 (1982) 399-403 Analysis of atropine sulphate injection The validity of the proposed assay method for pharmaceutical formulation was studied by assaying atropine sulphate injection (label claim 500 mg/mL atropine sulphate). The percentage purity was found th [1] Figure 4. Chromatogram of assay for atropine sulphate solution by RP-UPLC method. 336 A.C. ARVADIYA, P.P. DAHIVELKER: DEVELOPMENT AND VALIDATION OF NOVEL RP-UPLC… [5] C. Abbara, I. Bardot, A. Cailleux, G. Lallement, A. Le Bouil, A. Turcant, P. Clair, B. Diquet, J. Chromatogr., B 874 (2008) 42-50 [6] H.X. Chen, Y. Chen, P. Due, F.M. Han, Chromatographia 65 (7-8) (2007) 423-429 [7] I.L. Honigberg, J.T. Stewart, A.P. 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Nishijima, K.Kamata, J.Chromatogr.A. 775 (1997) 137-141 [17] O. W. Lau, C. S. Mok, J. Chromatogr., A. 766 (1997) 270–276 [18] T. Mroczek, K. Glowniak, J. Kowalska, J. Chromatogr., A 1107 (2006) 9-18 [19] N.B. Brown, H.K. Sleeman, J. Chromatogr. 150 (1978) 225–228 [20] ICH, Validation of Analytical Procedures: Methodology (Q2R1), International Conference on Harmonization, Food and Drug Administration, USA, 1996. RAZVOJ I VALIDACIJA NOVE RP-UPLC METODE ZA ODREĐIVANJE ATROPIN-SULFATA U FARMACEUTSKIM PREPARATIMA U radu je razvijena jednostavna, precizna, tačna, osetljiva i reproduktivna RP-UPLC metoda za kvantitativno određivanje atropin-sulfata u farmaceutskim preparatima. Uzorci su analizirani na C18 koloni Hiber HR Purospher Star (100 mm×2.1 mm, veličina čestica 2 µm). Kao mobilna faza korišćena je smeša fosfatni pufer:acetonitril (87:13, v/v). pH pufera je podešen na 3,5 dodatkom ortofosforne kiseline. Brzina protoka mobilne faze je 0,5 mL/min, a temperatura kolone je 30 °C. Komponente su detektovane PDA detektorom na 210 nm. Nađeno je da metoda ima zadovoljavajuću linearnost u opsegu koncentracija od 2,5-17,5 µg/mL sa r2 = 0,9998 (n = 6). Limit detekcije za ovu metodu određivanja atropin-sulfata je 0,0033 μg/ml, a limit kvantifikacije 0,0102 μg/ml. Metoda je validirana u skladu sa ICH uputstvima. Metoda je uspešno primenjena za određivanje atropin-sulfata u farmaceutskim preparatima. Ključne reči: atropin-sulfat, metoda validacije, RP-UPLC hromatografija. 337 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 339−346 (2013) ARKAN JASIM HADI1 GHASSAN JASIM HADI2 GHAZI F. NAJMULDEEN1 IQBAL AHMED1 SYED F. HASANY1 1 Faculty of Chemical engineering and Natural Resource, University Malaysia Pahang, Kuantan, Malaysia 2 Al Dour Technical Institution, Technical Education Organization, Tikrit, Iraq SCIENTIFIC PAPER UDC 544.344.2-14-13:546.264-31:66 DOI 10.2298/CICEQ120324067H CI&CEQ GAS–LIQUID EQUILIBRIUM PREDICTION OF SYSTEM CO2-AQUEOUS ETHANOL AT MODERATE PRESSURE AND DIFFERENT TEMPERATURES USING PR-EOS One of the most important design considerations that should not be ignored during industrial purpose equipment designing is vapour-liquid equilibrium (VLE). Thus, in chemical engineering, the first step is the computation of VLE properties of materials by employing equations of state (EOS). In this study, we have used a thermodynamic model established for a binary system of carbon dioxide (1)–aqueous ethanol (2), which was employed to estimate the gas–liquid equilibrium at moderate pressures (up to 6 bar) and varying temperatures (288–323 K). The Peng-Robinson EOS was employed to determine the VLE properties. Mixing rules such as van der Waals and quadratic mixing rules were also used for the determination of ethanol-water mixture critical parameters, which entails the pseudo-critical method as one component, and the results obtained from this study were similar to the ones reported in recent literature for empirical phase equilibrium studies. Keywords: gas-liquid equilibrium, carbon dioxide, mixture, moderate pressure, PR-EOS. Several attempts have been made during the last five decades to compute the VLE properties of different materials by employing a mathematical model, but unfortunately due to lack of theoretical basis, all attempts resulted in no significant outcome. The advent of computer technology and programs has made it possible to interpolate, extrapolate and predict thermodynamic information, which is crucial in designing of equipment sand modeling of process operations [1]. Intensive research has been conducted on gas solubility in liquids during the last three decades. This is significant from an industrial application point of view where gas solubility in pure and mixed liquids are of considerable importance, e.g. carbonation processes employed for wastewater treatment, stripping columns, gas absorption, soft drinks and alcoholic beverages, etc. [2]. Correspondence: A.J. Hadi, Faculty of Chemical engineering and Natural Resource, University Malaysia Pahang, Kuantan, 26300, Malaysia. E-mail: arkanaldoury72@gmail.com Paper received: 24 March, 2012 Paper revised: 26 April, 2012 Paper accepted: 26 June, 2012 However, gas solubility in diluted liquids is also of considerable importance from a theoretical point of view. Molecular theories are being tested by employing empirical solubility data and it is also utilized to illustrate the intermolecular interactions and microscopic structure of materials. Wilhem et al. [3] reported the dependence of benefits of low-pressure gas solubility over high-pressure equilibrium data and it was based on the observation that inaccuracies brought by semi-empirical relation is insignificant and it has no effect on the final observations, e.g. the impact of the solute’s partial molar volume on indefinite diluted solvent and besides this some definite assumptions make possible the thermodynamic treatment of the system [2]. Other different thermodynamic information, such as volumetric characteristics and phase equilibrium of mixture and pure compounds (carbon dioxide either with alkane or alkanol), has great interest in the domains of chemical engineering, oil and biotechnology areas. It is also used for the establishment and validation of some models of thermodynamics. Identification of global phase behavior of different systems in a specified range of temperature and pressure is also crucial in this context [4]. 339 A.J. HADI et al.: GAS–LIQUID EQUILIBRIUM PREDICTION OF SYSTEM CO2-AQUEOUS ETHANOL… Empirical observations for gas solubility in common systems that are employed for the establishment of models for studying different parameters, especially at high pressures, can be found in the existing literature. The carbon dioxide and water binary system was also studied by Alain et al. [5], who reported new empirical observations for VLE data at a wide range of temperature (278.2–318.2 K) and pressure around 80 bar. These observations were consistent with the ones already present in the literature. Gas solubility and Henry’s data was also extensively researched by Dalmoelin et al. [2], who employed carbon dioxide gas to check its solubility in pure water and ethanol and a mixture of both and for this they chose temperature in range of (288–323K) whereas pressure was maintained up to 6 atm for pure solvents as well as their mixture with varying amounts of both solvents. The CO2 and alkanol system was studied by Elizalde-Solis et al. [4], who measured their VLE values. The temperature range for carbon dioxide and 1-propanol system was around 344 to 426 K and its equilibrium values were determined. However, for CO2 + 2-propanol, temperature in range of 334 to 443 K was used. 1-Butanol with CO2 system was studied at temperature 354 to 430 K. Polyethylene glycol 200 as a solvent was also studied using carbon dioxide as gas model by Minqiang Hou et al. [6]. They used the following solvents and their mixtures in his study; PEG200, PEG with an average molecular weight of 200 g/mol), 1-pentanol and 1-octanol. PEG200 + 1-pentanol, and PEG200 + 1-octanol and the reported temperature range was 303.15, 313.15 and 323.15 K up to 8.0 MPa, respectively. With increase in the pressure, increase in the gas solubility was reported by [6]; also, increased alcohol concentration was found to also have significant impact on mixed solvents. However, at increasing temperature, the solubility decreases and it was found to be different for different solvents. Carbon dioxide had high solubility in PEG200 + 1-pentanol. Thiophene as a solvent for carbon dioxide was investigated by Elizalde and Galicia-Luna [7] and CO2 + 1-propanol was also studied. The Peng-Robinson equation of state along with the classical mixing rule was employed for the computation of VLE data of binary mixtures. Comparative analysis of empirical and theoretical observations was made in the end. Secuianu et al. [8] studied the phase behavior of the carbon dioxide in methanol; they measured the VLE of this system and reported data at 293.15, 303.15, 313.15, 333.15 and 353.15 K and pressures between 5.2 and 110.8 bar. They modeled the measured VLE data and literature data by using a general cubic 340 CI&CEQ 19 (3) 339−346 (2013) equation of state combined with a classical van der Waals two parameter conventional mixing rule. They used one set of interaction parameters to predict the critical and subcritical VLE in binary mixture CO2 and ethanol in a varied temperature. They also concluded from the comparison between the predicted results, experimental data and the literature data, the phase behavior was suitable reproduced. Results obtained from this research for PR-EOS in CO2 (1)–aqueous ethanol (2) at optimum pressure and temperature was analyzed and compared with empirical data obtained from [2]. THERMODYNAMIC MODEL For the computation of phase equilibrium behaviour, the thermodynamic model employed for this purpose must meet the requirements mentioned in the expression mentioned below. This expression is for two-phase equilibrium in which one phase is represented by prime (') and the other by double prime ("). fi′ = fi″, i = 1,2,3,…,m (1) In the above expression f indicates the fugacity of component (i) in a multi-component mixture [9]. EOS A component’s fugacity in a phase is computed by employing a thermodynamic equilibrium model utilizing EOS. Interaction energies and size factors have been observed to have an impact on the results of the models used for fugacity computation. This creates the requirement of mixing rules development for the estimation of highest energy and size parameters as needed by EOS. For modeling phase behaviour, cubic EOS are generally employed, which are quite simple and extensively employed for empirical data analysis [10,11]. The following modified equation was proposed by Peng and Robinson: P = RT a (T ) − (v − b ) v (v + b ) + b (v − b ) (2) At the critical point: a (Tc ) = 0.45724 b (Tc ) = 0.0778 R 2Tc2 Pc RTc Pc (3) (4) At other temperatures, the parameter T is changed as: A.J. HADI et al.: GAS–LIQUID EQUILIBRIUM PREDICTION OF SYSTEM CO2-AQUEOUS ETHANOL… a (T ) = a (Tc )α (Tr ,ω ) (5) The efficiency of this term was improved by Graboski and Daubert [13] to explain the correlation terms of the vapour pressure curve up to the critical point as follows: α 0.5 = 1 + (1 −Tr 0.5 )(0.37464 + 1.5422ω − 0.26992ω 2 ) (6) Replacement of v in the general representation of Eq. (2) in terms of ZRT/P will give the expression for compressibility factor of PR-EOS as follows: Z 3 − (1 − B )Z 2 + ( A − 2B − 3B 2 )Z − A= aαP αP = 0.45724 2r R 2T 2 Tr (8) B= bP P = 0.0778 r RT Tr (9) Determination of compressibility factor can be made through the cubic EOS by simplifying it with an iterative procedure via the Newton–Raphson method. As pressure-explicit EOS are the more general types of equations, the significant relation for determination of fugacity coefficients can be made by using the following equation: ln ϕˆi = 1 RT v ∂P RT dV − ln Z − ∂ni T ,v ,nj V (10) b 2 × i − bm am j am = n n i j x x a i bm 1− v am + 2.828RTb × m bm 1 + 2.414 v x i aij ln bm 1 − 0.414 v bm = j (12) ij (11) Fugacity computation of components present in the gas phase was performed by employing equation 11 in which yi and entire PR-EOS a and b values were substituted by their corresponding terms. EOS was first formulated for pure components and later it was modified for mixed components by using mixing rules which combine pure component parameters [16]. n n i j x x b i j (13) ij The following mixing rule equations were employed in this study: Modified van der Waal’s mixing rules (MR1): n am = i n n x i x j a ij and bm = x b i i i j with a ij = (1 − k ij )(a i a j ) Quadratic mixing rules (MR2): n am = n i where V indicates the total system volume whereas n1 and n2 represent the mole numbers of components 1 and 2, respectively. Substituting PR-EOS into Eq. (10) will yield the following closed-form expression for fugacity coefficient, which it acquires in the liquid phase: b ln ϕˆi = i (Z − 1) − ln Z bm Van der Waal’s mixing rule has been used for the derivation of simple EOS expressions and later modifications may have been introduced in it. Onefluid mixing rules can be employed for the computation of the mixture parameters am and bm for the EOS as shown in Eqs. (12) and (13). Combining rule is the exception between the two and it helps in the calculation of cross coefficients aij and bij. and A and B are defined as: ∞ Mixing rules (7) −( AB − B 2 − B 3 ) = 0 CI&CEQ 19 (3) 339−346 (2013) j x i x j a ij and bm = n n i j x x b i j ij with a ij = (1 − k ij )(a i a j ) and bij = (bi + b j 2)(1 − l ij ) . RESULTS AND DISCUSSION Prediction of VLE by employing cubic EOS expressions along with physical characteristics of pure components and adjustable parameters of binary system of CO2 (1)–aqueous ethanol (2) was the major objective of this research. van der Waal’s equation was altered by PR-EOS and mixing rule. The quadratic rule is generally employed for finding the correlations of empirical observations for VLE. Comparison of calculations with empirical observations was made after the computation of CO2 mole fraction in the liquid phase (x). For comparative analysis, empirical data was obtained from [2]. Critical parameters of water-ethanol mixture at different compositions, such as critical temperature 341 A.J. HADI et al.: GAS–LIQUID EQUILIBRIUM PREDICTION OF SYSTEM CO2-AQUEOUS ETHANOL… (Tcm), critical pressure (Pcm) and acentric factor ωm were approximated by the following expressions [18]: T x = p x = ω x Tcm = Pcm ωm ci ci i (14) i (15) i (16) i In the above expression the symbols Tcm, Pcm and ωm represent the critical temperature, pressure and acentric factor, respectively, for a given mixture, whereas Tci, Pci and ωi are the critical parameters of ethanol and water. The expression xi shows the mole fraction of components (water and ethanol). The critical properties of the carbon dioxide, ethanol and water are shown in Table 1. Table 1. Critical properties (Tc and Pc) and acentric factor (ω) of CO2, ethanol and water [8,14] Component Tc / K Pc / bar ω CO2 304.7 73.8 0.225 Ethanol 513.9 61.47 0.6447 Water 647.9 221 0.344 The mentioned Eqs. (14)–(16) were employed for the transformation of the multicomponent mixture (ethanol-water) to a single component and it was CI&CEQ 19 (3) 339−346 (2013) aimed to convert the ternary system (carbon dioxide–ethanol-water) system into a binary system (carbon dioxide and aqueous ethanol). Mixing rules entail some adjustable parameters such as k12 and L12 and the latter one can be calculated by using two different approaches and it need the empirical observations and later it is fitted into EOS expression. A trial and error method was adapted for the identification of MR2. Computation of mole fraction solubility was performed by using each isotherm pressure. The minimum mean absolute deviation (MAD) obtained by acceptable values of k12 and L12 was calculated as: MAD = 100 N x exp. − x calc. (17) where N represents the number of considered data points. Computational and programming details have been described previously [19]. For all the given compositions, acceptable values of k12 and L12 were used and the MAD values taken at different temperatures and varying compositions utilizing PR-EOS in CO2– –aqueous ethanol system are shown in Table 2. The comparative observations for computed and empirical data sets that took place at the temperature in the range of 288 to 323 K for all the given mixture compositions are shown in Table 2. MAD for MR2 was found to be lower than MR1 and this difference in the Table 2. Values of adjustable parameters k12 and L12, obtained from fitting with PR-EOS. Mean absolute deviation (MAD) percentage between the experimental and pedicted mole fraction solubility of CO2 in aqueous ethanol with different mixing rules using PR-EOS Composition of mixtures (ethanol + water) 0.1 Ethanol + 0.9 water 0.25 Ethanol + 0.75 water 0.5 Ethanol + 0.5 water 0.75 Ethanol + 0.25 water 0.9 Ethanol + 0.1 water 342 T/K MR1 MAD / % MR2 k12 k12 L12 MR1 MR2 288 -0.1119 -0.1119 -0.117 2.285 2.069 298 -0.1038 -0.1038 2.198 1.828 308 -0.0946 -0.0946 -0.181 -0.004 0.926 323 -0.0817 -0.0817 -0.087 0.691 0.918 0.625 288 -0.0843 -0.0843 -0.025 2.337 2.272 298 -0.0796 -0.0796 -0.046 3.397 3.306 308 -0.0747 -0.0747 -0.228 3.023 2.733 323 -0.06966 -0.06966 -0.003 1.281 1.279 288 -0.0375 -0.0375 -0.088 2.358 2.160 298 -0.03768 -0.03768 -0.091 2.063 1.872 308 -0.03232 -0.03232 -0.048 3.113 2.990 323 -0.02806 -0.02806 -0.017 0.957 0.930 288 0.03148 0.03148 -0.134 3.971 3.740 298 0.03541 0.03541 -0.074 5.334 5.177 308 0.03722 0.03722 -0.163 2.535 2.530 323 0.04064 0.04064 -0.321 3.086 2.706 288 0.07616 0.07616 -0.035 0.747 2.661 298 0.08107 0.08107 -0.116 2.093 1.948 308 0.08797 0.08797 -0.154 1.827 1.610 323 0.09538 0.09538 -0.158 2.055 1.928 A.J. HADI et al.: GAS–LIQUID EQUILIBRIUM PREDICTION OF SYSTEM CO2-AQUEOUS ETHANOL… values is negligible. We have found that thermodynamic model using PR-EOS along with MR1 and MR2 is best suited to run this system smoothly. Figures 1-8 show the comparative analysis of theoretical and empirical data values. Figure 1. Phase composition diagram of CO2–mixture system at 288 K using PR with MR1. Figure 2. Phase composition diagram of CO2–mixture system at 288 K using PR with MR2. A decrease in k12 has been observed with increase in temperature. This data is valid for the mixtures of composition starting with 0.1 ethanol + 0.9 water and goes to 0.5 ethanol + 0.5 water. An increase in k12 values was noticed in mixtures with the following compositions; 0.75 ethanol + 0.25 water and 0.9 ethanol + 0.1 water. However, it should be noted that alteration in the values of k12 is insignificant when CI&CEQ 19 (3) 339−346 (2013) compared to temperature values which are larger. L12 values are also referred as vacillation values. The binary interaction parameter k12 decreases with the increase in ethanol concentration in the mixture. Figure 3. Phase composition diagram of CO2–mixture system at 298 K using PR with MR1. Figure 4. Phase composition diagram of CO2–mixture system at 298 K using PR with MR2. It is obvious that there is good agreement between the calculated data using PR-EOS and the previous work Ghazi et al. [20] using the Soave-Redlich-Kwong equation of state (SRK) and experimental data. However, it is noticeable that there is small deviation between the results of the two equations where the MAD of the SRK that is less than the MAD for the PR-EOS for the two mixing rules. 343 A.J. HADI et al.: GAS–LIQUID EQUILIBRIUM PREDICTION OF SYSTEM CO2-AQUEOUS ETHANOL… CI&CEQ 19 (3) 339−346 (2013) conditions in CO2 mixtures. In the studied system, variation in the L12 values was observed. Figure 5. Phase composition diagram of CO2–mixture system at 308 K using PR with MR1. Figure 7. Phase composition diagram of CO2–mixture system at 323 K using PR with MR1. Figure 6. Phase composition diagram of CO2–mixture system at 308 K using PR with MR2. CONCLUSION We used PR-EOS along with MR1 and MR2 for studying VLE and the obtained observations were consistent with empirical data provided in [2]. We used this model for the computation of VLE for CO2 (1)–mixture (2) (ethanol and water) at varying temperatures and moderate pressures. In the mixing rule MR2, two adjustable parameters named k12 and L12 are used, which yielded reduced MAD compared to the one obtained by MR1. The latter one was used to determine the equilibrium data for CO2 (1)–mixture (2). Besides this, MAD variation between MR1 and MR2 was insignificant. This results in the preferable use of MR1 with k12 parameter to study gas equilibrium 344 Figure 8. Phase composition diagram of CO2–mixture system at 323 K using PR with MR2. Acknowledgment The authors express special gratitude to University Malaysia, Pahang, who provided the lab facility for the successful completion of this research and financial support through the Doctoral Scholarship scheme (No. GRS100357). Nomenclature a, b A, B parameters in the equation of state dimensionless parameters A.J. HADI et al.: GAS–LIQUID EQUILIBRIUM PREDICTION OF SYSTEM CO2-AQUEOUS ETHANOL… f kij, Lij n ni N P R T x, y Z V ν fugacity, bar adjustable parameters number of components number of moles of component i, mol number of data points pressure, bar universal gas constant, 0.08314 L bar/(mol K) temperature , K liquid and gas mole fractions, respectively compressibility factor total system volume, L total system molar volume , L/mol [5] A. Valtz, A. Chapoy, C. Coquelet, P. Paricaud, D. Richon, Fluid Phase Equilib. 226 (2004) 333-344 [6] M. Hou, S. Liang, Z. Zhang, J. Song, T. Jiang, B. Han, Fluid Phase Equilib. 258 (2007) 108-114 [7] O. Elizalde-Solis, Fluid Phase Equilib. 230 (2005) 51-57 [8] Secuianu, Catinca, Feroiu, Viorel Geană, Dan, Fluids 47 (2008) 109-116 [9] J. Smith, H. van Ness, M. Abbott, Introduction to chemical engineering thermodynamics, McGraw-Hill, New York, 2001 [10] E. Bender, U. Klein, W.P. Schmitt, J.M. Prausnitz, Fluid Phase Equilib. 15 (1984) 241-255 [11] R.D. Deshmukh, A.E. Mather, Fluid Phase Equilib. 35 (1987) 313-314 [12] D.Y. Peng, D.B. Robinson, Ind. Eng. Chem. Fund. 15 (1976) 59-64 [13] M.S. Graboski, T.E. Daubert, Ind. Eng. Chem. Process Des. Dev. 18 (1979) 300-306 [14] T. McCalla, Introduction to numerical methods and Fortran programming, Wiley, New York, 1967 [15] S.M. Walas, Phase equilibria in chemical engineering, Butterworth, Boston, MA, 1985 [16] K.A.A. Mnam, Phase Equilibrium study for the separation of solid and liquid components using supercritical carbon dioxide, PhD Thesis, University of Technology-Iraq, Baghdad, 1998 [17] Y. Adachi, H. Sugie Fluid Phase Equilib. 28 (1986) 103-118 [18] H.C. Smith, Van Ness, Introduction to Chemical Engineering Thermodynamics, 4 ed., McGraw-Hill, New York 1987 [19] A.J. Hadi, Thermodynamic Model for High Pressure Phase Behavior of Carbon Dioxide in Several Physical Solvents at Different Temperatures, Tikrit J. Eng. Sci. 15 (2008) 32-50 [20] G.F. Najmuldeen, G.J. Hadi, A.J. Hadi, I. Ahmed, Phys. Chem. 2(1) (2012) 1-5. Greek symbols ϕ ω fugacity coefficient in mixture acentric factor Subscripts and Superscripts c exp. calc. g i,j m r critical condition experimental value calculated value gas phase component mixture reduced property REFERENCES [1] R. Sytryjeck, J.H. Vera, Can. J. Chem. Eng. 64 (1986) 323–333 [2] I. Dalmolin, E. Skovroinski, A. Biasi, M. Corazza, Fluid Phase Equilib. 245 (2006) 193-200 [3] E. Wilhelm, R. Battino, R.J. Wilcock, Chem. Rev. (Washington, DC, U. S.) 77 (1977) 219-262 [4] O. Elizalde-Solis, L.A. Galicia-Luna, L.E. CamachoCamacho, Fluid Phase Equilib. 259 (2007) 23-32 CI&CEQ 19 (3) 339−346 (2013) 345 A.J. HADI et al.: GAS–LIQUID EQUILIBRIUM PREDICTION OF SYSTEM CO2-AQUEOUS ETHANOL… ARKAN JASIM HADI1 GHASSAN JASIM HADI2 GHAZI F. NAJMULDEEN1 IQBAL AHMED1 SYED F. HASANY1 1 Faculty of Chemical engineering and Natural Resource, University Malaysia Pahang, Kuantan, Malaysia 2 Al Dour Technical Institution, Technical Education Organization, Tikrit, Iraq NAUČNI RAD CI&CEQ 19 (3) 339−346 (2013) PREDVIĐANJE RAVNOTEŽE GAS-TEČNOST SISTEMA CO2-VODENI RASTVOR ETANOLA NA UMERENOM PRITISKU I RAZLIČITIM TEMPERATURAMA PRIMENOM PENG-ROBINSON-OVE JEDNAČINE STANJA Jedan od navažnijih aspekata projektovanja, koji ne sme biti zanemaren pri projektovanju opreme za industrijsku primenu, jeste ravnoteža para-tečnost (VLE). Zbog toga je u hemijskom inženjerstvu prvi korak izračunavanje ravotežnih podataka primenom jednačine stanja. U ovom radu je korišćen termidinamički model koji je utvrđen za binarni system CO2-vodeni rastvor etanola. Ovaj model je korišćen za izračunavanje ravnoteže gas-tečnost na umerenim pritiscima (do 6 bar) i različitim temperaturama (280-323 K). Peng-Robinson-ova jednačina stanja je korišćena za određivanje ravnotežnih svojstava. Pravila mešanja, kao što su van der Waals-ovo i kvadratno pravilo, su takođe korišćeni za određivanje kritičnih parametara smeše etanol-voda koji zahteva pseudo-kritičnu metodu kao jednu komponentu. Dobijeni rezultati su slični sa nedavno objavljenim empirijskim istraživanjima fazne ravnoteže. Ključne reči: ravnoteža gas-tečnost, CO2, smeša, umereni pritisak, Peng-Robinson-ova jednačina stanja. 346 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 347−357 (2013) S.E. MORADI1 J. KHODAVEISY2 R.DASHTI2 1 Young Researchers Club, Islamic Azad University - Sari Branch, Iran 2 Young Researchers Club, Islamic Azad University-Booshehr Branch, Iran SCIENTIFIC PAPER UDC 504.5:544.723.2:661.183:66.061.3 DOI 10.2298/CICEQ120204069M CI&CEQ REMOVAL OF ANIONIC SURFACTANTS BY SORPTION ONTO AMINATED MESOPOROUS CARBON Direct and indirect releases of large quantities of surfactants to the environment may result in serious health and environmental problems. Therefore, surfactants should be removed from water before release to the environment or delivery for public use. In the present work, the removal of anionic surfactants, benzene sulfonate (BS), p-toluene sulfonate (TS) and 4-octylbenzene sulfonate (OBS) from water by adsorption onto amino modified mesoporous carbon (AMC) were studied. The AMC surface chemistry and textural properties were characterized by nitrogen adsorption, XRD and FT-IR analyses. Experiments were conducted in batch mode with variables such as amount of contact time, solution pH, dose of adsorbent and temperature. Finally, the adsorption isotherms of anionic surfactants on mesoporous carbon adsorbents were in agreement with a Langmuir model. AMC has shown higher anionic surfactants adsorption capacity than the untreated mesoporous carbon, which can be explained by the strong interaction between the anionic surfactant and the cationic surface of the adsorbent. Keywords: aminating; mesoporous carbon; anionic surfactant; Langmuir model. Surfactants are widely used compounds, as their dual hydrophobic/hydrophilic nature makes them invaluable for flocculation, detergency and stabilization processes in industrial and domestic applications. There has been an exponential increase in the production and use of these substances over the past century. Despite the high biodegradability required by law for these products, the enormous amount of waste they produce has a severe impact on waters and soils [1-4]. A rough estimate of the worldwide surfactant production is 10 million tons per year, of which anionic surfactants account for about 60%. Anionic surfactants are popular detergent ingredients, because of their straightforward synthesis and consequently low production costs [5]. Surfactants in wastewaters can partly be biodegraded especially under aerobic conditions. However, under anaerobic conditions they are not biodegradable and show adverse effects on aquatic life. Correspondence: S.E. Moradi, Young Researchers Club, Islamic Azad University - Sari Branch 48164-194, Iran. E-mail: er_moradi@hotmail.com Paper received: 14 February, 2012 Paper revised: 14 June, 2012 Paper accepted: 2 July, 2012 Furthermore, they can act synergistically with some other toxic chemicals which may be present in wastewaters increasing their negative effects on the environment [6-8]. Moreover, the discharge of this compound into waters has produced numerous problems of environmental contamination and therefore a marked reduction in the quality of sources of drinking water. Therefore, the amount of surfactants present in wastewaters of many industries, especially detergent and textile, must be reduced at least to acceptable levels before discharging to the environment. The conventional methods for surfactant removal from water involve processes such as chemical and electrochemical oxidation, membrane technology, chemical precipitation, photo-catalytic degradation, adsorption and various biological methods [5,8]. Many of these processes are not cost effective and/or not suitable for application on a household scale. Adsorption technology can be of low cost and can be applied in small devices. It therefore offers potential for use on household scale, also in low-income households. At this stage of the project, re-use of the spent adsorbent is not considered. We propose to use an environmentally harmless absorbent that can be discarded or burnt as low-volume domestic waste. The preparation 347 S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… of low-cost adsorbents from waste materials has several advantages, mainly of economic and environmental nature. A wide variety of novel adsorbents have been recently prepared from different waste materials utilizing agricultural as well industrial and municipal wastes. Although many articles have been published [9-19] so far discussing the importance of low-cost adsorbents in water pollution control, many of them are generally either adsorbate-specific or adsorbent-specific. Recently, Ryoo et al. prepared ordered mesoporous carbons (CMK-x) from mesoporous silica templates such as MCM-48, SBA-1 and SBA-15 using sucrose as the carbon source [20–23]. Adsorption plays an important role in these processes. Therefore, the interactions of such compounds with the mesoporous carbon surface must be studied in detail. The mesoporous carbon materials adsorption capacity depends on quite different factors. Obviously, it depends on the mesoporous carbon’s characteristics: texture (surface area, pore size distributions), surface chemistry (surface functional groups) [24–26]. Mesoporous carbon materials with ordered pore structure, high pore volume, high specific surface area, and tunable pore diameters can be used as an effective adsorbent in industry. Due to its open pore structure and mesoporous properties, mesoporous carbon provides marked advantages over typical activated carbon in the adsorption and diffusion process [27]. Ordered mesoporous carbon materials have some superiority in contrast with microporous carbon adsorbents. The most important superiorities are given as higher specific surface area and specific pore volume that increases the contact area between adsorbent and adsorbate to reach to maximum of organic and inorganic molecules adsorption. Moreover, highly ordered structure and mesopore size of this novel ordered nanoporous carbon that affect on equilibrium time decrease for removal of pollutant. However, the hydrophobic and inert nature of mesoporous carbons can be unfavorable for several applications. Surface modification or functionalization of porous carbon materials is crucial not only for the development and application of hybrid mesoporous materials but also to change the hydrophobicity and hydrophilicity character of the surface of the materials in order to make them available as good adsorbents or catalysts for the selective removal of some organic contaminants [28]. The objective of this study is to investigate the adsorption characteristics of some anionic surfactants onto amino modified and unmodified mesoporous carbon adsorbents in relation to wastewater purifycation. The influence of the surface modification of 348 CI&CEQ 19 (3) 347−357 (2013) mesoporous carbon adsorbent was analyzed in terms of adsorption rate (adsorption kinetic) and capacity (adsorption isotherm) for anionic surfactants. Interestingly, it was found that the adsorption capability of different types of amino modified ordered mesoporous carbon for anionic surfactants is much higher compared to that of pristine mesoporous carbon. MATERIALS AND METHODS Materials The reactants used in this study were tetraethyl orthosilicate (TEOS) as a silica source, cetyltrimethylammonium bromide (CTAB) as a surfactant, sodium hydroxide (NaOH), sodium fluoride (NaF), deionized water for synthesis of mesoporous silica (MCM-48), sucrose as a carbon source, sulfuric acid as a catalyst for synthesis of mesoporous carbon, aqueous ammonia, sodium hydrosulfite, acetic anhydride, fuming nitric acid, and sulfuric acid as fictionalization agents, benzene sulfonate (BS), p-toluene sulfonate (TS) and 4-octylbenzene sulfonate (OBS). All chemicals were of analytical grade from Merck (Darmstadt, Germany). Working standard solutions were prepared by appropriate dilution of the stock standard solution. The following buffers were used to control the pH of water samples: hydrochloric acid–glycine (pH 1–3), sodium acetate–acetic acid (pH 3–6), disodium hydrogen phosphate–sodium dihydrogen phosphate (pH 6–8), and ammonium chloride–ammonia (pH 8–10). Synthesis of silica template and MC MCM-48 was prepared using CTAB as a surfactant and TEOS as a silica source, according to Shao et al. [29]. Briefly, 10 mL of TEOS was mixed with 50 mL of deionized water, and the mixture was vigorously stirred for 40 min at 35 °C, then 0.9 g of NaOH was added into mixture, and at the same time, 0.19 g of NaF was added into the mixture. After the NaF was added completely, the required content of sources, respectively, were added. After another 60 min of vigorous stirring, 10.61 g of CTAB was added to the mixture, and stirring continued for 60 min. The mixture was heated for 24 h at 393 K in an autoclave under static conditions, and the resulting product was filtered, washed with distilled water, and dried at 373 K. The sample was calcined at 823 K for 4 h in air to remove the surfactant completely. The product thus obtained was referred to as MCM-48. Then 1.25 g sucrose and 0.14 g H2SO4 were dissolved in 5.0 g H2O, and this solution was added to 1 g MCM-48. The sucrose solution corresponded approximately to the maximum amount of sucrose and sulfuric acid that S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… could be contained in the pores of 1 g MCM-48. The resultant mixture was dried in an oven at 373 K, and subsequently, the oven temperature was increased to 433 K. After 6 h at 433 K, the MCM-48 silica containing the partially carbonizing organic masses was added with an aqueous solution consisting of 0.75 g sucrose, 0.08 g H2SO4 and 5.0 g H2O. The resultant mixture was dried again at 373 K, and subsequently the oven temperature was increased to 433 K. The color of the sample turned very dark brown or nearly black. This powder sample was heated to 1173 K under vacuum using a fused quartz reactor equipped with a fritted disk. The carbon-silica composite thus obtained was washed with 1 M NaOH solution of 50% ethanol – 50% H2O twice at 363 K, in order to dissolve the silica template completely. The carbon samples obtained after the silica removal were filtered, washed with ethanol. Treatment before modification on MC The prepared MC was vacuum-dried at 110 °C for 24 h after being washed with deionized water until the electroconductivity of the filtrate became nearly the same as that of the water. It was then treated with hydrogen at 100 °C according to the previous report [30]. Surface modification was done by nitrating the carbon surface through electrophilic substitution and then aminating it through reduction. Reagent grade acetic anhydride, fuming nitric acid, and sulfuric acid were used as supplied in nitration. Distilled water for injection as the solvent, 28% aqueous ammonia, and reagent grade sodium hydrosulfite were employed as purchased in amination. Surface modification of mesoporous carbon AMC was prepared using MC, according to Abe et al. [31]. Briefly, nitration was allowed to proceed in a 1000 mL three-neck flask containing MC, acetic anhydride, and concentrated sulfuric acid with dropwise addition of fuming nitric acid in 5 h while keeping the temperature below 5 °C. The reaction was completed after 19 h of stirring at room temperature. Modified MC thus obtained was thoroughly washed with deionized water until the electroconductivity of filtrate attained a value nearly the same as that of the water and vacuum-dried for 24 h at 110 °C. Reduction of the nitrated mesoporous carbon was permitted to proceed in a 1000 mL flask containing deionized water, 28% aqueous ammonia, sodium hydrosulfite, and the carbon with stirring for 24 h in nitrogen atmosphere at room temperature. The aminated mesoporous carbon thus obtained was vacuum-dried at 110 °C after being washed with deionized water until the electroconductivity of filtrate became nearly the same CI&CEQ 19 (3) 347−357 (2013) as that of the water. This carbon sample is hereafter abbreviated to AMC. Characterization X-ray powder diffraction patterns were recorded on a Philips 1830 diffractometer using CuKα radiation (XRD, Philips Electronic Instruments, PW 1710). The diffractograms were recorded in the 2θ range of 0.8– 10 with a 2θ step size of 0.01° and a step time of 1 s. Adsorption-desorption isotherms of the synthesized samples were measured at 77 K on micromeritics model ASAP 2010 sorptometer (Norcross, GA, USA) to determine an average pore diameter. Pore-size distributions were calculated by the Barrett-JoynerHalenda (BJH) method, while surface area of the sample was measured by Brunaure-Emmet-Teller (BET) method. Elemental analysis was carried out to determine the amount of nitrogen-containing groups introduced onto mesoporous carbon surface with an elemental analyzer (CHN-O-RAPID type, Heraeous Co., Ltd.). Adsorption studies Each of the synthesized adsorbents was transferred to a 50 mL flask with a stopper, containing 50 mL of anionic surfactant dissolved in Mili-Q water. The initial concentrations of anionic surfactants in adsorption experiments were less than 2.1 mmol/L. After stirring for different times at 25 °C, the mixture was filtered through a Dismic filter (pore size 0.2 mm). The first 10 mL of filtrate was discarded and the rest was harvested for analysis by a UV–Vis spectrophotometer (Hitachi U2000 with 1 cm quartz cell) at 212, 222 or 224 nm for benzene sulfonate (BS), p-toluene sulfonate (TS) or 4-octylbenzene sulfonate (OBS), respectively. Samples with higher anionic surfactant concentration than CMC (critical micelle concentration) were analyzed after diluting to less than 2.1 mmol/L. The adsorption capacities were calculated based on the differences of the concentrations of solutes before and after the experiment according to Eq. (1) [32]: qe = (c 0 − c e )V W (1) where qe is the concentration of the adsorbed solute (mmol/g), c0 and ce are the initial and final (equilibrium) concentrations of the solute in solution (mmol/L), V (mL) is the volume of the solution and W (g) is the mass of the adsorbent. Adsorption kinetics of anionic surfactants For the measurement of the time resolved uptake of anionic surfactant onto adsorbents, 15 ml of 349 S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… distilled water was mixed with 60 mg of adsorbent in a 500 ml flask for about 10 min. 285 ml of anionic surfactant solution was quickly introduced into the flask (keeping the initial concentrations of the resulting solutions at 2.1 mmol/L) and stirred continuously at 20 °C. Samplings were done by fast filtration at different time intervals. The concentration of residual anionic surfactant in the solution was determined and the adsorption amount qt was calculated according to Eq. (2) [33]: qt = (c 0 − ct )V W where qt is the adsorption amount at time t, c0 is the initial concentration of anionic surfactant solution, ct is the concentration of anionic surfactant solution at time t, and V is the volume of anionic surfactants solution and m is the mass of MC and AMC. pH point of zero charge The suspension test of the carbonaceous adsorbent, to provide a quick and reliable way of determining the pH point of zero charge (pHPZC), was carried out using the pH drift method used by Yang et al. [34], with the modification that sodium chloride was used as an inert electrolyte. Prior to measurement of pH drift, the carbonaceous adsorbent was thoroughly washed with water followed by dilute sodium hydroxide (pH ∼10) to neutralize any free sulfuric acid that may have remained and finally soaked in HCl for 24 h. After filtration, it was washed with distilled water till the filtrate was free of chloride and sulfate ions as detected by AgNO3 and barium sulfate tests. The “enriched” carbon adsorbent was then air-dried. This was done to ensure the removal of any potential effects on pH drift due to dissolution of salts in carbon adsorbent. The pH of test solutions was adjusted in 0.005 M NaCl in the range between 1.92 and 10.90 using 0.5 M HCl or 0.5 M NaOH. Then, 0.06 g of carbonaceous adsorbent was added into 20 mL of the pH adjusted solution in a plastic capped vial and equilibrated for 24 h. The final pH was measured and plotted against the initial pH. The pH at which the curve crosses the pHinitial = pHfinal line was taken as pHPZC. RESULT AND DISCUSSION Characterization Nitrogen physisorption is the method of choice for gaining knowledge about mesoporous materials. This method gives information on the specific surface area and the pore diameter. Calculating pore diameters of mesoporous materials using the BJH 350 CI&CEQ 19 (3) 347−357 (2013) method is common. Former studies show that the application of the BJH theory gives appropriate qualitative results which allow a direct comparison of relative changes between different mesoporous materials. The nitrogen sorption isotherms of the MC and AMC have a typical type IV shape. Interestingly, the pore size distributions are essentially the same as before amine functionalization. The adsorption uptakes at relative pressure close to p/p0 = 0 are identical. However, the total uptakes are slightly different, (2) shown in decreasing with the surface modification. As Table 1, the decreases in the specific surface areas and pore volumes are 4.2 and 8.6%, respectively. From the nitrogen sorption isotherms (Figure 1) of mesoporous carbon type carbons before and after amine functionalization, it can be seen that after amine functionalization the obtained carbons still have type IV isotherms, indicating that mesoporousity is still preserved. However, the amine functionalization leads to a decrease in the total uptake of the amine functionalized carbons, which reflects the decrease of the total pore volume resulting from amine functionalization. Interestingly, the amine functionalized carbons essentially keep the bimodal pore size distribution, which is characteristic of the parent MC. The textural parameters listed in Table 1 clearly confirm the structural changes of amine functionalized MC. The variations of the surface area and pore volume are especially significant with the increase in the acid concentration. Table 1. Textural parameters of the MC and AMC employed in this study Adsorbent d Spacing, nm ABET / m2 g-1 Vp / cm3 g-1 MC 3.4 1010.5 0.69 AMC 3.1 967.4 0.63 In order to check the structural degradation, XRD data of AMC and MC were obtained on a Philips 1830 diffractometer using CuKα radiation of wavelength 0.154 nm. Figure 2 shows the XRD peaks of the samples. The XRD patterns of AMC showed three diffraction peaks that can be indexed to (110), (210), and (220) in the 2θ range from 0.8 to 10°, representing well-ordered cubic pores [20]. The XRD patterns of MC carbon and AMC (Figure 2) show wellresolved reflections indicating that MC carbon nicely maintains it original structure even after amine functionalization. For AMC sample, the cubic structure of MC was maintained well; but, the XRD reflections become less pronounced that might be due to the partial damage of the mesoporous (cubic) structure or S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… CI&CEQ 19 (3) 347−357 (2013) 600 MC Volume Adsorbed (cm3/g) STP 500 AMC 400 Pore Volume, (cm3/g) 300 200 100 0.4 0.3 0.2 0.1 0 0 5 10 Pore Diameter, (nm) 0 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 Relative Pressure (P/Po) Fig. 1. Adsorption-desorption isotherms of nitrogen at 77 K on MC and AMC. The insert shows the BJH pore size distribution calculated from the desorption branch of the isotherm. 6 5 MC AMC Intensity 4 3 2 1 0 0 1 2 3 4 2θ 5 6 7 8 9 Fig. 2. XRD Pattern of AMC and MC. due to the decreased contrast between walls and pores because of the cleavage of the carbon species from the pore walls. The FT-IR technique was used to monitor changes on the surface of the ordered mesoporous carbon and the content of the introduced nitrogen-containing functional surface group. Figure 3 shows the FT-IR spectra of MC and as treated AMC samples. A broad band at around 3450 cm −1 was observed in the MC sample. It was mainly caused by the O–H stretching vibration of the adsorbed water molecules, which also had a bending vibration mode corresponding to the band recorded at 1600 cm−1. Bands at 1600–1745 cm−1 denoted the absorption of stretching and bending vibration modes of –COOH on the surface of mesoporous carbon materials. In addition, the broad band that appeared at 1150 cm−1 was caused by the stretching vibration of C–O bonds. The AMC sample FT-IR showed that the surface amino group was produced after chemical modification, IR absorption bands for C-N bond stretching were detected at 1170-1240 cm-1, broad NH2 stretching at 3250–3450 cm-1, and an N-H deformation peak at 1640–1560 cm-1. Table 2 shows the results of elemental analysis performed to check if amino groups have really been introduced to the mesoporous carbon adsorbents. Since 2.1% of nitrogen was detected for AMC though no nitrogen was detected for MC, the results in the 351 S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… CI&CEQ 19 (3) 347−357 (2013) Fig. 3. FT-IR Spectra of MC and AMC samples. table demonstrate the presence of nitrogen-containing functional groups. Table 2. Elemental analyses of mesoporous carbons Sample %C %H %N MC 93.5 0.49 0 AMC 89.8 1.48 2.1 pH of point of zero charge for AMC and MC The pHPZC of any adsorbent is a very important characteristic that determines the pH at which the surface has net electrical neutrality. In this work the pH drift method was employed to determine this parameter. It was noted that despite extensive washing of the amino modified mesoporous carbon, the final pH after equilibration decreased rapidly as shown in Figure 4. The curve obtained cuts the pHinitial = 12 AMC MC 10 pHzpc(MC) = 5.34 pHzpc(AMC) = 4.05 Final pH 8 6 4 2 0 0 2 4 6 Initial pH 8 10 12 Fig. 4. Suspension test for determining the pH of point of zero charge of mesoporous carbon adsorbents by pH drift method. 352 S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… = pHfinal line at 4.05 (and 5.34 for MC). The importance of this value is that one can readily expect that removal of anionic surfactants is not feasible below this pH because the net positively charged surface is unlikely to attract the cations. This intrinsic acidity of the carbonaceous material is due to the treatment with concentrated sulfuric acid and could not be removed upon thorough washing with distilled water. CI&CEQ 19 (3) 347−357 (2013) process, the adsorption of benzene sulfonate on carbonaceous adsorbent was studied as a function of contact time and the results are shown in Figure 5. It is seen that the rate of uptake of the surfactant is rapid in the beginning and 50% adsorption is completed within 100 min. Figure 5 also indicates that the time required for equilibrium adsorption is 200 min. In order to be confident about equilibrium, the equilibration period was kept 300 min [35]. The effect of concentration on the equilibration time was also investigated as a function of initial surfactant concentration and the results are shown in Figure 6 (on Effect of contact time and concentration In order to establish equilibration time for maximum uptake and to know the kinetics of adsorption 2 Amount adsorbed (mmol.gr-1) 1.8 1.6 1.4 1.2 1 0.8 0.6 0.4 0.2 0 0 100 200 300 400 500 600 700 Contact time(min) Fig. 5. Effect of contact time on removal of anionic surfactant (benzene sulfonate = 2.1 mmol/L, agitation speed = 150 rpm, adsorbent dosage = 0.2 g/l, room temperature = 25 °C). 2 200 ppm 100 ppm 50 ppm 25 ppm Amount adsorbed (mmol gr-1) 1.8 1.6 1.4 1.2 1 0.8 0.6 0.4 0.2 0 0 100 200 300 400 500 600 700 Contact time (min) Fig. 6. Effect of initial concentration on removal of benzene sulfonate (agitation speed = 150 rpm, adsorbent dosage = 0.2 g/l, room temperature = 25 °C). 353 S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… zene sulfonate adsorbed (mmol g−1) at equilibrium and at any time. The equilibrium adsorption capacity (qe), and the second order constants (k2) can be determined experimentally from the slope and intercept of plot t/q versus t. The calculated qe, k2 and the corresponding linear regression correlation coefficient values are summarized in Table 3. R2 value is greater than 0.99. As seen from Table 3, the values of qe calculated from pseudo-second order kinetics almost agreed well with the experimental values of qe. These results indicate that the adsorption of benzene sulfonate on the amino modified mesoporous carbon follows pseudo-second order kinetics. AMC). At lower initial surfactant concentrations, sufficient adsorption sites are available for the sorption of benzene sulfonate. Conversely, the numbers of benzene sulfonate at higher initial concentrations are relatively more as compared to the available adsorption sites. Hence, the percentage of benzene sulfonate removal correlates inversely with the initial surfactant concentration. Kinetics of adsorption The study of adsorption kinetics is significant as it provides valuable insights into the reaction pathways and the mechanism of the reactions. Any adsorption process is normally controlled by the three diffusion steps: i) transport of the solute from bulk solution to the film surrounding the adsorbent, ii) from the film to the adsorbent surface and iii) from the surface to the internal sites followed by binding of the surfactants to the active sites. The slowest steps determine the overall rate of the adsorption process and usually it is thought that the step (ii) leads to surface adsorption and the step (iii) leads to intraparticle adsorption [36]. Several kinetic models are used to explain the mechanism of the adsorption processes. A simple pseudo-first order equation is given by the Lagergren equation [36]: log(q e − q ) = log q e − kit Effect of temperature on adsorption of anionic surfactants on MC The amount of benzene sulfonate adsorbed on mesoporous carbon depends on temperature and the chemical structure. The activation energy is the amount of energy required to ensure that a reaction happens. According to the Arrhenius equation: log k = -Ea/(2.303RT)+const. where qe and q are the amounts of benzene sulfonate adsorbed (mmol/g) at equilibrium time and any time t, respectively, and k1 is the rate constant of adsorption (min−1). A plot of log (qe−q) versus t gives a straight line for first order adsorption kinetics, which allows computation of the rate constant k1. The calculated qe, k1 and the corresponding linear regression correlation coefficient values are summarized in Table 3. As seen from Table 3, the calculated linear regression correlation coefficient was relatively small (R2 = 0.984) and the experimental qe values did not agree with the calculated values obtained from the linear plots. The pseudo-second order equation based on equilibrium adsorption is expressed as [36]: t 1 t = + 2 q k 2q e q e (5) where k is the rate coefficient, Ea is the activation energy, R (8.314 J mol−1 K−1) is the universal gas constant, and T is the temperature (K), we found the activated energy for benzene sulfonate. After linearization of the Arrhenius equation, we achieved the values of the activated energy for benzene sulfonate 15.03 J mol-1. According to the results, the amount of benzene sulfonate adsorbed on the mesoporous carbon increased with an increase in temperature. As it is widely agreed, the adsorption is a spontaneous exothermic process but according to the results, anionic surfactant adsorption increases with the increase in temperature. It has been suggested that in aqueous solution the anionic surfactant forms a hydrated complex containing up to six water molecules attached to each unit and therefore a decrease in surfactant–water hydrogen bonding with increase in temperature can explain the higher adsorption capacity. (3) 2.303 CI&CEQ 19 (3) 347−357 (2013) Effect of surface modification In order to evaluate the efficacy of the prepared adsorbents, the equilibrium adsorption of the anionic surfactants was studied as a function of equilibrium concentration. The adsorption isotherms of benzene (4) where k2 is the pseudo-second order rate constant (g mmol−1 min−1), qe and q represent the amount of ben- Table 3. Pseudo-first order and pseudo-second order constants for the removal of benzene sulfonate by AMC Pseudo-first order constants qe,exp / mmol g 1.48 354 –1 qe,cal / mmol g 1.01 –1 Pseudo-second order constants –1 k1 / g mmol min 0.024 –1 2 R qe,cal / mmol g–1 k2 / g mmol–1 min–1 R2 0.984 1.45 0.026 0.996 S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… sulfonate (BS), p-toluene sulfonate (TS) and 4-octylbenzene sulfonate (OBS) on AMC and MC are shown in Figures 7 and 8. It is seen that order of adsorption in terms of amount adsorbed (mmol/g) on different adsorbents is: AMC > MC. It is interesting that the amount of anionic surfactants adsorbed increases with increasing solution pH for both samples. Further, AMC registers higher anionic surfactants adsorption capacity (2.1, 1.7 and 1.4 mmol/g for benzene sulfonate (BS), p-toluene sulfonate (TS) and 4-octylbenzene sulfonate (OBS)) than the untreated mesoporous carbon (1.1, 0.87 and 0.71 mmol/g for benzene sulfonate (BS), p-toluene CI&CEQ 19 (3) 347−357 (2013) sulfonate (TS) and 4-octylbenzene sulfonate (OBS)). The higher adsorption capacity of AMC can be explained by the undoubtedly increasing interaction as a result of the amino functional group in AMC. It means that a new and strong interaction between the anionic surfactant and cationic surface of the adsorbent is introduced [37]. Langmuir and Freundlich isotherms In order to indicate the sorption behavior and to estimate the adsorption capacity, adsorption isotherms were studied. The adsorption processes of benzene sulfonate were tested with Langmuir and 1.2 1 Amount adsorbed, (mmol/gr) OBS TS BS 0.8 0.6 0.4 0.2 0 0 0.2 0.4 0.6 0.8 1 Equilibrium concentration, (mmol/lit) 1.2 1.4 1.6 Fig. 7. Adsorption isotherm for benzene sulfonate (BS), p-toluene sulfonate (TS) and 4-octylbenzene sulfonate (OBS) on MC (contact time = 300 min, agitation speed = 150 rpm, adsorbent dosage = 0.2 g/l, room temperature = 25 °C). Amount adsorbed, (mmol/gr) 2.5 OBS TS BS 2 1.5 1 0.5 0 0 0.2 0.4 0.6 0.8 1 Equilibrium concentration, (mmol/lit) 1.2 1.4 1.6 Fig. 8. Adsorption isotherm for benzene sulfonate (BS), p-toluene sulfonate (TS) and 4-octylbenzene sulfonate (OBS) on AMC (contact time = 300 min, agitation speed = 150 rpm, adsorbent dosage = 0.2 g/l, room temperature = 25 °C). 355 S.E. MORADI, J. KHODAVEISY, R.DASHTI: REMOVAL OF ANIONIC SURFACTANTS… Freundlich isotherm models. Two commonly used empirical adsorption models, Freundlich and Langmuir, which correspond to heterogeneous and homogeneous adsorbent surfaces, respectively, were employed in this study. The Freundlich model is given by: ln q e = ln K f + 1 n ln c e (6) where Kf and n are the Freundlich constants related to adsorption capacity and intensity, respectively. In the second model, the Langmuir equation assumes maximum adsorption occurs when the surface is covered by the adsorbate, because the number of identical sites on the surface is finite. The Langmuir equation is given as: ce 1 1 = + c q e q mb q m (7) where qe (mmol/g) is the amount adsorbed at equilibrium concentration ce (mmol/L), qm (mmom/g) is the Langmuir constant representing maximum monolayer capacity and b is the Langmuir constant related to energy of adsorption. The isotherm data was linearized using the Langmuir equation. The regression constants are shown in Table 4. The high value of correlation coefficient indicated good agreement between the parameters. The same data was also fitted by the Freundlich equation (Table 4). The value of correlation coefficients showed that the data conform well to the Langmuir equation. CI&CEQ 19 (3) 347−357 (2013) The kinetic data was best fitted to the pseudo-second order model and adsorption isotherm was fitted well by the Langmuir model. Isotherm data at 25 °C were fitted by the Langmuir model better than the Freundlich model. 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Mittal, J. Colloid Interface Sci. 335 (2009) 24-33 Table.4. Langmuir and Freundlich constants for adsorption of benzene sulfonate on carbonaceous adsorbents Adsorbent Langmuir Freundlich qm / mmol g–1 b / L mmol–1 R2 KF / mmol g–1 n / L mmol–1 R2 MC 0.67 5.62 0.998 0.89 3.22 0.981 AMC 1.48 2.96 0.987 1.55 3.23 0.964 CONCLUSIONS [12] V.K. Gupta, A. Mittal, V. Gajbe, J. Mittal, J. Colloid Interface Sci. 319 (2008) 30-39 In this work, the performance of aminated mesoporous carbon was investigated using tree different nonionic surfactants. The structural order and textural test (XRD, BET and FT-IR spectroscopy) confirm the proper structure on unmodified and modified mesoporous carbon sorbents. It is found that the AMC can efficiently adsorb the surfactants BS, TS, OBS and DBS from water solutions predominantly by hydrophobic interactions. 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KHODAVEISY2 R.DASHTI2 UKLANJANJE ANJONSKIH SURFAKTANATA SORPCIJOM NA AMINOVANOM MEZOPOROZNOM UGLJENIKU 1 Young Researchers Club, Islamic Azad University - Sari Branch, Iran 2 Young Researchers Club, Islamic Azad University-Booshehr Branch, Iran NAUČNI RAD Direktno i indirektno oslobađanje velikih količina surfaktanata u životnu sredinu može dovesti do ozbiljnih zdravstvenih i ekoloških problema. Stoga je neophodno ukloniti surfaktante iz vode pre ispuštanja u životnu sredinu ili upotrebu. U ovom radu je proučavano uklanjanje anjonskih surfaktanta, benzen-sulfonata (BS), p-toluensulfonata (TS) i 4-oktilbenzen-sulfonata (OBS), iz vode adsorpcijom na amino modifikovanom mezoporoznom ugljeniku (AMC). Hemija AMC površine i osobine same teksture su proučavane adsorpcijom azota, XRD i FTIR analizom. Eksperimenti su izvođeni u šaržnom režimu pri različitim operativnim uslovima, kao što su kontaktno vreme, pH rastvora, količina adsorbenta i temperatura. Na kraju, adsorpcione izoterme anjonskih surfaktanata na mezoporoznom ugljeniku opisane su Langmuir-ovim modelom. AMC je pokazao veći adsorpcioni kapacitet anjonskog surfaktanta od netretiranog mezoporoznog ugljenika, što se može objasniti jakim interakcijama između anjonskog surfaktanta i katjonske površine adsorbensa. Ključne reči: aminacija; mezoporozni ugljenik; anjonski surfaktant; Langmuir-ov model. 357 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 359−368 (2013) XIAO-QIN XIONG KE-JING HUANG CHUN-XUAN XU CHUN-XUE JIN QIU-GE ZHAI College of Chemistry and Chemical Engineering, Xinyang Normal University, Henan, Xinyang, China SCIENTIFIC PAPER UDC 544.6:547.436:66.012.1 DOI 10.2298/CICEQ120325070X CI&CEQ GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-GRAPHENE COMPOSITE FILM FOR DETERMINATION OF ACETAMINOPHEN AND CAFFEINE A novel electrochemical sensor poly(taurine)/TiO2-graphene nanocomposite modified glassy carbon electrode (PT/TiO2-Gr/GCE) was fabricated. This sensor was based on an electrochemically polymerized taurine layer on a TiO2-graphene modified glassy carbon electrode. The electrochemical behavior of acetaminophen and caffeine at the modified electrode was studied by cyclic voltammetry and differential pulse voltammetry. The results showed that the oxidation peak currents of acetaminophen and caffeine were linear with their concentrations in the range of 1×10-7-9×10-5 M and 2.5×10-5-2×10-4 M, respectively. The detection limits of acetaminophen and caffeine were 3.4×10-8 M and 5.0×10-7 M, respectively (S/N = 3). This modified electrode showed good sensitivity and stability, which has promising potential applications in electrochemical sensors and biosensors design. Keywords: taurine; TiO2-graphene nanocomposite; acetaminophen; caffeine; electropolymerization. Acetaminophen (N-acetyl-p-aminophenol or paracetamol), an antipyretic and analgesic drug, is widely used in the world. It is used mainly as an effective medicine for the relief pain and reduction of fever and a suitable alternative for patients who are sensitive to aspirin [1-5]. Caffeine (3,7-dihydro-1,3,7-trimethyl-1H-purine-2,6-dione) is a natural alkaloid N-methyl derivative of xanthine, and is extensively present in foods such as coffee, tea, cola nuts, yerbamate, guarana berries and cacao bean. Caffeine ingestion exerts many physiological effects, such as stimulation of the central nervous system, diuresis and gastric acid secretion [2]. The unique properties of caffeine are also applied in analgesic preparations. Therefore, acetaminophen and caffeine often occur together in analgesic pharmaceutical formulations. Generally, limited use of acetaminophen and caffeine does not exhibit any harmful side effects. However, overdosed ingestions of acetaminophen lead to the accumulation of toxic metabolites, which Correspondence: K-J. Huang, College of Chemistry and Chemical Engineering, Xinyang Normal University, Henan, Xinyang 464000, China. E-mail: kejinghuang@163.com Paper received: 25 March, 2012 Paper revised: 3 July, 2012 Paper accepted: 3 July, 2012 may cause severe and sometimes fatal heptatotoxicity and nephrotoxicity, which in some cases associate with renal failure [4-7]. Caffeine is considered to be a risk factor for cardiovascular diseases and may have behavior effects such as depression and hyperactivity. Therefore, in analgesic preparation ca. 200 mg per day of dosage is generally recommended [8]. It is vital to establish a simple, sensitive, accurate methodology for simultaneous determination of acetaminophen and caffeine. Some methods including titrimetry [9], spectrophotometry [10-12], liquid chromatography [13-15] and electrochemistry [3,4,6, 16-22] have been developed for the individual estimation of two molecules. Only a few methods have been reported for the determination of acetaminophen and caffeine. Lau et al. used perchloric acid-methanol (1:1) as the solvent and electrolyte to improve the sensitivity and peak separation of acetaminophen and caffeine. Obviously, it is difficult to make quantitative determination due to the addition of easily evaporating methanol [23]. Zen and Ting used a nafion/ruthenium oxide pyrochlore chemically modified electrode for the simultaneous determination of acetaminophen and caffeine in drug formulation by square-wave voltammetry. The experiments were completed in 0.05 M perchloric acid, high cost reagent with controlled sale [8]. Fatibello-Filho et al. used a boron-doped diamond 359 X.-Q. XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… (BDD) electrode for acetaminophen and caffeine simultaneous determination. However, prior to the experiments, this electrode was cathodically pretreated in a 0.5 mol L-1 H2SO4 solution [2]. Sanghavi et al. used an in situ surfactant-modified multi-walled carbon nanotube paste electrode for simultaneous determination of acetaminophen and caffeine. An accumulation potential of -0.7 V and an accumulation duration time of 300 s were used for stripping voltammetric analysis [24]. Recently, graphene (Gr) was found to be an ideal two-dimensional (2D) catalyst support to anchor metal and semiconductor catalyst nanoparticles because of its unique two-dimensional geometric structure, large surface area, and high mobility of charge carriers [25]. Being a famous semiconductor, TiO2 has received much attention due to its nontoxicity, long-term stability, low cost and mutifunctions [26]. Most recently, we reported the TiO2-Gr nanocomposite prepared by hydrothermal method using graphene as templates to immobilized TiO2 nanoparticles. The as-prepared TiO2-Gr exhibited remarkable electrocatalytic activity toward dopamine oxidation [23]. Taurine is a well-known dissociated amino acid, which exhibits important physiological functions and pharmacological characteristics. It has been widely used as a food nutrition enhancer and common drug. Taurine possesses electron-rich N atoms and high electron density of sulfonic groups. Hence, the poly(taurine) (PT) film is negatively charged and is propitious to adsorb acetaminophen and caffeine from the solution. PT modified electrodes have been reported and have shown good electrochemical performance [27, 28]. In this work, we report about the fabrication of PT modified electrode by electrochemical polymerization of taurine on the TiO2-Gr-modified glassy carbon electrode (PT/TiO2-Gr/GCE) and the application of the modified electrodes for simultaneous detection of acetaminophen and caffeine. EXPERIMENTAL Chemicals and materials Graphite powder (320 mesh, spectrum pure) was purchased from Sinopharm Chemical Reagent Co., Ltd., China. Titanium isopropoxide (Ti(OiPr)4) was obtained from Aladdin Chemistry Co., Ltd., China. Acetaminophen and caffeine were purchased from Alfa Aesar and used without further purification. Taurine was purchased from Shanghai No. 1 Chemical Company (Shanghai, China). The phosphate buffer solution (PBS) was prepared using Na2HPO4 360 CI&CEQ 19 (3) 359−368 (2013) and NaH2PO4. Double distilled water was used to prepare all solutions used in the present work. Apparatus All electrochemical experiments were carried out with a CHI660D electrochemical workstation (CH Instruments, Shanghai). A conventional three-electrode system was used for all electrochemical experiments, which consisted of a platinum wire as counter electrode, an Ag/AgCl/3M KCl as reference electrode, and a bare or modified glassy carbon electrode (3mm diameter) as working electrode. All pH measurements were measured with a PHS-3C digital pH meter (Shanghai Rex Instrument Factory, Shanghai, China). A Hitachi S-4800 scanning electron microscope (SEM) was used. Preparation of TiO2-graphene nanocomposite Graphene oxide was synthesized from graphite powder according to the modified Hummers method [29,30]. Gr was obtained by the chemical reduction of a colloidal suspension of exfoliated graphene oxide sheets in water with hydrazine hydrate [31]. To prepare TiO2-Gr nanocomposite, Gr (50 mg), titanium isopropoxide (0.2 mL) and H2SO4 (1 M, 2 mL) was firstly added into a 25-mL Teflon-sealed autoclave. This resultant mixture was ultrasonicated for 10 min, and then the autoclave was kept in oven for 24 h at the temperature of 170 °C. Finally, black powder of TiO2-Gr nanocomposite was obtained by filtration, rinsed thoroughly with deionized water and methanol, and dried in vacuum [25]. Preparation of the modified electrodes The as-prepared TiO2-Gr nanocomposite (1.5 mg) was dispersed in DMF (4.0 mL) to form a homogenous suspension. Before modification, glass carbon electrode (GCE) was polished to a mirror-like with 0.3 and 0.05 µM of alumina slurry, and then washed successively with ultrapure water, anhydrous alcohol and ultrapure water in an ultrasonic bath and dried in N2 flow. The TiO2-Gr film-modified GCE (TiO2-Gr/GCE) was prepared by dropping 6 µL of the resultant suspension on the cleaned GCE, and dried at room temperature. The PT/GCE and PT/TiO2-Gr/GCE were prepared as follows. Cyclic voltammetry (CV) was used to form polymerization film on the bare GCE and TiO2-Gr/GCE, respectively. The polymeric film was deposited by cyclic sweeping from -1.5 to 2.0 V at 100 mVs-1 for 10 cycles in PBS (pH 7.0) containing 2.0×10-3 M taurine. The obtained electrodes were individually noted as PT/GCE and PT/TiO2-Gr/GCE. X.-Q. XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… Serum sample preparation Human blood serum samples were obtained from healthy volunteers. The samples were centrifuged at 4000 rpm for 30 min at room temperature. Then 1.2 mL of acetonitrile was added to remove serum protein, followed by fortification with acetaminophen and caffeine. After vortexing for 1 min, the mixture was centrifuged for 10 min at 10000 rpm to remove the serum protein residues. The supernatant was taken carefully and appropriate volumes of this supernatant were transferred into the electrochemical glass cell and diluted up to the volume with the PBS. RESULTS AND DISCUSSION Surface morphology of TiO2-graphene and poly(taurine)/TiO2-graphene composite The surface morphologies of TiO2-Gr and PT/TiO2-Gr composite were examined by SEM observation (Figure 1). In Figure 1A, it can be seen that TiO2 was formed in a highly faceted morphology on the substrates of Gr with ca. 20-30 nm diameter for the clusters. As shown in the SEM images, the asprepared TiO2-Gr nanocomposite exhibited considerable edge plane defect structures. These edge plane defects have shown to be essentially responsible for the high electron transfer kinetics and the electrocatalytic activity of Gr, which contributed significantly to the electrochemical property of the present TiO2-Gr nanocomposite as well. Figure 1B depicts the SEM image of the PT/TiO2-Gr composite, showing that a layer of PT was formed on the TiO2-Gr surface. The electropolymerization of taurine at the TiO2-graphene/GCE In the previous reports, repeated cyclic voltammetry was used for the electrochemical formation of PT film. The potential scan range was the most CI&CEQ 19 (3) 359−368 (2013) important factor. If the positive value for polymerization was below 1.6 V or if the negative one was above -0.8 V, no polymer reaction occurred [26]. Therefore, we selected the potential range of -1.5 and 2.0 V as the electropolymerization potential window in this work. Figure 2 shows CVs of electrochemical polymerization of taurine on the TiO2-Gr/GCE. One obvious reduction peak was observed at -0.7 V. An increase in cycle number results in the enhancement of the peak currents and a slight shift of potential peak, which was reflecting the continuous growth of the film. It could be observed that the film growth was faster for the first four cycles than for the other cycles. After modification, a shiny and light green color was found on the electrode surface. These facts indicated taurine was deposited on the surface of TiO2-Gr film modified GCE by electropolymerization. The inset of Figure 2 shows CVs of electrochemical polymerization of taurine on the GCE, and a similar phenomenon was obtained. Effect of different electrodes In the present study, the electrochemical behavior of the mixture containing acetaminophen and caffeine on the aforementioned electrodes (bare GCE, TiO2-Gr/GCE, PT/GCE, PT/TiO2-Gr/GCE) was investigated using the CV. Figure 3 depicts CVs curves of the acetaminophen and caffeine (0.1 mM) in PBS (0.1 M, pH 7.0) at a scan rate of 100 mVs-1. A well shaped oxidation peak and a poorly defined reduction peak on the bare GCE was observed (curve a). The height of the reduction peak was lower than that of the oxidation peak. For caffeine, the oxidation peak was characterized by an extraordinarily asymmetric shape and no obvious reduction peak was observed on the reverse scan, indicating that the oxidation was irreversible. The oxidation peak potentials of acetaminophen and caffeine at bare GCE are 461 (A) (B) Figure 1. SEM of TiO2-Gr (A) and PT/TiO2-Gr (B). 361 X.-Q. XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… 100 CI&CEQ 19 (3) 359−368 (2013) 10 0 100 I / µA I / µA 1 -100 0 -100 -200 -1.5 -1.0 -0.5 0.0 0.5 1.0 1.5 E/V -200 -1.5 -1.0 -0.5 0.0 0.5 1.0 1.5 E/V Figure 2. Cyclic voltammograms for the polymerization of taurine on the TiO2-Gr/GCE. Inset: cyclic voltammograms for the polymerization of taurine on bare GCE. Scan rate of 100 mV s-1. The supporting electrolyte: 0.1 M phosphate buffer (pH 7.0). 40 20 I / μA 0 -20 -40 c b -60 a d -80 -100 0.0 0.3 0.6 0.9 1.2 1.5 E/V Figure 3. Cyclic voltammetric curves of 110 µM acetaminophen and 320 µM caffeine in PBS (pH 7.0) on the different electrode: a) bare GCE, b) TiO2-Gr/GCE, c) PT/GCE and d) PT/TiO2-Gr/GCE. and 1433 mV, respectively. Compared to bare GCE, the oxidation peak potential of acetaminophen at the PT/GCE (curve c) shifted 23 mV negatively, and the peak current decreased slightly. However, caffeine showed the oxidation peak current increased slightly without the change of peak potential. To TiO2-Gr/ /GCE, acetaminophen and caffeine demonstrated broad oxidation peaks at 539 and 1476 mV, respectively. The charging current was obviously larger than that at both the above electrodes (curve b). Also, the peak current of acetaminophen enhanced slightly. The highest improvement of the oxidation peak currents of acetaminophen and caffeine was obtained at the PT/TiO2-Gr/GCE (curve d). These phenomena indicated that the enhancement effect may be due to the synergetic effect of PT and TiO2-Gr. The PT film 362 might facilitate the adsorption of acetaminophen and caffeine from the solution to the modified electrode surface through physical adsorption by the improvement of area of the modified electrode. Moreover, the coarseness of the modified electrode surface also contributed to this. Effect of scan rate The effect of scan rate was also studied at the PT/TiO2-Gr/GCE. Figure 4 showed that the oxidation peak shifted to a more positive value for both compounds, and the reduction peak of acetaminophen shifted to more negative values with increasing scan rates that had concurrent increases in current. For acetaminophen, the plot of the anodic peak current (ip) vs. the square root of scan rate showed excellent X.-Q. XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… CI&CEQ 19 (3) 359−368 (2013) 30 I / µA 0 a -30 -30 I / µA -40 -60 i ACOP -50 -60 -70 -90 CF -80 9 10 11 12 13 14 15 16 -1 1/2 (Scan rate / mV ) 0.0 0.3 0.6 0.9 E/V 1.2 1.5 Figure 4. Cyclic voltammetric response of the PT/TiO2-Gr/GCE to 70 µM acetaminophen and 210 µM caffeine in 0.1 M BPS (pH 7.0) at various scan rates (a-r): 90, 110, 130, 150, 170, 190, 210, 230 and 250 mV s-1. Inset: peak current vs. v1/2. linearity over the range of 90-250 mV s-1, the corresponding equation was: ip (μA) = -3.38(v / mV s–1)1/2 + + 5.927 (R = 0.999) (inset a of Figure 4). Similarly, as shown in inset to Figure 4, the oxidation peaks currents of caffeine increased linearly with the increase of square root of scan rate, the corresponding equation was: ip (μA) = -4.658(v / mV s–1)1/2 - 4.637 (R = = 0.999). This revealed that the oxidation processes of acetaminophen and caffeine on the surface of PT/ /TiO2-Gr/GCE were under diffusion control. Effects of supporting electrolyte The electrode reaction can be affected by the buffer solution. The effect of different electrolyte on the current responses was investigated. Some electrolytes including KHP-NaOH, NH4Cl, NaH2PO4Na2HPO4, BR, NaNO3, KCl and NH3-NH4Cl (each 0.1 M) were studied. The results showed that high current peaks and good peak shape were obtained in phosphate buffer. Therefore, this solution was applied in the subsequent studies. Effect of pH The effect of varying pH of buffer solution on the electrochemical behavior of acetaminophen and caffeine at PT/TiO2-Gr/GCE was performed using CV in 0.1 M PBS. Figure 5 depicts the response of peak current and potential of acetaminophen and caffeine to pH. The anodic and cathodic peak potentials were shifted negatively when the solution pH was increased (Figure 5D). The anodic peak current of acetaminophen increased from pH 3.0 to 7.0 and reached the maximum at pH 7.0, and then decreased again with higher pH value (Figures 5A and 5C). The anodic peak current of caffeine increased from pH 3.0 to 7.0 and kept almost unchanged in the pH range of 7.0-9.0 (Figure 5B). To obtain the high response signal for acetaminophen and caffeine, the solution of pH 7.0 was used for the optimal supporting electrolyte. Effect of TiO2-graphene amount The effect of TiO2-Gr amount was investigated. When the amount of TiO2-Gr suspension (0.375 mg mL-1) increased from 0 to 6 µL, the oxidation peak current of acetaminophen and caffeine increased notably. However, when it exceeded 6 µL, the oxidation peak currents conversely showed gradual decline. Therefore, 6 µL of TiO2-Gr suspension was selected for the fabrication of the electrochemical sensor in this work. Simultaneous determination of acetaminophen and caffeine Under the optimal experiment conditions, the simultaneous determination of acetaminophen and caffeine was carried out at PT/TiO2-Gr/GCE. The experiment was performed by changing the equal concentrations of acetaminophen and caffeine over the range from 5×10-7 to 1×10-4 M. The differential pulse voltammetric results (Figure 6) showed two well-distinguished anodic peaks at potentials of 396 and 1372 mV, corresponding to the oxidation for acetaminophen and caffeine, respectively. The peak current values were proportional to the concentrations of acetaminophen and caffeine in the mixture. The insert of Figure 6 showed the relationship between the anodic currents and the concentrations of acetaminophen (curve a) and caffeine (curve b). The oxidation 363 X.-Q. XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… 40 10 A 20 -20 I / µA 0 I / µA CI&CEQ 19 (3) 359−368 (2013) -20 -40 B -50 -80 -60 a f g a -110 -80 -100 0.0 -40 0.3 0.6 0.9 1.2 0.9 1.5 1.0 1.1 E/V 1.2 1.3 1.4 1.5 E/V 1.8 C D 1.5 -50 ACOP E/V I / µA 1.6 -60 CF 1.2 0.9 0.6 -70 CF ACOP 0.3 -80 0.0 3 4 5 6 pH 7 8 9 10 3 4 5 6 pH 7 8 9 10 Figure 5. A) Cyclic voltammograms of 160 µM of acetaminophen at PT/TiO2-Gr/GCE with different pH values of PBS (0.1 M) (a-f): pH 3, 4, 5, 7, 8 and 9; B) cyclic voltammograms of 390 µM caffeine at PT/TiO2-Gr/GCE with different solution pH values (a-f): pH 3, 4, 5, 6, 7, 8 and 9; C) peak current vs. pH value; D) peak potential vs. pH value. peak current of acetaminophen was proportional to its concentration over the range from 0.5 to 100 µM, obeying the following equation: I (µA) = -0.302(C / / µM) - 6.143 (R = 0.991). The oxidation peak current of caffeine was proportional to its concentration over the range from 0.5 to 100 µM, obeying the following equation: I (µA) = -0.186(C / µM) + 0.255 (R = 0.994). The detection limits of acetaminophen and caffeine were 3.4×10-8 and 5.0×10-7 M, respectively. A comparison of the detection methods are shown in Table 1, which includes the limit of detection and the linear range. Table 1 indicates that the proposed sensor exhibited low detection limit and wide measurement range. The reason might be as follows: firstly, the excellent electrical conductivity of Gr enhanced the charge transport; secondly, the formation of the PT film increased the adsorb amount of analytes. Individual determination of acetaminophen and caffeine For further investigation of electrochemical response when both substances are present in the solu- 364 tion, the DPV experiments were performed in solutions containing variable concentration of one species and constant concentration of the other one. The separate determination of acetaminophen in the concentration range of 1.0×10-7-9.0×10-5 M was accomplished in solutions containing caffeine at the fixed concentration of 3.0×10-5 M. As shown in Figure 7A, the peak current of acetaminophen clearly increased gradually while that of caffeine remained fairly constant, suggesting that the change of acetaminophen did not have significant influence on the peak currents and peak potentials of the caffeine. On the other hand, the separate determination of caffeine in the concentration range of 2.5×10-5-2.0×10-4 M was accomplished in solutions containing acetaminophen at the fixed concentration of 1.0×10-6 M. As shown in Figure 7B, the peak current of caffeine increased gradually while that of acetaminophen remained fairly constant. Furthermore, the peak currents of acetaminophen or caffeine increased linearly with the increase of concentration in the presence of a constant concentration of the other compound (insert in Figure 7A X.-Q. XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… CI&CEQ 19 (3) 359−368 (2013) 0 h -10 I / μΑ -40 I / µA -30 CF -20 -30 a ACOP -40 0 -20 20 40 60 80 100 C / μΜ -10 0 0.0 0.3 0.6 0.9 1.2 1.5 E/V Figure 6. Differential pulse voltammograms of PT/TiO2-Gr/GCE in 0.1 M PBS (pH 7.0) containing equal concentrations of acetaminophen and caffeine: a) 0.5, b) 5, c) 7.5, d) 10, e) 25, f) 50, g) 75 and h) 100 µM. Inset: calibration plots of the oxidation peak current versus different concentration of acetaminophen and caffeine. and 7B). The calibration equations were ipa (µA) = = -0.543(C / µM) - 2.432 (R = 0.990) and ipa(µA) = = -0.179(C / µM) - 0.654 (R = 0.993) for acetaminophen or caffeine, respectively. The detection limits were 3.4×10-8 and 5.0×10-7 M, respectively. Hence, it was confirmed that for the oxidation of acetaminophen and caffeine at PT/TiO2-Gr/GCE, the other component did not give interference to the electrochemical signal. Interference study Under the optimized conditions, the influence of various foreign species on the simultaneous determination of acetaminophen and caffeine (50 µM) was investigated in PBS (pH 7.0). It was found that the common ions such as Na+, K+, Fe3+, Cu2+, Al3+, Cl-, NO3-, H2PO4-, HPO42-, CO32-, and SO42- had almost no interference with acetaminophen and caffeine detection. As for the common interferences in pharmaceutical samples for the determination of acetaminophen and caffeine, 10-fold sodium carbonate, saccharin, citric acid, ascorbic acid, glucose, uric acid had no obvious interference with the current response of acetaminophen and caffeine (signal change below 5%). Stability, reproducibility and repeatability In order to investigate the stability of PT/TiO2Gr/GCE, the reproducibility was tested. Repetitive CV Table 1. Comparison of electrochemical sensors for acetaminophen (ACOP) and caffeine (CF) Modified electrode Linear range, μM LOD / μM Reference Screen-printed carbon electrode ACOP: 2.5-1000 ACOP : 0.1 [1] Carbon-doped diamond electrode ACOP: 0.5-83; CF: 0.5-83 ACOP: 0.49; CF: 0.035 [2] Palladium nanoclusterspolyfuran/platinum electrode ACOP: 0.5-100 ACOP: 0.0764 [3] ZrO2 nanoparticles/carbon paste electrode ACOP: 1.0-2500 ACOP: 0.912 [4] ACOP: 0.1-20 ACOP: 0.032 [6] ACOP: 5-250; CF: 10-250 ACOP: 2.2; CF: 1.2 [8] ACOP: 1.0-100 ACOP: 0.5 [17] CF: 5-200 CF: 2.0 [19] CF: 0.995-10.6 CF: 0.798 [20] Graphene/GCE Nafion/ruthenium oxide pyrochlore/GCE Poly(taurine)/multiwalled carbon nanotube/GCE Nafion-ruthenium oxide pyrochlore/GCE Nafion/GCE Carbon nanotubes/carbon-ceramic electrode Dowex50wx2 and gold nanoparticles/glassy carbon paste electrode In situ surfactant-modified multi-walled carbon nanotube paste electrode PT/TiO2-GR/GCE ACOP: 0.2-100.0 ACOP: 0.12 [21] ACOP: 0.0334-42.2 ACOP: 0.0047 [22] ACOP, CF: 0.291-62.7 ACOP: 0.0258; CF: 0.0883 [24] ACOP, CF: 0.05-100 ACOP: 0.034; CF: 0.5 This work 365 X.-Q. XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… -50 0 A I / µA -10 -40 j f 0 -30 -10 -30 0 20 40 60 C / µM 80 100 -40 -20 a -30 -20 a I / μΑ -40 -50 -20 B -60 -20 I / µA I / µA CI&CEQ 19 (3) 359−368 (2013) -40 30 60 90 120 150 180 210 C / μΜ -10 0 0 0.0 0.3 0.6 0.9 1.2 1.5 0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 E/V E/V Figure 7. A) Differential pulse voltammograms of PT/TiO2-Gr/GCE in 0.1M BPS (pH 7.0) containing 30 µM caffeine and different concentrations of acetaminophen: a) 0.1, b) 1, c) 3, d) 5, e) 7, f) 10, g) 30, h) 50, i) 70 and j) 90 µM. Inset: plot of oxidation peak current as a function of acetaminophen concentration. B) Differential pulse voltammograms of PT/TiO2-Gr/GCE in 0.1 M BPS (pH 7.0) containing 1 µM acetaminophen and different concentrations of caffeine: a) 25, b) 50, c) 70, d) 90, e) 100 and f) 200 µM. Inset: plot of oxidation peak current as a function of caffeine concentrations. measurements were performed 20 times in 0.1 M PBS (pH 7.0). The relative standard deviations (RSD) were 1.81 and 3.17% for acetaminophen (100 µM) and caffeine (100 µM), respectively. This result suggested that this sensor had a good reproducibility and did not undergo surface fouling during the voltammetric measurements. The stability of PT/TiO2-Gr/GCE towards the catalytic oxidation of acetaminophen (100 µM) and caffeine (100 µM) was examined as well. The CVs of this binary solution were recorded after this electrochemical sensor has been dipped into PBS (pH 7.0) for 2 weeks. The anodic current responses of acetaminophen and caffeine individually decreased 4.25 and 4.83%, indicating that the good stability of developed sensor. Furthermore, the repeatability between multiple PT/TiO2-Gr modified glassy carbon electrodes was carried out by parallel determining of 100 µM acetaminophen and caffeine mixture. The RSD was 3.29% for 6 independent glassy carbon electrodes modified with PT/TiO2-Gr. Analytic application In order to testify the performance of this modified electrode in real sample analysis, four serum samples from the hospital affiliated to our university were examined by the developed electrochemical sensor and the high-performance liquid chromatography (HPLC) method, respectively. The concentrations of acetaminophen and caffeine were measured by the standard addition method, and the results showed that no acetaminophen and caffeine were found in the four serum samples. To test the reliability of the measurements, a known amount of acetaminophen and caffeine standard was spiked in the serum samples, and then analyzed with a standard addition method. The obtained results were shown in Table 2. The recoveries were in the range of 95.6% to 103.5%. It was in accordance with the result obtained by using HPLC, which indicated the developed was reliable and feasible. Table 2. Determination of acetaminophen and caffeine in human serum samples Serum sample Detected by PT/TiO2-GR/GCE Detected by HPLC Added, µM Found, µM RSD / % Recovery,% Found, µM RSD / % ACOP 5 4.86 2.6 97.2 5.11 1.5 CF 10 9.56 2.4 95.6 9.82 1.8 2 ACOP 30 30.72 3.1 102.4 29.1 2.1 CF 50 49.05 2.4 98.1 49.2 1.6 3 ACOP 80 77.36 3.6 96.7 78.6 2.2 CF 120 124.2 1.9 103.5 125.1 2.7 4 ACOP 150 152.4 2.2 101.6 147.3 1.8 CF 200 195.6 1.8 97.8 197.5 2.0 1 366 X.-Q. XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… CI&CEQ 19 (3) 359−368 (2013) CONCLUSION [11] Sirajuddin; A.R. Khaskheli, A. Shah, M.I. Bhanger, A. Niaz, S. Mahesar, Spectrochim Acta, A 68 (2007) 747-751 In this work, a novel type of polymer/TiO2-Grmodified glassy carbon electrode was prepared and used for the simultaneous determination of acetaminophen and caffeine. The modified electrode exhibited many desirable properties including excellent stability, reproducibility, high sensitivity, low detection limit and satisfactory linear range. Furthermore, its ease to construct, low cost and no treatment before use make it feasible to be applied in routine determination. [12] H. Filik, I. Sener, S.D. Cekic, E. Kilic, R. Apak, Chem. Pharm. Bull. 54 (2006) 891-896 [13] S. Ravisankar, M. Vasudevan, M.M. Gandhimathi, B. Suresh, Talanta 46 (1998) 1577-1581 [14] A. Goyal, S. Jain, Acta Pharm. Sci. 49 (2007) 147-151 [15] P.S. Selvan, R. Gopinath, V.S. Saravanan, N. Gopal, S. A. Kumar, K. Periyasamy, Asian J. Chem. 19 (2007) 1004-1010 [16] J.C. Song, J. Yang, J.F. Zeng, J. Tan, L. Zhang, Sens. Actuators, B 155 (2011) 220-225 [17] Q.J. Wan, X.W. Wang, F. Yu, X.X. Wang, N.J. Yang, A.J. Bard, L.R. Faulkner, J. Appl. Electrochem. 39 (2009) 785–790 Acknowledgments This work was supported by the National Natural Science Foundation of China (20805040), Program for Science and Technology Innovation Talents in Universities of Henan Province (2010HASTIT025), Excellent Youth Foundation of He’nan Scientific Committee (104100510020), and the Foundation of He’nan Education Committee (2009A150023). REFERENCES [1] P. Fanjul-Bolado, P. J. Lamas-Ardisana, D. HernándezSantosa, A. Costa-García, Anal. Chim. Acta 638 (2009) 133-138 [2] B.C. Lourencão, R.A. Medeiros, R.C. Rocha-Filho, L.H. Mazo, O. Fatibello-Filho, Talanta 78 (2009) 748-752 [3] N.F. Atta, M.F. EI-Kady, A. Galal, Sens. Actuators, B 141 (2009) 566-574 [18] T.L. Lu, Y.C. Tsai, Sens. Actuators, B 153 (2011) 439-444 [19] J.M. Zen, Y.S. Ting, Y. Shih, Analyst 123 (1998) 1145-1147 [20] B. Brunetti, E. Desimoni, P. Casati, Electroanal. 19 (2007) 385-388 [21] B. Habibi, M. Jahanbakhshi, M.H. Pournaghi-Azar, Electrochim. Acta 56 (2011) 2888-2894 [22] B.J. 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XIONG et al.: GLASSY CARBON ELECTRODE MODIFIED WITH POLY(TAURINE)/TIO2-… XIAO-QIN XIONG KE-JING HUANG CHUN-XUAN XU CHUN-XUE JIN QIU-GE ZHAI College of Chemistry and Chemical Engineering, Xinyang Normal University, Henan, Xinyang, China NAUČNI RAD CI&CEQ 19 (3) 359−368 (2013) ELEKTRODA OD STAKLASTOG UGLJENIKA MODIFIKOVANA POLI(TAURIN)/TIO2-GRAFEN KOMPOZITNIM FILMOM ZA ODREĐIVANJE ACETAMINOFENA I KOFEINA Napravljena je nova elektroda od staklastog ugljenika modifikovana poli(taurin)/TiO2-grafen nanokompozitnim filmom (PT/TiO2-Gr/GCE). Ovaj senzor je zasnovan na elektrohemijskoj polimerizaciji taurinskog sloja na TiO2 grafen modifikovanoj elektrodi od staklastog ugljenika. Elektrohemijsko ponašanje acetaminofena i kafeina na modofikovanim elektrodama je proučavano cikličnom volatmetrijom i diferencijalnom pulsnom voltametrijom. Rezultati pokazuju da oksidacioni pik struje ima zadovoljavajuću linearnost u opsegu koncentracija od 1×10-7-9×10-5 M za acetaminofen i 2.5×10-5-2×10-4 M za kafein. Limit detekcije za acetaminofen je 3.4×10-8 M, a za kofein 5.0×10-7 M. Ova modifikovana elektroda je pokazala dobru osetljivost i stabilnost, pa ima obećavajuću potencijalnu primenu kao dobar elektrohemijski senzor i biosenzor. Ključne reči: taurin; TiO2-grafen nanokomposit; acetaminofen; Kofein; elektropolimerizacija. 368 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 369−375 (2013) JELENA Đ. MARKOVIĆ NATAŠA LJ. LUKIĆ ALEKSANDAR I. JOKIĆ BOJANA B. IKONIĆ JELENA D. ILIĆ BRANISLAVA G. NIKOLOVSKI University of Novi Sad, Faculty of Technology, Novi Sad, Serbia SCIENTIFIC PAPER UDC 66.045.1:66.06:5/.6 DOI 10.2298/CICEQ120309071M CI&CEQ 2D SIMULATION AND ANALYSIS OF FLUID FLOW BETWEEN TWO SINUSOIDAL PARALLEL PLATES USING LATTICE BOLTZMANN METHOD In order to obtain better heat transfer, it is important to enhance fluid mixing in heat exchangers. Since there are negative effects when heat exchangers are operating in the turbulent regime (such as significant pressure drop and increased size of the pump), it is necessary to apply techniques that would provide better fluid mixing when heat exchangers are operating in the laminar regime. Investigations have shown that the use of sinusoidal instead of flat plates results in this effect. This study is a result of two-dimensional simulation of fluid flow between two parallel sinusoidal plates. Simulation was done with the use of modified OpenLB code, based on the lattice Boltzmann method. The Reynolds number was varied from 200 to 1000, and the space between the plates was varied from 3 to 5 cm. The results showed that sinusoidal plates enhance fluid mixing, especially with greater values of Re and smaller space between the plates, which is in agreement with previous investigations. Keywords: lattice Boltzmann, fluid flow, sinusoidal plates, plate heat exchanger, simulation. In heat exchanger design it is very important to obtain good fluid mixing, reduce heat transfer resistance, and minimize pressure drop. Good fluid mixing can be obtained in heat exchangers working in the turbulent regime, which, on the other hand, has a significant pressure drop as a negative effect. When operating in the turbulent regime, the pumping cost increases as the size of the pump increases, which is often a limiting factor, especially in compact heat exchangers or in heat exchangers with very viscous fluids. Enhancement of fluid mixing in laminar regime, which leads to better heat transfer, is possible to obtain when chaotic fluid flow is established. Chaotic advection occurs when pathlines that do not conform to laminar regime are present in the fluid, and can be generated in ducts with periodically perturbed geometry in downstream direction. In order to obtain better heat transfer in plate heat exchangers, several techniques have been used so far. One of the most often applied techniques was Correspondence: J.Đ. Marković, University of Novi Sad, Faculty of Technology, Bulevar cara Lazara 1, 21000 Novi Sad, Serbia. E-mail: jmarkovic@tf.uns.ac.rs Paper received: 9 March, 2012 Paper revised: 27 June, 2012 Paper accepted: 4 July, 2012 the use of wavy plates instead of flat plates [1], and many investigations showed that use of sinusoidal instead of flat plates enhances heat transfer without significant pressure drop [2-7]. The aim of this study was to simulate and analyze the fluid flow between two parallel sinusoidal plates with the use of the lattice Boltzmann method (LBM). In recent years, LBM has developed into an alternative and promising numerical scheme for simulating fluid flows and modeling physics in fluids. Unlike conventional numerical schemes based on discretizations of macroscopic continuum equations, the LBM is based on microscopic and mesoscopic kinetic equations. THEORETICAL PART Lattice Boltzmann Method The fundamental idea of the LBM is to construct simplified kinetic models that incorporate the essential physics of microscopic or mesoscopic processes so that the macroscopic averaged properties obey the desired macroscopic equations. Even though it is based on a particle picture, its principal focus is the averaged macroscopic behavior. The kinetic equation 369 J.Đ. MARKOVIĆ et al.: 2D SIMULATION AND ANALYSIS OF FLUID FLOW… provides many of the advantages of molecular dynamics, including clear physical pictures, easy implementation of boundary conditions, and fully parallel algorithms. Because of the availability of very fast and massively parallel machines, there is a current trend to use the code that can exploit the intrinsic features of parallelism. The LBM fulfills these requirements in a straightforward manner. The kinetic nature of the LBM introduces three important features that distinguish it from other numerical methods. First, the convection operator (or streaming process) of the LBM in phase space (velocity space) is linear. The feature is borrowed from kinetic theory, and contrasts with the nonlinear convection terms in other approaches that use a macroscopic representations. Simple convection combined with a relaxation process (or collision operator) allows the recovery of the nonlinear macroscopic advection trough multi-scale expansions. Second, the incompressible Navier-Stokes (NS) equations can be obtained in the nearly incompressible limit of the LBM. The pressure of the LBM is calculated using n equations of state. In contrast, in the direct numerical simulation of the incompressible NS equations, the pressure satisfies a Poisson equation with velocity strains acting as sources. Solving this equation for the pressure often produces numerical difficulties requiring special treatment, such as iteration or relaxation. Third, the LBM utilizes a minimal set of velocities in phase space. In the traditional kinetic theory with the Maxwell-Boltzmann equilibrium distribution, the phase space is a complete functional space. The averaging process involves information from the whole velocity phase space. Because only two speeds and only a few moving directions are used in LBM, the transformation relating the microscopic distribution function and macroscopic quantities is greatly simplified. The LBM originated from lattice gas (LG) automata, a discrete particle kinetics utilizing a discrete lattice and discrete time, which consists of a regular lattice with particles residing on the nodes. A set of Boolean variables ni(x,t) (i = 0,…,M) describing the particle occupation is defined, where M is the number of directions of the particle velocities at each node. The evolution equation of the LG automata is as follows: ni ( x + e i ,t + 1) = ni ( x ,t ) + Ω(n ( x ,t )), i = 0,1…, M (1) where ei are local particle velocities starting from an initial state. The configuration of particles at each time step evolves in two sequential sub-steps: a) streaming, in which each particle moves to the nearest node in the direction of its velocity and b) collision, which 370 CI&CEQ 19 (3) 369−375 (2013) occurs when particles arriving at a node interact and change their velocity directions according to scattering rules. For simplicity, the exclusion principle (no more than one particle being allowed at a given time and node with a given velocity) is imposed for memory efficiency and leads to a Fermi-Dirac local equilibrium distribution. The main feature of the LBM is to replace the particle occupation variables, ni (Boolean variables), in Eq. (1) by single-particle distribution functions (real variables), f i ni , and neglect individual particle motion and particle-particle correlations in the kinetic equations, where denotes an ensemble average. An important simplification of the LBM was made by linearization of the collision operator by assuming that the distribution is close to the local equilibrium state. An enhanced collision operator approach which is linearly stable was proposed [10]. A particular linearized version of the collision operator makes use of relaxation time towards the local equilibrium using a single time relaxation. The relaxation term is known as the Bhathnagar-Gross-Krook (BGK) collision operator and has been independently suggested by several authors [11,12]. In this lattice BGK model (LBGK), the local equilibrium distribution is chosen to recover the Navier-Stokes macroscopic equations. Use of LBGK model makes the computations more efficient and allows flexibility of the transport coefficients [13] . Lattice Botlzmann equations The lattice Boltzmann equation (LBE) is an explicit time-marching finite-difference representation of the continuous Boltzmann equation in phase space and time. The LBE incorporating the single relaxation BGK approximation has the form [11]: f i ( x + c i Δt ,t + Δt ) − f i ( x ,t ) = ω [f i eq ( x ,t ) − f i ( x ,t )] (2) where ω ≡ Δt / τ denotes the relaxation factor with limits 0 < ω < 2, c s = c / 3 is the speed of sound, and c = Δx / Δt. The kinematic viscosity is given by the relaxation factor: ν = (2 / ω − 1)Δxc / 6 (3) The local equilibrium distribution is an analog version of the Maxwellian distribution function for incompressible flows, and is expressed as: f i eq ( x ,t ) = w i ρ [1 + c iAu A u Au B c iAc iB + ( − δ AB )] 2c s2 c s2 c s2 (4) In these expressions, the flow properties are defined as: Flow density: ρ = f i i (5) J.Đ. MARKOVIĆ et al.: 2D SIMULATION AND ANALYSIS OF FLUID FLOW… Momentum: ρu A = f i c iA (6) iA In the equations above, sub-indices A and B denote the components of the Cartesian coordinates with implied summation for repeated indices. Furthermore, wi is the weighting which can be determined to achieve isotropy of the fourth-order tensor of velocities and Galilean invariance [11]. Applying the Chapman-Enskog expansion, the continuity equation and the Navier-Stokes equations can be recovered exactly at the second order approximation from the LBE if the density variation is sufficiently small [14]. For the D2Q9 (two-dimensional nine velocities) models, the weightings in Eq. (4) are assigned as follows: w i = 4 / 9 for c i = 0 (i.e., static particle), w i = 1/ 9 for c i = 1 , and w i = 1/ 36 for c i = 2 . The lattice Boltzmann method applies two essential steps, namely collision and propagation, to reveal the flow phenomena at the mesoscopic scale. Hence, the corresponding computations of LBM are performed as: Collision step: fi ( x ,t ) = f i ( x ,t ) + ω [f i eq ( x ,t ) − f ( x ,t )] (7) Propagation step: f i ( x + c i Δt ,t + Δt ) = fi ( x ,t ) (8) where fi denotes the post-collision state of the distribution function. From Eqs. (7) and (8), it is clear that the collision process is fully local and the propagation of the distribution functions is uniform. As a result, the lattice BGK scheme is very simple when applied with the unity lattice size (i.e., Δx = Δy = 1 ), and a relative time step of Δt = 1 such that c = Δx / Δt = 1 [15]. Boundary conditions The simulation was done with modified OpenLB LBM code with the use of bounce back boundary conditions. To generate the solid boundary of an obstacle, links between neighbouring nodes are selected to best confirm to the shape of the obstacle. The nodes CI&CEQ 19 (3) 369−375 (2013) just outside the boundary no longer communicate with their neighbours inside the obstacle. Instead, a particle striking this boundary bounces back in the direction from which it arrived. The bounce-back boundary condition is known to model, to first order, a boundary which lies halfway between these boundary nodes and the neighbouring fluid nodes. It is apparent that the boundary condition cannot directly model a general curvilinear surface but instead uses a stair-step approximation of the surface. The bounce-back condition is implemented in the lattice Boltzmann scheme after the particle distribution is updated. After the particle distribution is computed, the boundary condition reverses the direction of each component of particle distribution just inside the boundary. These components leave the boundary during the following time step. In irregular geometries, even with the use of a staircase approximation of domain boundaries, it is quite difficult attributing the right boundary type to each cell. In this approach, particle populations that are opposite to each other are swapped at each iteration step, and no additional collision is executed. The advantage of this procedure is that it is independent of the orientation of the domain. For the D2 Q9 scheme, the boundary conditions at the wall are given as f2 = f4, f5 = f7 and f6 = f8. f7 is bouncing back from left hand side lattice in the solid wall and f8 is bouncing back from the right hand lattice in the solid wall in reference to the main lattice location. f4, f7 and f8 are known from the streaming process. To ensure no-slip conditions velocity at the wall is set to zero. For low values of Re number calculations were numerically stable, but for Re > 1000, depending on the separation of the channel, in most cases it became numerically unstable [16]. Geometry of the model The geometry of plates used in the simulation is given in Figure 1, while Eq. (9) defines the sine function used for plate geometry description. Figure.1. Geometry model of parallel plates. 371 J.Đ. MARKOVIĆ et al.: 2D SIMULATION AND ANALYSIS OF FLUID FLOW… h = Ax sin( 2π x λx ) (9) where h is the height of the plate at a given coordinate x, Ax wave amplitude in the x direction, and λx is a wavelength in the x direction. Dimensions used in the calculations are: Ax = 0.45 cm, λx = 8.334 cm and Havg = 4 cm. The dimensionless geometric parameters that describe the corrugated plate model are given as λx = λx / H avg and β x = Ax / H avg , where Havg is the separation between corrugated plates that form the channel, which was varied from 3 to 5 cm throughout the investigation. The Reynolds number was defined as: Re = V inH avg ν CI&CEQ 19 (3) 369−375 (2013) number and the wavelength from the channel inlet increase, the recirculation regions increase in size and begin to cover a larger region of the channel. At the large Reynolds number, a weak recirculation region appears in wave 1 as well as other types of instabilities. These instabilities are rolling vortices that appear in the limits between the principal flow and the upper part of the recirculation. (10) where Vin is the average velocity at the inlet of the corrugated plates and υ is the kinematic viscosity [1]. RESULTS AND DISCUSSION The criterion used to determine if one wave has macroscopic mixing is the presence of crossing paths in the central flow, broken recirculation regions or too big vortices compared to wave amplitude. Flow mixing occurs when the core flow undergoes large oscillations, resulting in large changes in the position of the reattachment point of the free shear layer. When the reattachment point moves far enough upstream, the core flow impinging on the wall “injects” freestream fluid into the separation bubble; this injection is accompanied by “ejection” of fluid from the separation bubble into the core flow. This dynamically driven exchange of fluid results in macroscopic mixing [6]. Low Reynolds number was set at 200, while the upper limit was 1000. The flow pattern is very much like the one reported in previous investigations [6,17]. At small Reynolds numbers there are steady recirculation regions along the sinusoidal channel. At very low velocities (Re ≈ 200) there were no recirculation regions throughout the channel. In general, the flow moves and tries to follow the channel shape. This case is a typical Stokes flow since the viscous forces dominate the flow pattern. Steady recirculation regions could be observed in the first wave for Reynolds larger than 200. More recirculation regions are observed along the channel as the Reynolds number increases. Eventually, recirculation regions and rolling vortices appear throughout the entire channel. Figures 2 and 3 show the flow pattern that appears in this type of channel. Recirculation regions do not cover the entire wave. As the Reynolds 372 Figure 2. Pathlines; Havg = 4 cm, Re = 800. When the Reynolds number is increased the separation point moves closer to the beginning of the wave, and the reattachment point is closer to the end of the wave. In this case there are not symmetric recirculation regions, which can also be observed in Figures 2 and 3. As the Reynolds number increases, instabilities appear in waves closer to the channel inlet. At the large Reynolds number (Re ≈ 800), some waves present random particle paths that promote macroscopic mixing over all the separation between the plates. It was observed that the wave number from inlet where macroscopic mixing first occurs, decreases as the Reynolds number increases. Macroscopic mixing was rarely observed in wave 1, even at large Reynolds numbers. For large Havg, it becomes difficult J.Đ. MARKOVIĆ et al.: 2D SIMULATION AND ANALYSIS OF FLUID FLOW… appear. The vortices appear at the beginning of the wave and move downstream to the end of the wave, where they join the main core flow. When there are waves in the channel with macroscopic mixing, there are always waves with rolling vortices upstream from this wave. However, it is not necessarily true that macroscopic mixing exists when rolling vortices exist. It is believed that instabilities in the central flow are created by rolling vortices and flow asymmetry. Finally, it is important to mention that rolling vortices and macroscopic mixing move closer to the channel inlet as the Reynolds number increases. In addition to the appearance of macroscopic mixing, which is also always followed by rolling vortices in downstream direction, it can be inferred that rolling vortices instabilities appear at lower Reynolds numbers than macroscopic mixing instabilities. This behavior is independent of Havg (Figure 4; Tables 1 and 2). Table 1 shows, for a range of the Re number, the closest wave number from the inlet, in which rolling vortices appear compared to experimental data found in literature [1]. The data in Table 1 shows that the increase of the average separation between plates promotes rolling vortices to appear at larger Reynolds numbers. For example, with Havg = 5 cm and Re = 800 there is already a rolling vortex in wave 4, but there is a rolling vortex in wave 2 for Havg = 4 cm and Re = 800. This indicates that increasing the average separation between plates makes the flow pattern in the channel steadier. Decreasing the average separation between plates promotes macroscopic mixing to appear at for macroscopic mixing to appear even in waves relatively far from the inlet. Figure 3. Pathlines; Havg = 4 cm, Re = 400. In the limits between the principal flow and the upper part of the recirculation region, rolling vortices Wave number CI&CEQ 19 (3) 369−375 (2013) 10 9 8 7 6 5 4 3 2 1 0 0 200 400 600 800 1000 1200 Re Wave with rolling vortices Wave with macroscopic mixing Figure 4. Comparison of the position of the first wave that presents the position of the rolling vortices and the position of the first wave that represents macroscopic mixing, Havg = 5 cm. 373 J.Đ. MARKOVIĆ et al.: 2D SIMULATION AND ANALYSIS OF FLUID FLOW… lower Reynolds numbers; this behavior is similar to those of rolling vortices. Table 1. Number of wave with rolling vortices counted from the inlet - comparison of the experimental data from the literature [1] and simulation data Wave number, Havg / cm Re 3 4 5 3 Experimental data 4 5 Simulation data 200 6 8 - 6 7 8 300 5 7 8 4 6 7 400 3 6 7 3 4 6 500 2 4 6 3 4 5 600 2 3 4 2 3 4 700 2 3 4 2 3 4 800 2 3 4 2 3 3 900 2 2 3 2 2 3 1000 2 2 3 2 2 3 Table 2. Number of wave with macroscopic mixing counted from the inlet - comparison of the experimental data from the literature [1] and simulation data Wave number, Havg / cm Re 3 4 5 3 Experimental data 4 For Re values from 500 to 1000 wave numbers are identical. The closest wave number from the inlet that presents macroscopic mixing can be observed in Table 2, as a function of Re number for simulation data and experimental data found in literature [1]. The data in Table 2 shows that wave 6 presents macroscopic mixing up to Re = 800 and Havg = 5 cm, while wave 4 at Havg = 4 cm already has macroscopic mixing at Re = 800. This proves that increase of Havg makes it more difficult for the macroscopic mixing to appear. Simulations results compared are in a very good agreement with experimental data from the literature. For lower Re values in some cases there are differences, like for Havg = 3 cm and Re = 200, the first wave with macroscopic mixing according to experimental data is wave number 8, while simulations results show that it is wave number 7. For Re values from 600 to 1000 results are almost identical. There is difference for Havg = 4 cm and Re values 700 and 800, where simulation shows that the first wave is wave number 4, but experimental results show that the first wave with macroscopic mixing is wave number 3 [18]. 5 CONCLUSIONS Simulation data 200 8 8 8 7 7 8 300 7 7 7 7 7 7 400 6 5 7 7 6 7 500 5 5 7 5 6 6 600 5 4 6 5 5 6 700 4 3 6 4 4 6 800 3 3 6 4 4 6 900 3 3 6 3 3 6 1000 3 3 6 3 3 6 It can be seen that not only the visualized flow pattern, but also the number of wave where the rolling vortices first appear at given Re number is in a good agreement with previous investigations. For Havg= 3 cm first wave in which rolling vortices appear differs for Re 300 and 500. For Re 300 in simulation data rolling vortices appear in wave number 4, while experimental data shows that they appear in wave number 5. When Re is 500 there is an opposite behavior, experimental data shows appearance of rolling vortices in wave number 2, while simulation results show that it appears in the next wave, number 3. Situation is quite similar for Havg = 4 cm and Havg = 5 cm. For Re values up to 500 there are slight variations of first appearance of rolling vortices. Simulations results compared to experimental data in some cases show that they appear one wave before or one wave after. 374 CI&CEQ 19 (3) 369−375 (2013) The visualized flow pattern for given geometry of the heat exchanger agrees well with previous numerical and experimental investigations, which showed that the application of lattice Boltzmann method is successful in range of low Re values. It is known that macroscopic mixing is an effective way to enhance the heat transfer and mixing in sinusoidal plates because of its random particle trajectories and although it is in some ways an interesting phenomenon - capable of improving the heat transfer and the stirring in sinusoidal plates, it does not appear in waves very near the channel inlet at the small Reynolds number range. Previous investigations showed that enhancement of fluid mixing and formation of recirculation regions improves heat transfer. However, additional investigation on the heat transfer should be performed in order to obtain more information about the influence of recirculation regions, vortex formation, and chaotic mixing on the heat transfer enhancement. Acknowledgement This research was financially supported by the Ministry of Education, Science and Technological Development of the Republic of Serbia (Project No. 46010). J.Đ. MARKOVIĆ et al.: 2D SIMULATION AND ANALYSIS OF FLUID FLOW… CI&CEQ 19 (3) 369−375 (2013) REFERENCES [10] F.J. Higuera, J. Jimenez, Europhys. Lett. 9 (1989) 663–668 [1] B. Giron-Palomares, A. Hernadez-Guerrero, R. RomeroMendez, F. Oviedo-Tolentino, Int. J. Heat Fluid Flow 30 (2009) 158-171 [11] Y.H. Qian, D. d'Humieres, P. Lallemand, Europhys. Lett. 17 (1992) 470–484 [12] [2] P. Gschwind, A. Regele, V. Kottke, Exp. Therm. Fluid Sci. 11 (1995) 270-275 H. Chen, S. Chen, W.H. Matthaeus, Phys. Rev., A 45 (1992) 5339-5542 [13] [3] Y. Islamoglu, C. Parmaksizoglu, Appl. Therm. Eng. 24 (2004) 141-147 S. Chen, G.D. Doolen, Annu. Rev. Fluid Mech. 30 (1998) 329-364 [14] [4] J.Y. Jang, L.K. Chen, Int. J. Heat Mass Transfer 40 (1997) 3981-3990 Y.H. Qian, S.A. Orszag, Europhys. Lett. 21 (1993) 255–259 [15] [5] S. Mahmud, A.K.M.S. Islam, M.A.H. Mamun, Int. J. Eng. Sci. 40 (2002) 1495-1509 P.H. Kao, R.J. Yang, J. Comp. Phys. 227 (2008) 5671–5690 [16] [6] T.A. Rush, T.A. Newell, A.M. Jacobi, Int. J. Heat Mass Transfer 42 (1999) 1541-1553 J. Latt, J.M. Krause, OpenLB User Guide, available from: http://www.openlb.org/ [17] [7] R. Sawyers, M. Sen, C. Hsueh-Chia, Int. J. Heat Mass Transfer 41 (1998) 3559-3573 C.C. Wang, C.K. Chen, Int. J. Heat Mass Transfer 45 (2002) 2587-2595 [18] [8] J. Hardy, O. de Pazzis, Y. Pomeau, Phys. Rev. (1976) 4320-4327 J. Markovic, N. Lukic, D. Jovicevic, APTEFF 41 (2010) 1-203. [9] U. Frisch, B. Hasslacher, Y. Pomeau, Phys. Rev. Lett. (1986) 1505-1508 JELENA Đ. MARKOVIĆ NATAŠA LJ. LUKIĆ ALEKSANDAR I. JOKIĆ BOJANA B. IKONIĆ JELENA D. ILIĆ BRANISLAVA G. NIKOLOVSKI Univerzitet u Novom Sadu, Tehnološki fakultet, Novi Sad, Srbija NAUČNI RAD 2D SIMULACIJA I ANALIZA STRUJANJA FLUIDA IZMEĐU DVE PARALELNE SINUSOIDALNE PLOČE PRIMENOM LATTICE BOLTZMANN METODE U cilju postizanja boljeg prenosa toplote, neophodno je poboljšati mešanje fluida u razmenjivačima toplote. S obzirom na to da postoje negativni efekti pri radu razmenjivača toplote u turbulentnom režimu (kao što su značajni pad pritiska i potreba za većom pumpom) moraju se primeniti tehnike koje će obezbediti bolje mešanje fluida pri radu razmenjivača toplote u laminarnom režimu. Istraživanja su pokazala da upotreba sinusodialnih umesto ravnih ploča daje upravo ovakav rezultat. U radu su predstavljeni rezultati dvodimenzione simulacije strujanja fluida između dve paralelne sinusoidalne ploče. Simulacija je rađena modifikacijom OpenlB koda, na bazi lattice Boltzmann metode. Rejnoldsov broj prilikom simulacije je variran od 200 do 1000, a razmak između ploča od 3 do 5 cm. Rezultati pokazuju poboljšano mešanje fluida, naoročito pri većim vrednostima Rejnodsovog broja, što je u skladu sa prethodnim istraživanjima. Ključne reči: lattice Boltzmann metod, strujanje fluida, sinusoidalne ploče, pločasti razmenjivači, simulacija. 375 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 377−384 (2013) S. RAMESH R. MUTHUVELAYUDHAM R. RAJESH KANNAN T. VIRUTHAGIRI Department of Chemical Engineering, Annamalai University, Annamalainagar, Tamilnadu, India SCIENTIFIC PAPER UDC 547.455.526:543:547.458.87(540) DOI 10.2298/CICEQ120315072R CI&CEQ RESPONSE SURFACE OPTIMIZATION OF MEDIUM COMPOSITION FOR XYLITOL PRODUCTION BY Debaryomyces hansenii var. hansenii USING CORNCOB HEMICELLULOSE HYDROLYSATE Optimization of the culture medium for xylitol production using Debrayomyces hansenii var. hansenii was carried out. The optimization of xylitol production using corncob hemicelluloses hydrolysate as substrate was performed with statistical methodology based on experimental designs. The screening of nine nutrients for their influence on xylitol production was achieved using a PlackettBurman design. MgSO4⋅7H2O, KH2PO4, (NH4)2SO4 and yeast extract were selected for based on their positive influence on xylitol production. The selected components were optimized using Response Surface Methodology (RSM). The optimum conditions were: MgSO4⋅7H2O - 1.02 g/l, (NH4)2SO4 – 3.94 g/l, KH2PO4 – 2.74 g/l and yeast extract – 3.45 g/l. These conditions were validated experimentally, which revealed an enhanced xylitol yield of 0.76 g/g. Keywords: xylitol; corncob; Debaryomyces hansenii var. Hanseni; optimization; RSM. Xylitol is one of the most expensive polyol sweeteners and considerable attention in the food and pharmaceutical industries. They have medicinal applications such as tooth decay, ear infection for children, substitute for sugar to diabetic patients and parenteral application to trauma patients [1-3]. Xylitol is increasingly being used in chewing gum, candy, soft drinks, ice creams and hygiene products. Currently, xylitol is produced by chemical hydrogenation using nickel as a catalyst [4]; however, this process is expensive. There are several steps involved in the purification of xylose before the chemical reaction [5-7]. The microbial conversion of xylose to xylitol is particularly attractive in that the process is relatively easy and does not need toxic catalyst [8]. Xylitol production through bioconversion has been proposed to alternative process utilizing microorganism such as yeast, bacteria and fungi [9,10]. Among those, yeast has some desirable properties and was proven to be a potential xylitol producer [11,12]. In the Correspondence: S. Ramesh, Department of Chemical Engineering, Annamalai University, Annamalainagar-608002, Tamilnadu, India. E-mail: Ramesh_lecturer@yahoo.co.in Paper received: 15 March, 2012 Paper revised: 14 May, 2012 Paper accepted: 9 July, 2012 present study, yeast strain of species Dabaryomyces hansenii var. hansenii were selected for xylitol production. Furthermore studies have showed that nutritional factors including sources of carbon and nitrogen influence xylitol production [13]. Corncob is a large volume solid waste that results from the sweet corn processing industry in India. They are currently used as animal feed and returned to the harvested field for land application [14]. Corncob contains approximately over 40% of dry matter in corn residues [15] and value of raw material for production of xylose, xylitol, arabinose, xylobiose and xylooligosaccharides. The hemicelluloses fraction in corncob can be easily hydrolysed to constituent carbohydrates. These carbohydrates mainly consist of xylose and other minor pentose [16-18]. In various agricultural wastes, corncob is regarded as promising agricultural resources for microbial xylitol production because corn is widely cultivated, and corncobs are rich in hemicellulose but are not effectively utilized. Bioconversion of xylitol is influenced by factors of the various concentrations of ingredients in culture medium, so their optimization study is very important. Response surface methodology (RSM) is a mathematical and statistical analysis that is useful for modeling and analysis problems [19]. RSM has been 377 S. RAMESH et al.: RESPONSE SURFACE OPTIMIZATION OF MEDIUM COMPOSITION… utilized extensively for optimizing different biotechnological processes [20,21]. In the present study, the screening and optimization of medium composition for xylitol production by D. hansenii using Plackett-Burman and RSM were carried out. The Plackett-Burman screening design was applied for identifying the significant variables that enhance xylitol production. The central composite design (CCD) was further applied to determine the optimum level of each significant variable. MATERIALS AND METHODS Microorganisms and maintenance The yeast strain Dabaryomyces hansenii var. hansenii (MTCC 3034) was collected from the Microbial Type Culture Collection and Gene bank, Chandigarh. The lyophilized stock cultures were maintained at 4 °C in culture medium supplemented with 20 g agar. The medium composition (g/l) is given as: malt extract - 3.0; yeast extract - 3.0; peptone - 5.0; glucose - 10.0, with pH 7. It was sub-cultured every thirty days to maintain viability. Size reduction Corncob was collected from agricultural farms at perambalur, Tamilnadu, India. The collected raw material were dried in sunlight for 2 days, crushed and sieved for different mesh size ranging from 0.45 mm to 0.9 mm (20–40 mesh) and used for further studies. The composition of corncob used for xylitol production is given in Table 1. Table 1. Composition (g/l) of the corncob hemicellulose hydrolysate Component Amount Xylose 28.7 Glucose 5.4 Arabinose 3.7 CI&CEQ 19 (3) 377−384 (2013) and unhydrolysed solid residue was washed with warm water at 60 °C. The filtrate and wash liquid were pooled together. Detoxification Hemicellulose acid hydrolysate was heated at 100 °C, and maintained for 15 min to reduce the volatile components. The hydrolysate were overlimed with solid Ca(OH)2 up to pH 10, in combination with 0.1% sodium sulfite and filtered to remove the insoluble materials. The filtrate was adjusted to pH 7 with H2SO4. The water phase was treated with activated charcoal and used for xylitol production. Fermentation conditions Fermentation was carried out in 250 ml Erlenmeyer flasks with 100 ml of pretreated corncob hemicelluloses hydrolysate at pH 7. This is supplemented with different nutrient concentration for tests according to the selected factorial design and sterilized at 120 °C for 20 min. After cooling the flasks at room temperature, the flasks were inoculated with 1 ml of grown culture broth. The flasks were maintained at 30 °C under agitation at 200 rpm for 48 h. During the preliminary screening process, the experiments were carried out for 5 days and it was found that the maximum production was obtained in 48 h. Hence, experiments were carried out for 48 h. Analytical methods Sugar and sugar alcohols in the culture broth were measured by high performance liquid chromatography (HPLC), model LC-10-AD (Shimadzu, Tokyo, Japan) equipped with a refractive index (RI) detector. The chromatography column used was an Aminex HPX-87H (300 mm×7.8 mm) column at 80 °C with 5 mM H2SO4 as mobile phase at a flow rate of 0.4 ml/min, and the injected sample volume was 20 µL. Optimization of xylitol production Cellobiose 0.5 Plackett–Burman experimental design Galactose 0.7 Mannose 0.4 Plackett–Burman experimental design assumes that there are no interactions between the different variables in the range under consideration. A linear approach is considered to be sufficient for screening. Plackett–Burman experimental design is a fractional factorial design and the main effects of such a design may be simply calculated as the difference between the average of measurements made at the high level (+1) of the factor and the average of measurements at the low level (–1). To determine the variables significantly affect xylitol production, the Plackett–Burman design was used. Nine variables (Table 2) were screened in 12 Acetic acid 2 Furfural 0.8 Hydroxymethylfurfural 0.2 Acid hydrolysis The pretreatment were carried out in 500 ml glass flasks. 2 g corncob in solid loading of 10 mass% mixed with 1 mass% dilute sulfuric acid and pretreated in an autoclave at 120 °C with residence time of 1 h. The liquid fraction was separated by filtration 378 S. RAMESH et al.: RESPONSE SURFACE OPTIMIZATION OF MEDIUM COMPOSITION… experimental runs (Table 3) and insignificant ones were eliminated in order to obtain a smaller, manageable set of factors. The low level (-1) and high level (+1) of each factor are listed in Table 2. The statistical software package Minitab 15 was used to analyze the experimental data. Once the critical factors were identified through the screening, the central composite design (CCD) was used to obtain a quadratic model. model parameter estimates are desired [19]. The coded values of the process parameters are determined by the following equation: xi = 1 Nutrient -1 +1 Min. value, g/l Max. value, g/l 7 A K2HPO4 6.6 2 B Yeast extract 1.5 5 3 C Peptone 2 5 4 D KH2PO4 1.2 3.6 5 E Xylose 9.8 10.2 6 F (NH4)2SO4 1 4 7 G MgSO4⋅7H2O 0.7 1.3 8 H Malt 2.8 3.2 9 I Glucose 9.8 10.2 Xi − X0 Δx (1) where xi – coded value of the ith variable, Xi – uncoded value of the ith test variable and X0 – uncoded value of the ith test variable at center point. The regression analysis is performed to estimate the response function as a second order polynomial: Table 2. Nutrients screening using Plackett-Burman design Ser. Nutrient No. code CI&CEQ 19 (3) 377−384 (2013) Y = β0 + k i =1 βi X i + k i =1 βii X i2 + k −1 k i =1,i < j j = 2 βij X i X j (2) where Y is the predicted response, β0 constant, βi, βj and βij are coefficients estimated from regression. They represent the linear, quadratic and cross products of Xi and Xj on response. Model fitting and statistical analysis The regression and graphical analysis with statistical significance were carried out using Minitab 15. In order to visualize the relationship between the experimental variables and responses, the response surface and contour plots were generated from the models. The optimum values of the process variables were obtained from the regression equation. The adequacy of the models was further justified through analysis of variance (ANOVA). Lack-of-fit is a special diagnostic test for adequacy of a model and compares the pure error, based on the replicate measurements to the other lack of fit, based on the model performance [22]. F-value, calculated ratio between the lack-of-fit mean square and the pure error mean square are statistic parameters used to determine whether the lack-of-fit is significant or not, at a significance level. Central composite design The central composite design is used to study the effects of variables on their responses and subsequently in the optimization studies. This method is suitable for fitting a quadratic surface and it helps to optimize the effective parameters with minimum number of experiments, as well as to analyze the interaction between the parameters. In order to determine the existence of a relationship between the factors and response variables, the collected data were analyzed in a statistical manner, using regression. A regression design is normally employed to model a response as a mathematical function (either known or empirical) of a few continuous factors and good Table 3. Plackett–Burman experimental design for nine variables Run Order A B C D E F G H I Xylitol yield, g/g 1. 1 1 -1 -1 -1 1 1 1 -1 0.21 2. 1 -1 1 -1 -1 -1 1 1 1 0.30 3. -1 -1 -1 1 1 1 -1 1 1 0.40 4. -1 1 1 1 -1 1 1 -1 1 0.45 5. 1 -1 -1 -1 1 1 1 -1 1 0.22 6. -1 -1 -1 -1 -1 -1 -1 -1 -1 0.40 7. 1 -1 1 1 -1 1 -1 -1 -1 0.55 8. 1 1 1 -1 1 1 -1 1 -1 0.44 9. 1 1 -1 1 1 -1 1 -1 -1 0.55 10. -1 1 1 -1 1 -1 -1 -1 1 0.64 11. -1 -1 1 1 1 -1 1 1 -1 0.45 12. 1 1 -1 1 -1 -1 -1 1 1 0.61 379 S. RAMESH et al.: RESPONSE SURFACE OPTIMIZATION OF MEDIUM COMPOSITION… Validation of the experimental model The statistical models were validated with respect to xylitol production under the conditions predicted by the model in shake-flasks level. Samples were drawn at the desired intervals and xylitol production was determined as described above. RESULTS AND DISCUSSION Plackett-Burman experiments (Table 3) showed a wide variation in xylitol production. This variation reflected the importance of optimization to attain higher productivity. From the pareto chart (Figure 1) the variables, viz., KH2PO4, yeast extract, MgSO4⋅7H2O and (NH4)2SO4 were selected for further optimization to attain a maximum response. The level of factors KH2PO4, yeast extract, MgSO4⋅7H2O and (NH4)2SO4) and the effect of their interactions on xylitol production were determined by central composite design of RSM. Thirty experiments were preferred at different combinations of the factors shown in (Table 4) and the central point was repeated six times (1, 4, 16, 17, 22, 24). The predicted and observed responses along with design matrix are presented in Table 5. The results were analyzed using ANOVA. The second order regression equation provided the levels of xylitol production as a function of KH2PO4, yeast extract, MgSO4⋅7H2O and (NH4)2SO4, which can be presented in terms of coded factors as in the following equation: CI&CEQ 19 (3) 377−384 (2013) Y = 0.748 + 0.006 − 0.01A − 0.0107B − 0.039C − −0.0193D − 0.021A × A − 0.0244B × B − −0.0356C × C − −0.0381D × D − 0.0048 A × B − −0.00025 A × C − 0.014 A × D − 0.0125B × C + +0.0163B × D + 0.0288C × D (3) where Y is the xylitol yield (g/g), A, B, C and D are (NH4)2SO4, KH2PO4, MgSO4⋅7H2O and yeast extract, respectively. ANOVA used for the response surface is shown in Table 6. The p-value of the model was 0.04533, which was used as a tool to check the significance of each co-efficient, and indicated that the model was suitable for using in this experiment. The p-value less than 0.05 indicate model terms are significant. Values greater than 0.05 indicates model terms are not significant. In the present work, linear terms of B, C, D and all the square effects of A, B, C, D and the combination of A×D, B×C, B×D and C×D were significant for xylitol production. The co-efficient of determination (R2) for xylitol production was calculated as 0.9488, and it is very close to 1 and can explain up to 94.88% variability of the response. The predicted R2 value of 0.7815 was in reasonable agreement with the adjusted R2 value of 0.8938. Table 4. Ranges of variables used in RSM Ser. No. 1 Variable Code (NH4)2SO4 A Levels, g/l -2 -1 0 1 2 2 3 4 5 6 2 KH2PO4 B 1 2 3 4 5 3 MgSO4⋅7H2O C 0.6 0.9 1.2 1.5 1.8 4 Yeast extract D 2 3 4 5 6 Pareto Chart of the Standardized Effects (response is C14, Alpha = .05) 4.303 G D F Term B C H E A I 0 1 2 3 4 5 Standardized Effect 6 7 8 Figure 1. Pareto chart showing the effect of media components on xylitol production (G - MgSO4⋅7H2O, D - KH2PO4, F - (NH4)2SO4, B - yeast extract). 380 S. RAMESH et al.: RESPONSE SURFACE OPTIMIZATION OF MEDIUM COMPOSITION… Table 5. Central Composite Design (CCD) in coded levels with xylitol yield as response Xylitol yield, g/g Run A B C D Experimental Predicted 1 0 0 0 0 0.75 0.742 2 -1 1 1 -1 0.55 0.543 3 -1 -1 1 1 0.60 0.627 4 0 0 0 0 0.75 0.742 5 1 1 -1 -1 0.70 0.688 6 1 1 -1 1 0.61 0.596 7 1 1 1 -1 0.54 0.541 8 1 -1 -1 -1 0.73 0.726 9 -1 1 -1 1 0.64 0.653 10 -1 -1 -1 -1 0.70 0.708 11 -1 -1 1 -1 0.60 0.624 12 -1 1 -1 -1 0.69 0.701 13 -1 -1 -1 1 0.61 0.619 14 -1 1 1 1 0.62 0.634 15 1 1 1 1 0.57 0.576 16 0 0 0 0 0.74 0.754 17 0 0 0 0 0.75 0.754 18 1 -1 1 -1 0.64 0.642 19 1 -1 -1 1 0.56 0.582 20 1 -1 1 1 0.60 0.600 21 2 0 0 0 0.64 0.651 22 0 0 0 0 0.76 0.754 23 -2 0 0 0 0.73 0.691 24 0 0 0 0 0.75 0.754 25 0 2 0 0 0.63 0.635 26 0 -2 0 0 0.71 0.677 27 0 0 0 -2 0.64 0.640 28 0 0 -2 0 0.68 0.675 29 0 0 2 0 0.57 0.547 30 0 0 0 2 0.59 0.562 tion up to 3 g/l. The optimal conditions of (NH4)2SO4, KH2PO4, MgSO4⋅7H2O and yeast extract for maximum xylitol production were determined by response surface analysis and estimated by regression equation. The predicted results are shown in Table 6 and values from the regression equation closely agreed with experimental values. Table 6. Analyses of variance (ANOVA) for response surface quadratic model for the production of xylitol; R2 - 94.88%; R2 (predicted) - 78.15%; R2 (adjusted) - 89.38% Term Coefficient SE Coefficient Constant 0.748000 0.009461 T P 79.058 0.000 Block 0.006000 A -0.010000 0.004904 1.223 0.241 0.004660 -2.146 B 0.050 -0.010667 0.004731 -2.255 0.041 C -0.031833 0.004731 -6.729 0.000 D -0.019333 0.004731 -4.087 0.001 A×A -0.020625 0.004359 -4.732 0.000 B×B -0.024375 0.004359 -5.592 0.000 C×C -0.035625 0.004359 -8.173 0.000 D×D -0.038125 0.004359 -8.747 0.000 A×B -0.004750 0.005837 -0.814 0.429 A×C -0.000250 0.005837 -0.043 0.966 A×D -0.014000 0.005837 -2.399 0.031 B×C -0.012500 0.005707 -2.190 0.046 B×D 0.016250 0.005707 2.848 0.013 C×D 0.028750 0.005707 5.038 0.000 0.7 C10 The above model is used to predict the xylitol production within the limits of the experimental factors that the actual response values agree well with the predicted response values. The production of xylitol with variable interactions were studied by plotting surface curves against any two independent variables, while keeping another variable at its central (0) level. The curves of calculated response (xylitol production) and contour plots from the interactions between the variables are shown in Figures 2-11. Figures 2 and 3 show the dependency of xylitol on yeast extract and KH2PO4. The xylitol production increased with increasing in yeast extract to about 4 g/l and then xylitol production is decreased with further increase in yeast extract. Similar results were observed in Figures 4-11. Increase in KH2PO4 resulted in the increase in xylitol produc- CI&CEQ 19 (3) 377−384 (2013) 0.6 2 0.5 0.4 0 D -2 0 B 2 -2 Figure 2. Plot showing the effect of yeast extract and KH2PO4 on xylitol production; hold values: A = 0, C = 0. Validation of the experimental model Validation of the experimental model was tested by carrying out the batch experiment under optimal operation conditions: (NH4)2SO4 – 3.94 g/l, KH2PO4 – 2.74 g/l, MgSO4⋅7H2O – 1.02 g/l and yeast extract – 3.45 g/l established by the regression model. Four repeated experiments were performed and the results are compared. The xylitol production (0.76 g/g) obtained 381 S. RAMESH et al.: RESPONSE SURFACE OPTIMIZATION OF MEDIUM COMPOSITION… CI&CEQ 19 (3) 377−384 (2013) 2 0.45 0.50 0.55 0.60 0.65 0.70 D 1 0 C10 < – – – – – – > 0.45 0.50 0.55 0.60 0.65 0.70 0.75 0.75 Hold Values A 0 C 0 -1 -2 -2 -1 0 B 1 2 Figure 3. Plot showing the effect of yeast extract and KH2PO4 on xylitol production. 2 C 10 < 0.4 – 0.5 – 0.6 – > 1 C10 C 0.7 0.4 0.5 0.6 0.7 0.7 Hold Values A 0 D 0 0 0.6 0.5 -1 2 0.4 0 C -2 0 B 2 -2 -2 -2 Figure 4. Plot showing the effect of MgSO4⋅7H2O and KH2PO4 on xylitol production; hold values: A = 0, D = 0. -1 0 B 1 2 Figure 5. Plot showing the effect of MgSO4.7H2O and KH2PO4 on xylitol production. 2 C 10 < 0.4 – 0.5 – 0.6 – > 1 C10 D 0.7 Hold Values B 0 C 0 0 0.6 0.5 2 0.4 0 0 A 2 -1 D -2 -2 Figure 6. Plot showing the effect of yeast extract and (NH4)2SO4 on xylitol production; B = 0, C = 0. from experiments was very close to the actual response (0.754 g/g) predicted by the regression model, which proved the validity of the model. 382 0.4 0.5 0.6 0.7 0.7 -2 -2 -1 0 A 1 2 Figure 7. Plot showing the effect of yeast extract and (NH4)2SO4 on xylitol production. CONCLUSION In this work, Plackett-Burman design was used to determine the relative importance of medium com- S. RAMESH et al.: RESPONSE SURFACE OPTIMIZATION OF MEDIUM COMPOSITION… CI&CEQ 19 (3) 377−384 (2013) 2 0.45 0.50 0.55 0.60 0.65 0.70 1 C1 0 C 0.7 0 -1 2 0.4 0 C -2 0 A 2 0.45 0.50 0.55 0.60 0.65 0.70 0.75 0.75 Hold Values B 0 D 0 0.6 0.5 C 10 < – – – – – – > -2 -2 Figure 8. Plot showing the effect of MgSO4⋅7H2O and (NH4)2SO4 on xylitol production; hold values: B = 0, D = 0. -2 -1 0 A 1 2 Figure 9. Plot showing the effect of MgSO4⋅7H2O and (NH4)2SO4 on xylitol production. 2 C 10 < 0.52 – 0.56 – 0.60 – 0.64 – 0.68 – > B 1 0.7 0.52 0.56 0.60 0.64 0.68 0.72 0.72 Hold Values C 0 D 0 0 C1 0 0.6 2 0.5 0 B -2 0 A 2 -1 -2 -2 -2 -1 0 A 1 2 Figure 10. Plot showing the effect of KH2PO4 and (NH4)2SO4 on Figure 11. Plot showing the effect of KH2PO4 and (NH4)2SO4 on xylitol xylitol production; C = 0, D = 0. production. ponents for xylitol production. Among the variables, (NH4)2SO4, KH2PO4, MgSO4⋅7H2O and yeast extract were found the most significant variables. From further optimization studies the optimized values of the variables for xylitol production were as follows: (NH4)2SO4 – 3.94 g/l, KH2PO4 – 2.74 g/l, MgSO4⋅7H2O – 1.02 g/l and yeast extract – 3.45 g/l. This study showed that corncob is a good source for the production of xylitol. Using the optimized conditions, the production reaches 0.76 g/g. The results show a close agreement between the expected and obtained production level. REFERENCES [1] T. Pepper, P.M. Olinger, Food Technol. 42 (1988) 98–106 [2] S. Ahmet, G. Gurbuz, LWT - Food. Sci. Technol. 39 (2006) 1053–1058 [3] Y. Takahashi, C. Takeda, I. Seto, G. Kawano, Y. Machida, Int. J. Pharmacol. 343 (2007) 220–227 [4] J.P. Mikkola, T. Salmi, Catal. Today 64 (2001) 271–277 [5] L. Hyvönen, P. Koivistoinen, F. Voirol, Adv. Food Res. 28 (1982) 373-403 [6] A.J. Melaji, L. Hamalainen, US patent no. 4.008, 1977, 285 [7] E. Winkelhausen, S. Kusmanova, J. Ferment. Bioeng. 86(1) (1998) 1–14 [8] T. Walther, P. Hensirisak, F.A. Agblevor, Bioresour. Technol. 76 (2001) 213-220 [9] A. Converti, J.M. Dominguez, Biotechnol. Bioeng. 75 (2001) 39–45 [10] A. Converti, P. Perego, A. Sordi, P. Torre, Biochem. Biotechnol. 101 (2002) 15–29 Acknowledgment The authors wish to express their gratitude for the support extended by the authorities of Annamalai University, Annamalainagar, India, in carrying out the research work in Bioprocess laboratory, Department of Chemical Engineering. 383 S. RAMESH et al.: RESPONSE SURFACE OPTIMIZATION OF MEDIUM COMPOSITION… CI&CEQ 19 (3) 377−384 (2013) [11] J.M Domınguez, C.S. Gong, G. Tsao, Appl. Biochem. Biotechnol. 63–65 (1997) 117–127 [17] V. Balan, B. Bals, S.P. Chundawat, D. Marshall, B.E. Dale, Mol. Biol. 581 (2009) 61–77 [12] F.M. Gırio, J.C. Roseiro, P. Sa-Machado, , A.R. DuarteReis, M.T. Amaral-Collaco, Enzyme Microb. Technol. 16 (1994) 1074–1078 [18] W.C. Liaw, C.S. Chen, W.S. Chang, K.P. Chen, J. Biosci. Bioeng. 105 (2008) 97–105 [19] [13] L. Hongzhi, Chengkeke, Gejingping, Ping Wenxiang, New Biotechnol. 28(6) (2011) 673-678 D.C. Montgomery, Design and Analysis of Experiments, John Wiley and Sons, New York, 2001 [20] W. Li, W. Du, D.H.J. Liu, Mol. Catal., B 45 (2007) 122–127 [14] G.E. Inglett, CT Westport, AVI Publishing Co., 1970 [21] [15] B. Barl, C.G. Biliaderis, E.D Murray, A.W. MacGregor, J. Sci. Food Agric. 56 (1991) 195–214 B.J. Naveena, M. Atlaf, K. Bhadnah. G. Reddy, Process. Biochem. 40 (2005) 681–690 [22] [16] O. Lisbeth, H.H. Barbe, Enzyme Microb. Technol. 18 (1996) 312–331 M.Y Noordin, V.C. Venkatesh, S. Sharif, S. Elting, A. Abdullah, J. Mater. Process. Technol. 145(1) (2004) 46–58. S. RAMESH R. MUTHUVELAYUDHAM R. RAJESH KANNAN T. VIRUTHAGIRI Department of Chemical Engineering, Annamalai University, Annamalainagar, Tamilnadu, India NAUČNI RAD OPTIMIZACIJA SASTAVA HRANLJIVE PODLOGE SA HIDROLIZATOM HEMICELULOZE KUKURUZNOG KLIPA ZA PRODUKCIJU KSILITOLA POMOĆU Debaryomyces hansenii var. Hansenii PRIMENOM METODE POVRŠINE ODZIVA Izvršeno je optimizovanje hranljive podloge za produkciju ksilitola pomoću Debaryomyces hansenii var. hansenii. Ova optimizacija produkcije ksilitola na podlozi sa hidrolizatom hemiceluloze kukuruznog klipa je izvršena primenom statističke metode zasnovane na planiranju eksperimenata. Uticaj devet nutrienata na produkciju ksilitola je ocenjen Plackett-Burman-ovim dizajnom. Pozitivan uticaj na produkciju ksilotola imali su MgSO4⋅7H2O, KH2PO4, (NH4)2SO4 i ekstrakt kvasca. Ove komponente su optimizovane metodom površine odziva. Optimalni uslovi su MgSO4⋅7H2O – 1,02 g/l, (NH4)2SO4 – 3,94 g/l, KH2PO4 – 2,74 g/l i ekstrakt kvasca – 3,45 g/l. Ovi uslovi su potvrđeni eksperimentalno, a prinos ksilitola je bio 0,76 g/g. Ključne reči: ksilitol, kukuruzni klip, Debaryomyces hansenii var. hanseni, optimizacija, metoda površine odziva. 384 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 385−388 (2013) SAŠA Ž. DRMANIĆ1 JASMINA B. NIKOLIĆ1 ALEKSANDAR D. MARINKOVIĆ1 GAVRILO M. ŠEKULARAC1 BRATISLAV Ž. JOVANOVIĆ2 1 Department of Organic Chemistry, Faculty of Technology and Metallurgy, University of Belgrade, Belgrade, Serbia 2 Institute of Chemistry, Technology and Metallurgy, University of Belgrade, Belgrade, Serbia SCIENTIFIC PAPER UDC 547.821:543.4 DOI 10.2298/CICEQ120326073D CI&CEQ THE EFFECTS OF SOLVENTS AND STRUCTURE ON THE ELECTRONIC ABSORPTION SPECTRA OF THE ISOMERIC PYRIDINE CARBOXYLIC ACID N-OXIDES The ultraviolet absorption spectra of the carboxyl group of three isomeric pyridine carboxylic acids N-oxides (picolinic acid N-oxide, nicotinic acid N-oxide and isonicotinic acid N-oxide) were determined in fourteen solvents in the wavelength range from 200 to 400 nm. The position of the absorption maxima (λmax) of the examined acids showed that the ultraviolet absorption maximum wavelengths of picolinic acid N-oxide are the shortest, and those of isonicotinic acid N-oxide acid are the longest. In order to analyze the solvent effect on the obtained absorption spectra, the ultraviolet absorption frequencies of the electronic transitions in the carboxylic group of the examined acids were correlated using a total solvatochromic equation of the form νmax = v0 + + sπ* + aα+ bβ, where νmax is the absorption frequency (1/λmax), π* is a measure of the solvent polarity, β represents the scale of solvent hydrogen bond acceptor basicities and α represents the scale of solvent hydrogen bond donor acidities. The correlation of the spectroscopic data was carried out by means of multiple linear regression analysis. The solvent effects on the ultraviolet absorption maximums of the examined acids were discussed. Keywords: picolinic acid N-oxide, nicotinic acid N-oxide, isonicotinic acid N-oxide, ultraviolet absorption maximum, protic and aprotic solvents, solvatochromic effects. Pyridine N-oxides, the group of compounds that pyridine carboxylic acids belong to, have applications in a wide range of fields including industry, medicine, biochemistry and even nano-tecnology [1-7]; therefore, there is interest in studying the structural and spectrochemical information about them. The connection that exists between the compound structure, solvent effect and the ultraviolet absorption spectra has been a subject of many studies [8-13]. The absorption of UV light can raise the electrons in the molecule to a higher energy level. The possible electronic transition under UV light are n → π* (lone electron from the pair in a nonbonding orbital to higher level antibonding orbital), π → π* (electron from a π bond to higher level antibonding orbital) and σ → σ* (electron from a σ bond into a higher level antibonding orbital) [14,15]. The part of molecule with an ability to absorb the UV light is called the chromophore. This part of the molecule has a characteristic value of the wavelength of the absorbed UV radiation, called the absorption maximum (λmax). The π → π* transition in the carboxylic group of the three isomeric pyridine carboxylic acids (Figure 1), dissolved in a set of solvents, was analyzed in this study. COOH COOH N Correspondence: S.Ž. Drmanić, Department of Organic Chemistry, Faculty of Technology and Metallurgy, University of Belgrade, Karnegijeva 4, Belgrade, Serbia. E-mail: drmana@tmf.bg.ac.rs Paper received: 26 March, 2012 Paper revised: 15 June, 2012 Paper accepted: 14 July, 2012 COOH N O O (1) (2) N O (3) Figure 1. Picolinic acid N-oxide (1), Nicotinic acid N-oxide (2), Isonicotinic acid N-oxide (3). 385 S.Ž. DRMANIĆ et al.: THE EFFECTS OF SOLVENTS AND STRUCTURE… During the excitation process, π → π* of the one electron from the π bond in the carbonyl (C=O) group of the carboxylic group is promoted from to an antibonding orbital which contains higher energy. The molecular structure or the present solvent can influence the wavelength of the absorption maximum: if λmax increases it is a batochromic shift, while if it decreases it is a hypsochromic shift. Also, batochromic shift signifies the lower energy of the electronic π → π* transition, while the hypsochromic shift means higher energy. The effects of solvent polarity and hydrogen bonding on the absorption spectra of the examined compounds are interpreted by means of the linear solvation energy relationships (LSER) concept, developed by Kamlet and Taft [16], using a general solvatochromic equation of the form: νmax = v0 + sπ* + aα+ bβ (1) where α, β and π* are solvatochromic parameters; s, a and b are solvatochromic coefficients; νmax = 1/λmax is the maximum absorption frequency; and v0 is the reference value, which is taken to be in the solvent cyclohexane, for which all the solvent parameters have the value zero [16]. In Eq. (1), π* is the index of the solvent dipolarity/polarizability, which is a measure of the ability of a solvent to stabilize a charge or a dipole by its own dielectric effects. The π* scale was selected to range from 0.00 for cyclohexanone to 1.00 for dimethyl sulfoxide. The α coefficient represents the solvent hydrogen bond donor (HBD) acidity, in other words it describes the ability of a solvent to donate a proton in a solvent-to-solute hydrogen bond. The α scale CI&CEQ 19 (3) 385−388 (2013) extends from 0.00 for non-HBD solvents to about 1.00 for methanol. The β coefficient is a measure of the solvent hydrogen bond acceptor (HBA) basicity, and describes the ability of a solvent to accept a proton in a solute-to-solvent hydrogen bond. Theβ scale was selected to extend from 0.00 for non-HBA solvents to about 1.00 for hexamethylphosphoricacid triamide. EXPERIMENTAL Picolinic acid N-oxide, nicotinic acid N-oxide and isonicotinic acid N-oxide were commercial product (Fluka) of p.a. quality. Spectroscopic measurements The UV spectra of the examined compounds were recorded using a Shimadzu 1700A spectrophotometer. The wavelength range was 200-400 nm. The concentrations of the examined solutions were 10-4 mol/dm3. The solvents used were of high purity, designed for spectroscopic measurements. RESULTS AND DISCUSSION The absorption maxima of the examined pyridine carboxylic acids N-oxides in a set of fourteen solvents are given in Table 1. It can be noticed that the values of wavelengths of the absorption maxima increase with the number of C-atom between the carboxylic group and the N-oxy group in the ring. This batochromic shift is a consequence of the compounds structure. The negative inductive effect of the N-oxy group in the molecule of the picolinic acid N-oxide is strong on the substituent next to it, which is the carboxylic group. This effect Table 1. The absorption maxima for the examined pyridine carboxylic acids N-oxides in various solvent Solvent Picolinic acid N-oxide λmax / nm νmax / 103 cm-1 Nicotinic acid N-oxide λmax / nm νmax / 103 cm-1 Isonicotinic acid N-oxide λmax / nm νmax / 103 cm-1 Methanol 260.41 38.4 267.37 37.4 286.53 34.9 Ethanol 261.78 38.2 268.81 37.2 288.18 34.7 Propan-1-ol 263.85 37.9 271.00 36.9 289.85 34.5 Propan-2-ol 264.55 37.8 271.73 36.8 291.54 34.3 2-Methylpropan-2-ol 266.66 37.5 273.97 36.5 290.69 34.4 Ethylene glycol 250.62 39.9 257.07 38.9 282.48 35.4 Butan-1-ol 262.46 38.1 269.54 37.1 291.54 34.3 Pentan-1-ol 263.15 38.0 270.27 37.0 289.85 34.5 2-Methylnutan-2-ol 263.85 37.9 269.54 37.1 289.85 34.5 Butan-2-ol 263.85 37.9 271.74 36.9 290.69 34.4 N-Methylformamide 258.39 38.7 264.55 37.8 266.66 37.5 Dioxane 247.52 40.4 250.62 39.9 251.30 39.8 Methyl acetate 250.62 39.9 258.39 38.7 263.85 37.9 Chloroform 250.62 39.9 257.06 38.9 258.39 38.7 386 S.Ž. DRMANIĆ et al.: THE EFFECTS OF SOLVENTS AND STRUCTURE… can change the electronic density and the electronic disposition in the carboxylic group and therefore cause the need for higher energy of the π → π* transition. Furthermore, the intramolecular hydrogen bond can be formed between the carboxylic hydrogen and the oxygen from the N-oxy group (Figure 2) in the molecule of picolinic acid N-oxide, which additionally increases the negative inductive effect of the N-oxy group. This hydrogen bond has been proved and analyzed by X-ray, FTIR and NMR spectra [17]. The final electron acceptor in the system, oxygen, attracts the electrons from the σ bond strongly in order to keep the hydrogen bond. O N C O O H Figure 2. The inductive effect of the N-oxy group and the hydrogen bond in the molecule of picolinic acid N-oxide. In the case of nicotinic acid N-oxide there is only the negative inductive effect of the N-oxy group that can influence the carbonyl group, somewhat weaker than for picolinic acid N-oxide and there is hardly any possibility for the formation of the intramolecular hydrogen bond. This compound therefore has longer λmax and the lower energy of the examined π → π* transition. Even weaker negative inductive effect and no possibility for an intramolecular hydrogen bond exists in the case of the isonicotinic acid N-oxide. There the maximum wavelengths are the longest and the π → π* transition energy the lowest, as it is free from the described effects. In order to discuss the effect of solvents on the absorption spectra of the examined isomeric pyridine carboxylic acids N-oxide, the absorption frequencies (νmax) were correlated with the Kamlet-Taft solvatochromic parameters, Table 2 [18]. The obtained correlation equations were as follows: Picolinic acid N-oxide: νmax = 39.61 + (1.98±0.62)π* – (2.26±0.48)β – - (0.86±0.35)α, (R = 0.957, s = 0.32, n = 14) (2) Nicotinic acid N-oxide: νmax = 38.66 + (2.06±0.80)π* – (2.28±0.60)β – - (1.09±0.46)α, (R = 0.937, s = 0.41, n = 14) Isonicotinic acid N-oxide: CI&CEQ 19 (3) 385−388 (2013) νmax = 37.64 + (3.47±1.46)π* – (2.56±1.13)β – - (3.48±0.84)α, (R = 0.938, s = 0.75 n = 14) (4) Table 2. Solvent parameters Solvent π* β α Methanol 0.60 0.62 0.93 Ethanol 0.54 0.77 0.83 Propan-1-ol 0.52 0.83 0.78 Propan-2-ol 0.48 0.95 0.76 2-Methylpropan-2-ol 0.41 1.01 0.68 Ethylene glycol 0.92 0.52 0.90 Butan-1-ol 0.47 0.88 0.79 Pentan-1-ol 0.40 0.86 0.84 2-Methylbutan-2-ol 0.40 0.93 0.28 Butan-2-ol 0.40 0.80 0.69 N-Methylformamide 0.90 0.80 0.62 Dioxane 0.55 0.37 0.00 Methyl acetate 0.60 0.42 0.00 Chloroform 0.58 0.10 0.20 From the given equation it can be seen that the here applied solvent set has a similar effect on all three examined isomeric acids. For all the examined compounds the solvent polarity/polarizability effect causes the hypsochromic shift, while the HBA and HBD solvent effects cause the batochromic shift. In other words, the energy of the π* electronic transition in the carboxylic group of the examined pyridine carboxylic acids N-oxides is raised by the solvent polarity, but lowered by its proton-donor and protonacceptor effects. When a dipolar molecule is dissolved in a polar solvent, as it is a case in this study, the hypsochromic shift appears when the molecule is a higher dipole in the ground state, than in the excited state. With the increase of solvent polarity the more dipolar structure is better stabilized, so it can be concluded that the molecules of the examined acids are higher dipoles in the ground state and that the π* transition in the carbonyl group decreases their polarity. From the highest values of the coefficients for all three parameters (π*, β and α) in the case of the isonicotinic acid N-oxide it can be seen that the solvent effect on the π* transition of the C=O group of this compound is the strongest, i.e., that it is the most sensitive to solvent properties. CONCLUSION (3) From the analysis of the absorption spectra of the π* transitions of the carbonyl group in the carboxyl group of picolinic acid N-oxide, nicotinic acid N-oxide and isonicotinic acid N-oxide in the chosen solvent set it can be concluded that the both the structure and 387 S.Ž. DRMANIĆ et al.: THE EFFECTS OF SOLVENTS AND STRUCTURE… the solvent effect can influence the position of the absorption maxima. The examined transition demands the highest energy in the case of picolinic acid N-oxide, where it is hardened by the negative inductive effect of the N-oxy group, and the intramolecular hydrogen bond, and the lowest energy in the case of isonicotinic acid N-oxide, where there is no possibility for such a hydrogen bond, and the negative inductive effect is the lowest. The analysis of solvent effects, expressed quantitatively by the Kamlet-Taft total solvatochromic equation, showed that for all three examined compounds the π* transition energy increases with the solvent polarity, meaning that they are lower dipoles in the excited than in the ground state. Acknowledgements Authors are grateful to the Ministry Education, Science and Technological Development of The Republic of Serbia for financial support (Project 172013). REFERENCES CI&CEQ 19 (3) 385−388 (2013) [4] A. Ataç, F. Bardak, Turk. J. Chem. 30 (2006) 609 [5] M. Karabacak, M. Cinar, M. Kurt, J. Mol. Struct. 885 (2008) 28 [6] M. Karabacak, M. Kurt, Spectrochim. Acta, A 71 (2008) 876–883 [7] A. Albini, S. Pietra, Heterocyclic N-oxide, CRC Press, Boca Raton, FL, 1991 [8] A.T. Nielsen, J. Org. Chem. 22 (1957) 1539 [9] C.N.R. Rave, Ultraviolet and Visible Spectroscopy: Chend mical Applications, 2 ed., Butterworks, London, 1967 [10] J.N. Gardner, A.R. Katritzky, J. Chem. Soc. (1975) 4375 [11] J.B. Nikolić, G.S. Ušćumlić, V. Krstić, J. Serb. Chem. Soc. 65 (2000) 353 [12] G.S. Ušćumlić, A.A. Kshad, D.Ž. Mijin, J. Serb. Chem. Soc. 68 (2003) 699 [13] D.Ž. Mijin, G.S. Ušćumlić, N.U. Perišić-Janjić, N.V. Valentić, Chem. Phys. Lett. 418 (2006) 223 [14] F.I. Schadt, C.J. Lancelot, J. Am. Chem. Soc. 100 (1978) 228 [15] C. Reichardt, Solvent and Solvent Effects in Organic Chemistry, VCH, Weinheim, 1990, p. 285 [16] M. Kamlet, J. Abboud, R.W. Taft., Prog. Phys. Org. Chem. 13 (1983) 485 [1] A. Atac, M. Karabacak, C. Karaca, E. Kose, Spectrochim. Acta, A 85 (2012) 145 [17] J. Stare, J. Mavri, G. Ambrožič, D. Hadži, J. Mol. Struct. (Theochem) 500 (2000) 429 [2] F. Bardak, A. Ataç, M. Kurt, Spectrochim. Acta 71 (2009) 1896 [18] A.F. Lagalante, R.J. Jacobson, T.J. Bruno, J. Org. Chem. 61 (1996) 6404. [3] N. Can, A. Ataç, F. Bardak, Ş.E.S. Can, Turk. J. Chem. 29 (2005) 589 SAŠA Ž. DRMANIĆ1 JASMINA B. NIKOLIĆ1 ALEKSANDAR D. MARINKOVIĆ1 GAVRILO M. ŠEKULARAC1 BRATISLAV Ž. JOVANOVIĆ2 1 UTICAJ RASTVARAČA I STRUKTURE NA ELEKTRONSKE ABSORPCIONE SPEKTRE IZOMERNIH PIRIDIN-KARBOKSILNIH KISELINA NOKSIDA Katedra za organsku hemiju, Tehnološko-metalurški fakultet, Univerzitet u Beogradu, Beograd, Srbija 2 Institut za hemiju, tehnologiju i metalurgiju, Univerzitet u Beogradu, Beograd, Srbija UV apsorpcioni spektri pikolinske kiseline N-oksida, nikotinske kiseline N-oksida i izonikotinske kiseline N-oksida određeni su u 14 protičnih i aprotičnih rastvarača u opsegu od 200-400 nm. Položaji maksimuma apsorpcije bili su najniži za pikolinsku kiseline N-oksid, a najviši za izonikotinsku kiseline N-oksid. Da bi se analzirao uticaj ratvarača, apsorpcione frekvence su korelisane Kamlet-Taftovom jednačinom, kojom se uticaj polarnosti/polarizabilnosti, proton-donorskog i proton-akceptorskog dejstva rastvarača može kvantiativno izraziti. NAUČNI RAD Ključne reči: pikolinska kiselina N-oksid, nikotinska kiselina N-oksid, izonikotinska kiselina N-oksid, apsorpcioni spektri, protični i aprotični ratvarači, solvatohromni efekti. 388 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 389−398 (2013) HADI BASERI ALI HAGHIGHI-ASL MOHAMMAD NADER LOTFOLLAHI School of Chemical, Gas and Petroleum Engineering, Semnan University, Semnan, Iran SCIENTIFIC PAPER UDC 66.06/.071:546.264-31 DOI 10.2298/CICEQ120203074B CI&CEQ THERMODYNAMIC MODELING OF SOLID SOLUBILITY IN SUPERCRITICAL CARBON DIOXIDE: COMPARISON BETWEEN MIXING RULES In this paper, the Peng-Robinson equation of state is used for thermodynamic modeling of the solubility of various solid components in supercritical carbon dioxide. Moreover, the effects of three mixing rules (van der Waals, Panagiotopoulos and Reid, and modified Kwak and Mansoori mixing rule) on the accuracy of calculation results were studied. Good correlations between calculated and experimental data were obtained in a wide temperature and pressure range. A comparison between the used models showed that modified Kwak and Mansoori mixing rules gave better correlations in comparison with the other mixing rules. Keywords: solid solubility; supercritical carbon dioxide; equation of state; mixing rules. In recent years, there has been increasing interest in the use of clean technologies that reduce pollution or waste, as well as energy or material use compared traditional technologies. Supercritical fluid technology is one of the most important clean technologies that can be used in many important industries, such as in chemical and biochemical reactions, extraction and purification processes, particle production or more recently in material and polymer processing [1-4]. To develop or improve these processes for producing better products, it is necessary to know the phase behavior of the solute component in supercritical or pressurized fluid. Experimental methods were used to determine the solubility of solids in supercritical fluids (SCF). Since these methods are very costly and time consuming, models are often used to provide correlations. Several models have been developed in order to correlate and predict solubility data at various pressures and temperatures. Some of these models are empirical, while others have fundamental basis [5]. Correspondence: A. Haghighi-Asl, School of Chemical, Gas and Petroleum Engineering, Semnan University, P.O. Box: 3519645399, Semnan, Iran. E-mail: ahaghighi@semnan.ac.ir; alihaghighiasl@yahoo.com Paper received: 3 February, 2012 Paper revised: 16 July, 2012 Paper accepted: 16 July, 2012 Generally, for prediction of solid solubilities in supercritical fluids, an equation of state (EOS) approach, a density-based approach or a solubility parameter approach is used. Density-based models and solubility parameter based models are used because of their relative ease of application in comparison to models based on equations of state. But equations of state based models have been used because of their proper abilities to predict the phase properties [6]. Equation of state based models are applied in many industries including oil and gas industries, separation and purification industries and some supercritical assisted industries. Van der Waals [7] developed the first two-parameter cubic equation of state. In this equation, the effect of intermolecular forces and size of molecules are considered in two terms of repulsive and attractive terms. Redlich and Kwong [8], Soave [9] and Peng and Robinson [10] modified the repulsive and attractive terms of van der Waals EOS and proposed new equations of state in which parameters were defined as functions of reduced temperature and acentric factor. These models were proposed for pure substances; however, for mixtures, mixing rules must be used. Cubic equations of state are valuable engineering tools for process design of any complex system. These equations are remarkably successful in mode- 389 H. BASERI et al.: THERMODYNAMIC MODELING OF SOLID SOLUBILITY… ling of phase equilibrium with supercritical components. The Peng-Robinson equation of state (PREOS) is a well-known cubic EOS that gives a good qualitative picture of all types of SCF phase behavior and reasonably it gives good quantitative fits for a wide variety of systems [11,12]. For example, many researchers used the PR-EOS for modeling of vapor liquid equilibrium or solid vapor equilibrium which contains supercritical carbon dioxide [13,14]. Moreover, PR-EOS has also been attempted to model the solubility of polar solutes in supercritical CO2 in the presence of a polar co-solvent with some degree of success [15,16]. Mixing rules are used for modeling of phase equilibrium in the mixtures. Conventional mixing rules such as van der Waals mixing rules or Panagiotopoulos and Reid mixing rules were used in many literatures for modeling of phase equilibrium of various systems in solid, liquid or gas phase [17]. Kwak and Mansoori [18] proposed new mixing rules based on statistical mechanical arguments. They presented new mixing rules by making relevance between the parameters of EOS and the parameters (energy and volume) of potential function in which the constants used for the mixing rules are temperature independent. Valderrama and Alvarez [19] have considered the application of the original Kwak and Mansoori mixing rules and a simplification of the combining rules for bij and dij. They presented new simplified mixing rules based on original Kwak and Mansoori mixing rules and they modeled the solubility of some solid components in supercritical carbon dioxide. In the present report, we study temperature independent mixing rules for PR-EOS, i.e. the van der Waals one fluid mixing rules, Panagiotopoulos and Reid mixing rules, and MKM mixing rules to predict the solubility of various solutes in supercritical carbon dioxide. The solutes studied here have a very different molecular structure and have been used in many important industries, e.g., textile, polymer, food and cosmetic industries. Thermodynamic model When equilibrium between a fluid mixture (solute i + solvent j) and a solid (i) is reached, the general condition of equilibrium is as follows (it is assumed that the solid phase is pure and does not contain solvent): fi S = fi F (1) F f i is the fugacity of solute i in the fluid mixtur, where f i S is the fugacity of pure solute i at the same 390 CI&CEQ 19 (3) 389−398 (2013) temperature and pressure in the solid phase. Since the solid phase is pure, the fugacity of solute i is given by [20]: v isat dP P sat RT f i S = Pi sat (T ) φisat exp P (2) i The solubility of solute i can be expressed as [20]: Vi S d P P sat R T i Pi sat (T ) φi sat (T ) exp yi = P φi F P (3) By supposing that the molar volume of the solid is independent of pressure and the fugacity coefficient of pure solid is unity, a simplified equation can be obtained: V i S P − Pi sat (T ) Pi sat (T ) yi = F exp RT φi P F (4) In Eq. (4), φi is the fugacity coefficient of solute component i in the fluid phase, in this paper, φi F was calculated by using of PR EOS (5) plus three different mixing rules: van der Waals one fluid mixing rules, Panagiotopoulos and Reid mixing rules and MKM mixing rules. The PR-EOS combined with VDW mixing rules gives Eq. (6) for fugacity coefficient [20]: P = RT a − V − b V (V + b ) + b (V − b ) b (i ) bP ln φiF = (Z − 1) − ln(Z − b RT ) − bP 2 y j aij Z + (1+ 2) b ( i ) RT j ln − − a b bP bP 2 2 Z − (1− 2) RT RT aP (RT ) 2 a ij = a i a j (1 − k ij ) and a = i j y i y j a ij b = yi y j i j bi + b j 2 (5) (6) (7) (8) In these equations ai and bi are the attraction and repulsion parameters for the pure substances, but aij and bij are the unlike interaction parameters. For PR EOS these parameters can be calculated by the following equations: H. BASERI et al.: THERMODYNAMIC MODELING OF SOLID SOLUBILITY… R 2TC i 2 1− T ai = 0.45724 k 1 + TCi Pc i k = 0.37464 + 1.5422 ω − 0.26922 ω 0.5 2 (9) CI&CEQ 19 (3) 389−398 (2013) bi + b j 2 bm = y i y j i j and 2 (10) i RT bi = 0.07780 c i PC i di +d j 2 dm = yi y j (11) A= j cP (RT )2 and B = (15) bm P RT The Panagiotopoulos and Reid mixing rules are as follow [21]: and a = y i y j (1 − K ijPan ) ai a j c = am + d mRT − 2 amd mRT with Ai = y j (1 − k ij ) ai a j and Bi = y j i j K ijPan = k ij − (k ji − k ij )y i (12) Detailed method for calculation of the fugacity coefficient by PR-EOS and Panagiotopoulos and Reid mixing rules was presented in our last work [22]. The fugacity coefficient for a component (i) in a mixture can be obtained by equation (13): RT ∂ (nb ) lnφi F = ( Z − 1)) − b ∂ni T ,n j a ( ( ) ) − (13) where n is the total number (moles) of molecules, ni is the number of molecule (i) in the mixture and V is the total volume of mixture. For calculation of the fugacity coefficient by this equation, energy parameter for the mixture (a) and the volume parameter for the mixture (b) must be calculated by Eqs. (8) and (12). Valderrama and Alvarez [19] modified the Kwak and Mansoori mixing rules and a new equation for fugacity coefficient was derived: (2Bi − bm )(Z − 1) lnφi F = − ln(Z − B ) − bm ×( A 2 2B × 2 Ai + 2RTDi − 2 RT (am Di + d m Ai ) / amd m c 2Bi − bm bm Z + B (1 + 2) )ln Z + B (1 − 2) am = y i y j (1 − k ij ) ai a j i and j j bi + b j 2 and Di = y j di +d j (17) 2 j In these d j = d j (1 − δ j ) . equations, b j = b j (1 − β j ) and RESULTS AND DISCUSSION RT 1 1 ∂(n 2a ) b + ( 2 2 a n ∂ni T ,n j V + 1 − 2 b 1 1 ∂(nb ) − × RT ln V + 1 + 2 b b n ∂ni T ,n j (V − b ) Z RT ln V j (16) − (14) The solubility of various solid components, with different molecular weights, like climbazole, cinnamic acid and spiroindolinonaphthoxazine photochromic dye have been successfully predicted by using a thermodynamic model which consisted of the PR-EOS with various mixing rules. The experimental data of the solubility of solid components in supercritical CO2 used in this paper have been given from various literatures. The critical constants, acentric factors, molar volume of solids and constants for Antoine equation of these components are listed in Table 1 (for Irgacure 2959 photoinitiator and spiroindolinonaphthoxazine photochromic dye, the estimated vapor pressure at required temperatures were reported). Table 2 shows a comparison of the results of PR-EOS with three various mixing rules: van der Waals one fluid, Panagiotopoulos and Reid, and MKM mixing rules. Comparison between the used models is based on Average Absolute Relative Deviation (AARD) between calculations and experimental solubility data (Eq. (18)). AARD = 1 N N i =1 exp calc y solid − y solid exp y solid (18) In this paper, solubility of nine different solid components in supercritical CO2 was predicted by 391 H. BASERI et al.: THERMODYNAMIC MODELING OF SOLID SOLUBILITY… CI&CEQ 19 (3) 389−398 (2013) Table 1. Properties of the solids which were studied in this paper a Substance TC / K PC / MPa ω Vm / cm3 mol–1 Climbazole 872.0 2.37 0.819 Triclocarbon 935.8 3.49 1,5 Naphtaline diamine 886.3 4.339 4-Methoxyphenylacetic acid 827.30 3.485 Naphtalin 748.2 Cinnamic acid Phenoxyacetic acide Irgacure 2959 photoinitiator Sublimation vapor B 223.8 10.382 5479.6 [23] 0.760 206.3 10.533 5588.4 [23] 0.714 113 11.854 4453.7 [24] 0.808 127.9 55.95 21101.81 [25] 4.05 0.302 110.3 13.583 3733.9 [19] 803.94 3.858 0.688 118.8 40.92 14527.28 [25] 802.61 3.991 0.760 113.0 43.78 14557.64 [25] 840.6 2.89 0.60 151.1 At 318.2 K: At 328.2 K: [26] 4.63×10 Pa 0.134 Pa 0.361 Pa At 308 K: at 318 K At 308 .2 K: -2 Spiroindolinonaphthoxazine photochromic dye Reference A 1446.2 1.436 1.169 344.9 0.72×10 -13 pa 3.81×10 -13 At 328 K: Pa 18.3×10 -13 [27] Pa a A and B are the constants in the sublimation pressure expression: log P (105 Pa) = A − B/T (K) Table 2. Average absolute relative deviations between the experimental data and calculation results of CO2-solid systems by using the PR EOS with three temperature independent mixing rules No. 1 System: CO2 + T/K P / MPa Range of y2×10 Climbazole 313-333 10-40 6-48 -4 Parameters a Kij = 0.1483 Kij = 0.1466 Kji = -0.1816 K = -0.155 β = -0.0398 δ = 0.4868 17.47 Kij = 0.1933 Kij = 0.1466 Kji = -0.1816 K = -0.1193 β = -0.1395 δ = 0.3889 16.79 Kij = 0.2606 Kij = 0.2606 Kji = 0.1551 K = 0.7931 β = 0.1835 δ = 1.1452 55.79 Kij = 0.2079 Kij = 0.2079 Kji = 0.1331 K = 0.2015 β = -0.4538 δ = 0.7818 17.6 Kij = 0.2219 Kij = 0.2219 Kji = 3.44 K = 0.4711 β = 0.2545 δ = 0.9563 33.0 PR_VDW1 PR_Pa.& Reid MKM 2 Triclocarbon 313-333 10.9-39 0.9-8.7 b c PR_VDW1 PR_Pa.& Reid MKM 3 Spiroindolinonaphthoxazine photochromic dye 308-328 10-26 0.0022-0.05 PR_VDW1 PR_Pa.& Reid MKM 4 1,5 Naphtaline diamine 313-333 11-20 0.02-0.16 PR_VDW1 PR_Pa.& Reid MKM 5 Irgacure 2959 photoinitiator 308-328 10-26 0.05-2.8 PR_VDW1 PR_Pa.& Reid MKM 392 AARD / % Ref. Mixing rules [23] 16.5 2.34 [23] 16.5 3.20 [27] 54.0 13.6 [24] 17.3 6.00 30.0 10.0 [26] H. BASERI et al.: THERMODYNAMIC MODELING OF SOLID SOLUBILITY… CI&CEQ 19 (3) 389−398 (2013) Table 2. Continued No. 6 System: CO2 + T/K P / MPa Range of y2×10 Naphtalin 308-318 15-35 70-300 -4 Parameters PR_VDW1 Kij = 0.1012 Kij = 0.0987 Kji = -0.4032 K = 0.1440 β = -0.1130 δ = 0.6456 7.20 Kij = 0.0248 Kij = 0.0238 Kji = 2.0528 K = 0.0415 β = 0.0772 δ = 0.5908 6.28 Kij = 0.1449 Kij = 0.1439 Kji = 2.3006 K = 0.2482 β = 0.3003 δ = 0.7191 12.23 Kij = -0.1426 Kij = -0.1458 Kji = 2.5298 K = -0.2610 β = -0.3224 δ = 0.5174 14.43 PR_Pa.& Reid MKM 7 Cinnamic acid 308-328 15-24 0.3-4.3 PR_VDW1 PR_Pa.& Reid MKM 8 Phenoxyacetic acide 308-328 12-23 0.5-8 PR_VDW1 PR_Pa.& Reid MKM 9 4-Methoxyphenylacetic acid 308-328 11-24 0.4-6.3 PR_VDW1 PR_Pa.& Reid MKM a b AARD / % Ref.a Mixing rules [19] 3.60 3.40 [25] 6.20 4.21 [25] 11.86 3.74 [25] 14.0 4.79 c PR EOS with Panagiotopoulos and Reid mixing rules; PR EOS with modified Kwak and Mansoori mixing rules; reference of experimental data using of PR-EOS with three various mixing rules. Moreover, calculation results are compared with the experimental data which were reported in various literatures. Good estimating results are achieved by using of this calculating method. For example, climbasole is one of the solids which were studied in this paper. The results of calculations for this component are plotted in Figure 1. As can be seen in this figure, the best calculation results in comparison with experimental data are the results of calculations obtained using PR-EOS with MKM mixing rules. Experimental solubility of triclocarbon in supercritical CO2 at various temperatures of 313.2, 323.2, 333.2 K [23], and the results of calculations by the proposed model are shown in Figure 2. These figures show the experimental and calculation solubility data from 10 to 35 MPa. These figures show that by increasing pressure, deviation between experimental data and calculation results of the model by two mixing rules of Panagiotopoulos & Reid and van der Waals mixing rules increased. But MKM mixing rules show good results at all ranges of pressure. For Irgacure 2959 photoinitiator a comparison between experimental data and the results of calculations by the proposed models with three mixing rules of Van der Waals one fluid mixing rules, Panagioto- poulos and Reid mixing rules, and MKM mixing rules are shown in Figure 3. This figure shows that at pressures higher than 20 MPa, deviation between experimental data and calculation results by two mixing rules of Van der Waals one fluid mixing rules and Panagiotopoulos and Reid mixing rules becomes very large. The MKM mixing rule showed good calculation results in all pressure ranges. Based on the results reported in Figures 1-3 it can be concluded that the performance of MKM mixing rules in comparison with other applied models is the best. The reported values of AARD show that for the MKM mixing rules, the deviation between calculated results and experimental data is very small. PR-EOS with Kwak-Mansoori mixing rules is an equation of state with three temperature independent parameters. In this equation, the thermodynamic variables were separated from constants of PR-EOS [18]. MKM mixing rules are based on original Kwak-Mansoori mixing rules but they have been simplified by [19]. As can be shown in Figures 1-3, by using MKM mixing rules, the accuracy of calculated results increased in comparison with other mixing rules such as Panagiotopoulos and Reid mixing rules. The calculated results of other researchers (by different models) are reviewed in Table 3. The used 393 H. BASERI et al.: THERMODYNAMIC MODELING OF SOLID SOLUBILITY… CI&CEQ 19 (3) 389−398 (2013) Figure 1. Solubility of Climbasole in supercritical CO2 at various temperatures (A: 313.2, B: 323.2 and C: 333.2 K). (- - -): Calculation results by PR-EOS and van der Waals one fluid mixing rules, (⋅⋅⋅): calculation results by PR-EOS and Panagiotopoulos and Reid mixing rules, (─): calculation results by PR-EOS and MKM mixing rules and (●): experimental data [23]. thermodynamic models, number of adjustable parameters (that were used in the proposed model), number of used experimental data for estimation of adjustable parameters and the AARD between experimental and calculated values are reported in this table. Comparison between the reported AARD in Table 2 and those in Table 3 can be useful for comprehension of accuracy of different models. It can be shown from Tables 2 and 3 that for climbazole and triclocarbon, the values of AARD by MKM mixing 394 rules are about half in comparison with those for other proposed models. For Irgacure 2959 photoinitiator and spiroindolinonaphthoxazine photochromic dye, AARD of PR and SRK models in combination with temperature dependent mixing rules with six adjustable parameters are about 0.1 and 0.13. These values with MKM mixing rules are also about 0.1 and 0.13 but by use of three adjustable parameters. H. BASERI et al.: THERMODYNAMIC MODELING OF SOLID SOLUBILITY… CI&CEQ 19 (3) 389−398 (2013) Figure 2. Solubility of Triclocarbon in supercritical CO2 at various temperatures (A: 313.2, B: 323.2 and C: 333.2 K). (- - -): Calculation results by PR-EOS and van der Waals one fluid mixing rules, (⋅⋅⋅): calculation results by PR-EOS and Panagiotopoulos and Reid mixing rules, (─): calculation results by PR-EOS and MKM mixing rules and (●): experimental data [23]. For other components, the values in Tables 2 and 3 show that the PR-EOS in combination with MKM mixing rules gives better results in comparison with other models. CONCLUSIONS This paper studies the performance of different thermodynamic models for calculation of solid solubility in supercritical fluids. The results showed that the type of mixing rules and the number of adjustable parameters used in the mixing rules have major effects on the accuracy of model. Based on the comparison between experimental data and calculation results for nine studied components it can be concluded that MKM mixing rules with three adjustable parameters show better results for modeling of solid solubility in SCF in comparison with the van der Waals mixing rules and Panagiotopoulos and Reid mixing rules. 395 H. BASERI et al.: THERMODYNAMIC MODELING OF SOLID SOLUBILITY… CI&CEQ 19 (3) 389−398 (2013) Figure 3. Solubility of Irgacure 2959 photoinitiator in supercritical CO2 at various temperatures (A: 308.2, B: 318.2 and C: 328.2 K). (- - -): calculation results by PR-EOS and van der Waals one fluid mixing rules, (⋅⋅⋅): calculation results by PR-EOS and Panagiotopoulos and Reid mixing rules, (─): calculation results by PR-EOS and MKM mixing rules and (●): experimental data [26]. Table 3. Comparison between different thermodynamic models No. 1 2 3 396 Number of experimental data Mean of reported Reference AARDa / % System: CO2 + Used model Number of adjustable parameter Climbazole PR-VDW 1 3 Temperature dependent 24 7.70 QLF 3 Temperature dependent 24 6.33 PR-VDW 1 3 Temperature dependent 24 15.20 QLF 3 Temperature dependent 24 7.67 PR 6 Temperature dependent 27 5.03 Triclocarbon 1,5 Naphtaline diamine [23] [23] [24] H. BASERI et al.: THERMODYNAMIC MODELING OF SOLID SOLUBILITY… CI&CEQ 19 (3) 389−398 (2013) Table 3. Continued No. 4 Number of experimental data Mean of reported Reference AARDa / % System: CO2 + Used model Number of adjustable parameter 4-Methoxyphenylacetic acid PR-VDW 1 1 Temperature independent 22 14.04 PR-VDW 2 2 Temperature independent 22 4.80 SRK-VDW 1 1 Temperature independent 22 13.48 SRK-VDW 2 2 Temperature independent 22 5.15 [25] 5 Naphtalin PR-MKM 3 Temperature independent 22 4.70 [19] 6 Cinnamic acid PR-VDW 1 1 Temperature independent 19 6.16 [25] 7 8 9 Phenoxyacetic acide Irgacure 2959 photoinitiator PR-VDW 2 2 Temperature independent 19 5.37 SRK-VDW 1 1 Temperature independent 19 6.57 SRK-VDW 2 2 Temperature independent 19 5.48 PR-VDW 1 1 Temperature independent 22 12.14 PR-VDW 2 2 Temperature independent 22 4.41 SRK-VDW 1 1 Temperature independent 22 12.92 SRK-VDW 2 2 Temperature independent 22 4.73 PR-VDW 1 3 Temperature dependent 3 31.20 PR-VDW 2 6 Temperature dependent 6 9.20 6 Temperature dependent 6 12.33 6 Temperature dependent 6 13.17 Spiroindolinonaphthoxazine PR-VDW 2 photochromic dye SRK-VDW 2 [25] [26] [27] a Mean value of the average absolute relative deviation between experimental data and calculation results which reported in various papers for each component Nomenclature A, A a B, B b d fi kij, Kij P R T V yi Z α parameters used in MKM mixing rules EOS interaction energy parameter parameters used in MKM mixing rules EOS volume parameter EOS constants for KM mixing rules fugacity of component i binary interaction parameter pressure universal gas constant thermodynamic temperature volume mole percent of component i compressibility factor temperature-dependent parameter for calculation of a(T) parameters used in MKM mixing rules β, δ fugacity coefficient φ Superscripts c m critical point parameters of MKM mixing rules for the mix- tures s F Pan Sat VDW solid phase fluid phase Panagiotopoulos and Reid saturation Van der Waals REFERENCES [1] J. 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Tang, Fluid Phase Equilibria 275 (2009) 33–38 [26] [21] A.Z. Panagiotopoulos, D.B. Reid, Fluid Phase Equilibria, 29 (1986) 525-534 P. Coimbra, D. Fernandes, P. Ferreira, M.H. Gil, H.C. de Sousa, J. Supercritical Fluids 45 (2008) 272-281 [27] P. Coimbra, M.H. Gil, C.M.M. Duarte, B.H. Heron, H.C. de Sousa, Fluid Phase Equilibria 238 (2005) 120–128. HADI BASERI ALI HAGHIGHI-ASL MOHAMMAD NADER LOTFOLLAHI School of Chemical, Gas and Petroleum Engineering, Semnan University, Semnan, Iran NAUČNI RAD TERMODINAMIČKO MODELOVANJE RASTVORLJIVOSTI ČVRSTIH JEDINJENJA U NATKRITIČNOM UGLJEN-DIOKSIDU: POREĐENJE PRAVILA MEŠANJA U ovom radu, Peng-Robinson-ova jednačina stanja je korišćena za termodinamičko modelovanje rastvorljivosti različitih čvrstih komponenti u natkritičnom ugljen-dioksidu. Takođe, proučavan je uticaj tri pravila mešanja: Van der Waals-ovo, PanagiotopoulosReid-ovo i modifikovano Kwak-Mansoori-ovo, na tačnost dobijenih rezultata. Dobijena je dobra korelacija između izračunatih i eksperimentalnih podataka u širokom opsegu temperature i pritiska. Modifikovano Kwak-Mansoori-jevo pravilo mešana daje bolju korelaciju u odnosu na ostala pravila mešanja. Ključne reči: rastvorljivost čvrstih jedinjenja; natkritični ugljen-dioksid; jednačina stanja; pravila mešanja 398 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 399−409 (2013) S. NADEEM1 ARSHAD RIAZ2 R. ELLAHI2 1 Department of Mathematics, Quaid-i-Azam University, Islamabad, Pakistan 2 Department of Mathematics and Statistics, FBAS, IIU Islamabad, Pakistan SCIENTIFIC PAPER UDC 5/6:519:51-3 DOI 10.2298/CICEQ120402075N CI&CEQ PERISTALTIC FLOW OF A JEFFREY FLUID IN A RECTANGULAR DUCT HAVING COMPLIANT WALLS In this article, the theoretical and mathematical study of peristaltic transport of a Jeffrey fluid in a rectangular duct with compliant walls is discussed. The constitutive equations are simplified under the implementation of low Reynolds number and long wavelength approximations. The analytical solution of the resulting equations is evaluated by Eigen function expansion method. The graphical aspects of all the parameters of interest are also analyzed. The graphs of velocity for two and three dimensional flow are plotted. The trapping bolus phenomenon is also discussed though streamlines. Keywords: peristaltic flow, Jeffrey fluid, rectangular duct, compliant walls. The study of peristaltic flows is quite useful in physiology and industry because of its large number of applications and in mathematics due to its complicated geometries and solutions of nonlinear equations. In physiology, it is used by many systems in the living body to propel or to mix the contents of a tube. The peristaltic mechanism usually occurs in urine transport from the kidney to the bladder, swallowing food through the esophagus, chyme motion in the gastrointestinal tracts, vasomotion of small blood vessels, movement of Spermatozoa and the human reproductive tract. Theoretically and mathematically, the complete exact solutions of peristaltic flow problems are quite difficult to determine even in viscous fluid theory. However, after using certain physical simplifications such as long wavelength and low Reynolds number approximations, the authors successfully calculate only limited exact and analytical solutions. Some interesting studies are given in the references [1-11]. The study of peristaltic flows of Newtonian and non-Newtonian fluids in two-dimensional symmetric and asymmetric channels is also very useful in a number of applications, specially the study of inter-uterine fluid flow in a nonpregnant uterus [1221]. Recently, Reddy et al. [22] have given the idea that the sagittal cross-section of the uterus may be better approximated by a tube of rectangular cross section than a two dimensional channel and presented the influence of lateral walls on peristaltic flow in a rectangular duct. More recently, this idea has been extended by Nadeem and Akram [23] for nonNewtonian fluids. More studies on the peristaltic flow in three-dimensional rectangular channel are cited in the references [24-25]. A large number of analytical and numerical studies on the peristaltic flow of Newtonian and non-Newtonian fluids in different flow geometries are discussed by Tripathi [26-33]. However, the peristaltic flows of three dimensional non-Newtonian fluids in a rectangular duct having compliant walls have to the best of our knowledge not been explored. The aim of the present work is to discuss the peristaltic flow of a Jeffrey fluid in a rectangular duct with compliant walls. The governing equations of a Jeffrey fluid for three dimensional flows are simplified under the assumptions of long wavelength and low Reynolds number approximation. The exact solutions of the reduced equations having the compliant wall properties are found with the help of the Eigen function expansion method. The physical features of the pertinent parameters are measured with the help of graphs. The circulating bolus scheme is also described with the help of streamlines graphs. Correspondence: Arshad Riaz, Department of Mathematics and Statistics, FBAS, IIU Islamabad 44000, Pakistan. E-mail: arshadriaz26@gmail.com Paper received: 2 April, 2012 Paper revised: 9 July, 2012 Paper accepted: 17 July, 2012 MATHEMATICAL FORMULATION Consider the peristaltic flow of an incompressible non-Newtonian Jeffrey fluid in a cross section of 399 S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… rectangular channel having the width 2d and height 2a. In the present geometry, the Cartesian coordinate system is taken in such a way that the x-axis is taken along the axial direction, the y-axis is taken along the lateral direction and the z-axis is along the vertical direction of rectangular channel (Figure 1). The walls of the channel are assumed to be flexible and are taken as compliant, on which waves with small amplitude and long wave length are considered. CI&CEQ 19 (3) 399−409 (2013) β 2 ∂ 2u ∂p 1 ∂ 2u = + ∂x 1 + λ1 ∂y 2 1 + λ1 ∂z 2 (4) Here β = a/d is the aspect ratio. The corresponding non-dimensional boundary conditions for compliant walls are stated as: u ( x , y , z ,t ) = −1 at y = ±1 (5) u ( x , y , z ,t ) = −1 at z = ±h ( x ,t ) = ±1 ± η ( x ,t ) (6) where η(x,t) = ϕcos2π(x-t), ϕ = b/a (amplitude ratio) and 0≤ ϕ ≤1. The governing equation for the flexible wall may be specified as: L (η ) = p − p 0 where L is an operator, which is used to represent the motion of stretched membrane with viscosity damping forces such that [22]: L =m Figure 1. Schematic diagram for the peristaltic flow in a rectangular duct. The geometry of the channel wall is given by: 2π ( x − ct ) λ z = h ( x ,t ) = ±a ± b cos (1) where b is the amplitude of the wave, λ is the wavelength, c is the velocity of propagation, t is the time and x is the direction of wave propagation. The walls parallel to the xz-plane remain undisturbed and do not measure any peristaltic wave motion. We assume that the lateral velocity is zero as there is no change in lateral direction of the duct cross section. Let (u,0,w) be the velocity for a rectangular duct. The stress tensor for the Jeffrey model is defined by [3134]: S = .. . γ + λ2 γ 1 + λ1 μ (2) In the above equation, λ1 is the ratio of relaxation to retardation times, λ2 is the delay time, γ is shear stress and double dots denote the differentiation with respect to time. Under the assumption of long wave length and low Reynolds number, the governing equations in non-dimensional form for the considered flow problem are stated as [23]: ∂u ∂w + =0 ∂x ∂z 400 (3) ∂2 ∂ ∂4 ∂2 +D +B −T +K 2 4 ∂t ∂t ∂x ∂x 2 (7) In the above equation, m is the mass per unit area, D is the coefficient of the viscous damping membrane, B is the flexural rigidity of the plate, T is the elastic tension in the membrane, K is spring stiffness and p0 is the pressure on the outside surface of the wall due to tension in the muscle, which is assumed to be zero here. The continuity of stress at z=±1±η and using the x-momentum equation yield: ∂p ∂ 3η ∂ 2η ∂ 5η ∂ 3η ∂η = E1 2 + E 2 +E3 5 −E4 3 +E5 (8) ∂x ∂t ∂x ∂x ∂t ∂x ∂x ∂x ∂ 3η ∂ 2η ∂ 5η ∂ 3η ∂η +E2 +E3 5 −E4 3 +E5 = 2 ∂t ∂x ∂x ∂t ∂x ∂x ∂x 1 ∂ 2u β 2 ∂ 2u = + 2 1 + λ1 ∂y 1 + λ1 ∂z 2 E1 (9) at z = ±1 ± η , in which E1 = ma3c/λ3µ, E2 = Da3/λ2µ, E3 = Ba3/cλ5µ, E4 = Ta3/cλ3µ and E5 = Ka3/cλµ are the non-dimensional elasticity parameters. Now we differentiate Eq. (4) with respect to z as follows: β 2 ∂3u 1 ∂ 3u + =0 2 1 + λ1 ∂z ∂y 1 + λ1 ∂z 3 (10) The expressions for stream function satisfying Eq. (3) are defined as (u = ∂ψ/∂z, w = -∂ψ/∂x). Solution of the problem The solution of Eq. (10) with boundary conditions (5), (6) and (9) is computed by the eigenfunction expansion method and is directly defined as: S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… u = −1 + RESULTS AND DISCUSSIONS cosh α z 16C ( −1) π + 1− cos ( 2n − 1) y 2 cosh α h ( 2n − 1) π β n (11) n 3 3 2 n where: α = ( 2n − 1) n π 2 β (12) C = 2π (1 + λ ) ϕ [2E π cos 2π ( x − t ) − 1 2 − (E + 4π ( −E + E + 4E π 2 5 CI&CEQ 19 (3) 399−409 (2013) 1 4 3 2 ) ) sin 2π ( x − t )] (13) The detailed calculation is given in the appendix. It is noted that limiting λ1→0 results in reversing the present problem to the viscous fluid case. It is also observed from the above analysis that employing β→0 and β→1 reduces the discussed geometry to the twodimensional channel and square duct, respectively. (a) In this section, the effects of different physical parameters of a Jeffrey fluid model on the velocity profile of the fluid under discussion are examined graphically and the trapping phenomenon is also illustrated by plotting streamlines for different pertinent parameters. Figures 2-7 are plotted to see the variation of the velocity profile with the emerging parameters β, λ1, E1, E2, E3 and E4. The streamlines are sketched in Figures 8-13, which show the flow behavior with various values of all the observing parameters. In Figures 2, 4 and 5, the velocity profile is plotted with different values of the parameters β, E1 and E2. From these figures, we can observe that the magnitude of the velocity profile is a decreasing function of the above three parameters. The effects of (b) Figure 2. Velocity profile for different values of β for fixed ϕ = 0.2, x = 0.5, t = 0.4, λ1 = 0.5, E1 = 0.1, E2 = 0.2, E3 = 0.01, E4 = 0.2, E5 = 0.3. a) For 2-dimensional, b) for 3-dimensional. (a) (b) Figure 3. Velocity profile for different values of λ1 for fixed ϕ = 0.2, x = 0.5, t = 0.4, β = 2.5, E1 = 0.1, E2 = 0.1, E3 = 0.05, E4 = 0.2, E5 = 0.5. a) For 2-dimensional, b) for 3-dimensional. 401 S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… (a) CI&CEQ 19 (0) 000−000 (2013) (b) Figure 4. Velocity profile for different values of E1 for fixed ϕ = 0.2, x = 0.5, t = 0.4, β = 1.5, λ1 = 0.5, E2 = 0.1, E3 = 0.05, E4 = 0.2, E5 = 0.5. a) For 2-dimensional, b) for 3-dimensional. (a) (b) Figure 5. Velocity profile for different values of E2 for fixed ϕ = 0.2, x = 0.5, t = 0.4, β = 2.5, λ1 = 0.5, E1 = 0.1, E3 = 0.01, E4 = 0.2, E5 = 0.5. a) For 2-dimensional, b) for 3-dimensional. (a) (b) Figure 6. Velocity profile for different values of E3 for fixed ϕ = 0.2, x = 0.5, t = 0.4, β = 2.7, λ1 = 0.5, E1 = 0.1, E2 = 0.1, E4 = 0.2, E5 = 0.5. a) For 2-dimensional, b) for 3-dimensional. 402 S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… CI&CEQ 19 (3) 399−409 (2013) (a) (b) Figure 7. Velocity profile for different values of E4 for fixed ϕ = 0.2, x = 0.5, t = 0.4, β = 3, λ1 = 0.5, E1 = 0.1, E2 = 0.1, E3 = 0.2, E5 = 0.5. (a) For 2-dimensional, (b) For 3-dimensional. (a) (b) (c) (d) Figure 8. Streamlines for different values of β. a) For β = 0.4, b) for β = 0.6, c) for β = 0.8 d) for β = 1. The other parameters are y = 0.5, λ1 = 1, ϕ = 0.2, t = 0.5, E1 = 1, E2 = 0.2, E3 = 0.05, E4 = 0.1, E5 = 0.3. 403 S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… CI&CEQ 19 (3) 399−409 (2013) (a) (b) (c) (d) Figure 9. Streamlines for different values of λ1. a) For λ1 = 0.5, b) for λ1 = 1, c) for λ1 = 1.5, d) for λ1 = 2. The other parameters are y = 0.5, β = 1, ϕ = 0.2, t = 0.5, E1 = 1, E2 = 0.2, E3 = 0.01, E4 = 0.2, E5 = 0.3. (a) (b) (c) (d) Figure 10. Streamlines for different values of ϕ. a) For ϕ = 0.1, b) for ϕ = 0.2, c) for ϕ = 0.3, d) for ϕ = 0.4. The other parameters are y = 0.5, β = 1, λ1 = 1, t = 0.5, E1 = 1, E2 = 0.2, E3 = 0.01, E4 = 0.2, E5 = 0.3. 404 S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… CI&CEQ 19 (3) 399−409 (2013) (a) (b) (c) (d) Figure 11. Streamlines for different values of E1. a) For E1 = 1, b) for E1 = 2, c) for E1 = 3, d) for E1 = 4. The other parameters are y = 0.5, β = 1, λ1 = 1, t = 0.5, ϕ = 0.2, E2 = 0.2, E3 = 0.05, E4 = 0.2, E5 = 0.3. (a) (b) (c) (d) Figure 12. Streamlines for different values of E2. a) For E2 = 0.5, b) for E2 = 1, c) for E2 = 1.5, d) for E2 = 2. The other parameters are y = 0.5, β = 1, λ1 = 1, t = 0.5, ϕ = 0.2, E1 = 0.2, E3 = 0.05, E4 = 0.2, E5 = 0.3. 405 S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… CI&CEQ 19 (3) 399−409 (2013) (a) (b) (c) (d) Figure 13. Streamlines for different values of E3. a) for E3 = 0.01, b) for E3 = 0.05, c) for E3 = 0.09, d) for E3 = 0.13. The other parameters are y = 0.5, β = 1, λ1 = 1, t = 0.5, ϕ = 0.2, E1 = 0.2, E2 = 0.05, E4 = 0.2, E5 = 0.3. different values of the physical parameters λ1, E3 and E4 are mentioned in Figures 3, 6 and 7. From these plots, it is seen that velocity profile rises directly with increasing the magnitude of λ1, E3 and E4. From Figures 2-7, it can also be seen that the velocity attains its maximum value at the centre of the channel and remains symmetric throughout the channel. The streamlines for different values of the emerging parameters are drawn in Figures 8-13 to lookout for the trapping bolus phenomenon. From Figure 8, it can be seen that number of the trapped bolus is reduced when increasing the value of parameter β. Figure 9 is plotted to show the streamlines with the λ1 being increased. From this plot, it is clear that the size of the trapping bolus rises with increasing magnitude of λ1. The streamlines for different values of the parameter ϕ are shown in Figure 10. It is clear from this graph that the number of boluses is decreasing monotonically with increasing ϕ, but the size of the bolus is increasing with ϕ. Figure 11 reveals that the number of trapped boluses is decreasing with E1. In Figure 12, the number of trapped boluses remains unchanged, but increases in size with increasing values of E2 on the left side of the channel and has the opposite 406 behavior on the other side. The streamlines for E3 are shown in Figure 13. It is easy to see from this figure that the boluses decrease in number, but their size changes with the increase of E3. CONCLUDING REMARKS In the present study, the mathematical and graphical results of the peristaltic flow of a Jeffrey fluid in a compliant rectangular duct were discussed. The governing equations were simplified by employing the long wavelength and low Reynolds number approximations. The resulting equations were then solved by using the method of Eigen function expansion. The following main results were observed: • The profile of the velocity is decreasing function of the parameters β, E1 and E2. • The influence of the pertinent parameters λ1, E3 and E4 is totally opposite to that of β, E1 and E2. • The fluid flows more rapidly at the central part of the channel. • The number of boluses is reduced with the increasing effects of the parameters β, ϕ, E1 and E3, while increased in case of λ1. S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… • The size of the bolus changes randomly with the variation of all the physical parameters. • The results for the viscous fluid case can be obtained by taking λ1→0. Nomenclature u, w b a d x, y, z λ μ p c t λ1 λ2 γ γ β ϕ ψ m D B T K p0 velocity components amplitude of the wave height of the channel width of the channel Cartesian coordinates wavelength viscosity pressure velocity of propagation time relaxation time delay time shear stress derivative of shear stress aspect ratio amplitude ratio stream function mass per unit area coefficient of the viscous damping membrane flexural rigidity of the plate elastic tension in the membrane spring stiffness pressure on the outside surface REFERENCES [1] S. Nadeem, S. Akram, Commun. Nonlinear Sci. Numer. Simul. 15 (2010) 312-321 [2] S. Nadeem, N.S. Akbar, Commun. Nonlinear Sci. Numer. Simul. 14 (2009) 3844-3855 [3] M.A. Abd Elnaby, M.H. Haroun, Commun. Nonlinear Sci. Numer. Simul. 13 (2008) 752-762 CI&CEQ 19 (3) 399−409 (2013) [9] N.S. Akbar, S. Nadeem, Int. J. Heat Mass Tran. 55 (2012) 375-383 [10] N.S. Akbar, S. Nadeem, Int. Commun. Heat Mass Tran. 38 (2011) 154-159 [11] T. Hayat, S. Abelman, E. Momoniat, F. M. Mahomed, Math. Comput. Appl. 15 (2010) 638-657 [12] S. Nadeem, S. Akram, Math. Comput. Model. 52 (2010) 107-119 [13] S. Nadeem, S. Akram, Commun. Nonlinear Sci. Numer. Simul. 15 (2010) 1705-1716 [14] A. Ebaid, Phys. Lett., A 372 (2008) 4493-4499 [15] S. Nadeem, N.S. Akbar, Commun. Nonlinear Sci. Numer. Simul. 15 (2010) 2860-2877 [16] S. Srinivas, V. Pushparaj, Commun. Nonlinear Sci. Numer. Simul., 13 (2008) 1782-1795 [17] E.F. Elshehawey, N.T. Eladabe, E.M. Elghazy, A. Ebaid, App. Math. Comput. 182 (2006) 140-150 [18] S. Nadeem, S. Akram, Z. Naturforsch, A 64 (2009) 559– –567 [19] S. Tsangaris, N.W. Vlachakis, J. Fluid. Eng-T. ASME 125 (2003) 382-385 [20] S. Nadeem, S. Akram, Arch. Appl. Mech. 81 (2011) 97–109 [21] S. Nadeem, S. Akram, Int. J. Numer. Methods Fluids 63 (2010) 374-394 [22] M.V. Subba Reddy, M. Mishra, S. Sreenadh, A. R. Rao, J. Fluid. Eng. 127 (2005) 824-827 [23] S. Nadeem, S. Akram, Nonlinear Anal. Real World Appl., 11 (2010) 4238-4247 [24] S. 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Non-Linear Mech. 43 (2008) 915-924. [7] D. Tripathi, Math. BioSci. 233 (2011) 90-97 [8] A.M. Siddiqui, W.H. Schwarz, J. Non-Newton Fluid Mech. 53 (1994) 257-284 APPENDIX Eq. (10) can be written as: C= 1 ∂ 2u β 2 ∂ 2u + 1 + λ1 ∂y 2 1 + λ1 ∂z 2 (14) 407 S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… CI&CEQ 19 (3) 399−409 (2013) Now let us introduce a transformation: u ( x , y , z ,t ) = v 1 ( x , y , z ,t ) + w 1 ( y ) (15) After using the above equation in Eq. (14) we get system of two equations: 2 d w1 =0 dy 2 (16) with B.Cs: w 1 ( ±1) = −1 (17) and C= 1 ∂ 2v 1 β 2 ∂ 2v 1 + 1 + λ1 ∂y 2 1 + λ1 ∂z 2 (18) with B.Cs: v 1 ( x , ±1, z ,t ) = 0, v 1 ( x , y , ±h ,t ) = −1 − w 1 ( y ) (19) Now we solve Eq. (18) with B.Cs (19) by Eigen function expansion method. The Eigen functions for the above problem are defined as: ϕn ( y ) = cos ( 2n − 1) π 2 y , n = 1,2,3... (20) Now we define a series solution of the form: ∞ v 1 = ϕn ( y ) φn ( z ) (21) n =1 Now using the above equation in Eq. (18) and after using the orthogonality condition we obtained: φn ( z ) = 1 − n cosh α n z 16C ( −1) cosh α n h ( 2n − 1)3 π 3 β 2 (22) Using Eqs. (20) and (22), Eq. (21) can be written as: ∞ v 1 ( x , y , z ,t ) = 1 − n =1 n cosh α n z 16C ( −1) π cos ( 2n − 1) y 3 3 2 cosh α n h ( 2n − 1) π β 2 (23) Now from Eqs. (15), (16) and (23) we have the final solution: ∞ u ( x , y , x ,t ) = − 1 + 1 − n =1 n π cosh α n z 16C ( −1) cos ( 2n − 1) y 3 3 2 cosh α n h ( 2n − 1) π β 2 where αn and C are defined in Eqs. (12) and (13). 408 (24) S. NADEEM, A. RIAZ, R. ELLAHI: PERISTALTIC FLOW OF A JEFFREY FLUID… S. NADEEM1 ARSHAD RIAZ2 R. ELLAHI2 CI&CEQ 19 (3) 399−409 (2013) PERISTALTIČKO STRUJANJE JEFFREY-OVOG FLUIDA U PRAVOUGAONOM KANALU SA POPUSTLJIVIM ZIDOVIMA 1 Department of Mathematics, Quaid-iAzam University, Islamabad, Pakistan 2 Department of Mathematics and Statistics, FBAS, IIU Islamabad, Pakistan NAUČNI RAD Rad se bavi teorijskim i matematičkim izučavanjem peristaltičkog strujanja Jeffrey-evog fluida u pravougaonom kanalu sa popustljivim zidovima. Konstitutivne jednačine su pojednostavljena uvođenjem pretpostavkama o malom Rejnolds-ovom broju i velikoj talasnoj dužini. Analitičko rešenje rezultujućih jednačina je dobijeno primenom metode Eigen-ve funkcije širenja. Takođe, grafički su analizirani svi značajni parametri. Prikazani su grafici brzine za dvo- i trodimenzionalno strujanje. Ključne reči: peristaltičko strujanje, Jeffrey-ev fluid, pravougaoni kanal, popustljivi zidovi. 409 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 411−422 (2013) MOHAMMAD RAMEZANI NAVID MOSTOUFI MOHAMMAD REZA MEHRNIA School of Chemical Engineering, College of Engineering, University of Tehran, Iran SCIENTIFIC PAPER UDC 66.069.82:544.4 DOI 10.2298/CICEQ120407076R CI&CEQ EFFECT OF HYDRODYNAMICS ON KINETICS OF GLUCONIC ACID ENZYMATIC PRODUCTION IN BUBBLE COLUMN REACTOR Oxidation of glucose by homogeneous glucose oxidase was performed in rectangular bubble column reactor at 40 °C, ambient pressure and pH of 5.5 while superficial gas (oxygen) velocity was varied in the homogeneous and transition regime in the range of 0.0014–0.0112 m s-1. Effect of superficial gas (oxygen) velocity on the apparent reaction rate and its parameters was determined and it was observed that the apparent reaction rate on the basis of volume of the liquid increased with increasing the superficial gas (oxygen) velocity. The apparent reaction rate was assumed to be in the form of Michaelis-Menten equation and its apparent kinetic parameters were evaluated by the nonlinear regression method. Keywords: bubble column; kinetics; hydrodynamics; Michaelis-Menten equation; oxygen velocity. Bubble columns are gas-liquid contactors in which a gas consisting of one or more reactants is distributed into the column by a sparger and reacts with the liquid phase itself or with a component dissolved or suspended in it [1]. With their simple construction, no mechanically moving parts, efficient mixing and low shear stress and good heat and mass transfer properties, these reactors are becoming more popular in biological processes compared with stirred reactors [2,3]. Bioconversion of glucose to gluconic acid is one of the well known processes in the biological industries. Gluconic acid and its salts are important materials used in pharmaceutical, food, textile, detergent, leather, photographic and other biological industries [4]. In fact, gluconic acid and D-gluconolactone are simple dehydrogenation products of oxidation of Dglucose obtained by glucose oxidase (E.C.1.1.3.4) [5–7]. A detailed description of kinetics of gluconic acid production has been published in several papers [8–10]. The mechanism of this bioconversion can be given by three steps: Correspondence: N. Mostoufi, School of Chemical Engineering, College of Engineering, University of Tehran, Iran. E-mail: mostoufi@ut.ac.ir Paper received: 7 April, 2012 Paper revised: 22 July, 2012 Paper accepted: 22 July, 2012 GOD glucose + O2 ⎯⎯⎯ → D-gluconolactone + H2O2 CAT H2O2 ⎯⎯⎯ → H2O + 1 O2 2 LAC D-gluconolactone + H2O ⎯⎯⎯ → gluconic acid (1) (2) (3) where GOD is glucose oxidase, CAT is catalase and LAC is lactonase. The overall reaction can be considered as follows: glucose + 1 GOD,CAT O2 ⎯⎯⎯⎯→ gluconic acid 2 (4) Nakamura and Ogura [11] proposed the kinetics of the oxidation of glucose by the glucose oxidase from Penicillium amagaskiense. They expressed that semiquinoid intermediates do not affect the reactive mechanism of glucose oxidase. Thereafter, Gibson et al. [5] determined the kinetics and mechanism of glucose oxidase in two different ways, including monometric and stopped flow experiments. They measured the kinetics of glucose oxidase reaction with diverse substrates such as glucose, mannose, xylose and 2-deoxyglucose and concluded that the rate of glucose oxidation is considerably faster than other reactions. Furthermore, they mentioned that the rate of oxidation of glucose depends on oxygen concentration as well as temperature. 411 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… Despite sufficient amount of surveys conducted on kinetics of reaction and mass transfer characteristics of immobilized glucose oxidase [12,13], there are rather fewer studies focused on homogeneous glucose oxidase. Nakao et al. [14] investigated mass transfer characteristics and optimal operating conditions for producing gluconic acid with immobilized glucose oxidase in airlift and bubble column reactors. They concluded that bubble column reactor provides higher gluconic acid productivity and lower glucose oxidase activity decay compared to other type of reactors due to its better mass transfer properties. Afterwards, Bang et al. [15] investigated glucose oxidation in a three-phase stirred airlift reactor. They highlighted the influence of oxygen concentration and gas velocity on the reaction rate and concluded that the reaction rate noticeably increases with oxygen concentration in gas phase as well as gas velocity. Furthermore, Klein et al. [16] and Znad et al. [17] demonstrated the positive influence of air flow rate on the reaction rate of gluconic acid production. Although the effect of temperature on the reaction rate of glucose oxidation has been studied, there are limited surveys dedicated to thorough investi- gations of the effect of gas velocity on this rate. Accordingly, the aim of this work is to investigate the effect of gas velocity and hydrodynamics of the bubble column on the rate of enzymatic oxidation of glucose by glucose oxidase. The reason for choosing the bubble column reactor is that considerably higher amounts of gluconic acid can be produced, glucose oxidase activity decay is lower, and mass transfer properties are better in this reactor compared to other types of reactors [14]. In the present work, glucose was oxidized by homogeneous glucose oxidase at various gas velocities at 40 °C. Considering the Michaelis-Menten equation, the apparent reaction rate parameters were determined. The results of this work can be used in future studies concerning the modeling of bubble columns used in bioprocesses, taking into account reaction and hydrodynamic parameters. EXPERIMENTS AND METHODS Bioreactor set-up The schematic of the experimental setup used in this work is shown in Figure 1. The rectangular bub- Figure 1. Schematic of the experimental set-up. 412 CI&CEQ 19 (3) 411−422 (2013) M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… ble column was made of Plexiglas with dimensions of 0.12 m width, 0.7 m height and 0.05 m depth. The oxygen was introduced through a Plexiglas perforated plate sparger located 0.03 m above the base of the reactor. The sparger was rectangular with the dimensions of 0.12 m length and 0.05 m width. It contained 14 orifices with diameter of 0.0006 m and 0.01 m square pitch. The design of the reactor and sparger was based on the findings of Buwa and Ranade [18] who showed that the sparger design has an insignificant effect on the turbulence and flow regime (for this kind of sparger, with this pitch and hole diameter). A rectangular bubble column was utilized in order to improve the accuracy of measuring bubble sizes as in cylindrical bubble column reactors the curvature of the reactor introduces error when determining bubble size through photographic method. Materials The D-Glucose monohydrate (99% pure) from Fluka was used as reactant in different concentrations of 0.0555, 0.222, 0.3885 and 0.555 mol/ L. Distilled water was used as solvent in all experiments. Glucose oxidase produced by Aspergillus niger (SigmaAldrich Company) fermentation which was claimed to contain 1 mg g-1 of flavine-adenine dinucleotide (FAD) and with activity of 24,800 units g-1 (unit definition: required amount of enzyme to oxidize 1 μmol of glucose to gluconic acid and H2O2, per minute at 25 °C and pH 7). The catalase was produced by bovine liver with activity of 3940 units mg-1. Acetate buffer with pH 5.5 was used for adding the glucose oxidase and catalase to the solution of glucose. The physical properties of glucose solution with two enzymes used in this work are listed in Table 1. Methods All experiments were carried out at controlled temperature (±0.1 K) and pH value (±0.1) using a Mettler Toledo DL28 titrator using 1 M NaOH. The pH of the solution was maintained at 5.5 (maximum GOD activity) by NaOH, which was automatically added to the solution in order to neutralize gluconic acid. The catalase and glucose oxidase with concentration of 0.0101 g/L were added to the aqueous solution of glucose at various concentrations. Since oxygen was CI&CEQ 19 (3) 411−422 (2013) dissolved in the liquid, nitrogen gas was passed through the column to remove the oxygen. The gas was then changed to oxygen and oxygen concentration in the liquid phase was measured by a Mettler Toledo oxygen sensor connecting to a PC and recorded online. Oxygen was introduced into the column through a sparger at superficial velocities of 0.0014, 0.0028, 0.0056 and 0.0112 m/s. All experiments were carried out in the homogeneous and transition regime at atmospheric pressure and 40 °C. For highlighting the effect of gas hold-up and specific gas-liquid interfacial area on reaction rate, this hydrodynamic parameter were determined by the following equations [1]: εG = H G − HL HG (5) i d i3 i d i2 (6) d 32 = a= 6ε G (7) d 32 In order to determine the Sauter mean diameter (d32), the equivalent sphere diameter of bubble (di) is evaluated by Eq. (8) and photographic method: d i = 3 E 2e (8) For evaluating the bubble size distribution, the resulting data from Eq. (8) and number of bubbles in each size acquired from photographs were considered. The fraction of each bubble size in the total length of reactor was obtained from the proportion of number of bubbles in each size to the total number of bubbles. In order to assess the volumetric mass transfer coefficient (kLa), non-stationary or dynamic method was used. Under the assumptions of ideal mixing in gas and liquid phases, constant interfacial area and no significant change in oxygen concentration in the gas phase, the volumetric mass transfer coefficient can be determined from [19]: −t c ∗ − c L ( −k Lat ) τp τ e k a e = − (1 − k Laτ p ) L p ∗ c − c0 (9) Table 1. Physical properties of glucose solution used at 40 °C ρ / kg m-3 μ×103 / Pa s σ×103 / N m-1 0.05551 982.6 0.6891 69.79 0.2220 993.7 0.7463 69.64 0.3885 1000 0.8124 69.47 0.5551 1017 0.8870 69.30 Glucose concentration, mol L -1 413 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… In Eq. (9) τp represents the response time of the oxygen probe which was evaluated as the time needed to reach 63% of the value finally approached when exposed to a step change in concentration [19,20]. In the present work, this constant can be assessed by transferring the oxygen probe kept in a solution of sodium sulfite for 0.5 min (wherein the oxygen concentration is zero) to another solution saturated with oxygen (which in this work was glucose solution). The response time (τp) of the oxygen probe used in this work was evaluated to be 25 s at 40 °C. Due to the fact that hydrogen peroxide has the inhibition effect on GOD and reaction rate [9,21-23], it was necessary to prevent its production by adding sufficient amount of catalase, thus, no free hydrogen peroxide was observed. In order to determine the reaction rate, the concentration of gluconic acid was measured by titration with NaOH. The rates of gluconic acid production at various gas velocities were evaluated by measuring the slope of lines showing the time courses of gluconic acid production while the zero time was taken after 700 s from the enzyme addition. 0.035 u= 0.0014 m/s u= 0.0028 m/s u= 0.0056 m/s u= 0.0112 m/s CI&CEQ 19 (3) 411−422 (2013) RESULTS AND DISCUSSION Effect of gas velocity The quantitative determination of gluconic acid production, evaluated by titration with NaOH, is illustrated in Figure 2 at glucose concentration of 0.0555 mol L-1. The error bars represent standard deviations of the observed values and are presented only for oxygen velocity of 0.0056 m s-1 as an example. The error bars for other oxygen velocities were fairly in the same range and are not displayed to make the figure easy to understand. It can be seen in these figures that variations of gluconic acid concentrations vs. time are linear with the correlation coefficient greater than 0.985. These slopes determine the apparent rate of gluconic acid production. It can be seen that oxygen velocity has a positive effect on producing of gluconic acid and the reaction rate. The determined reaction rate versus oxygen velocity is illustrated in Figure 3. It can be easily recognized that gas velocity has a positive effect on reaction rate and with increasing gas velocity, the reaction rate increases. The results of this study are in agreement with those in literature [15,16]. Bang et 0.03 y = 0.003x + 0.000 R² = 0.994 Gluconic Acid [mol L-1] 0.025 y = 0.002x + 0.000 R² = 0.985 0.02 0.015 y = 0.002x + 0.000 R² = 0.997 0.01 y = 0.001x + 0.000 R² = 0.995 0.005 0 0 1 2 3 4 5 6 7 8 Time [hr] Figure 2. Gluconic acid concentration at various different oxygen velocities. Reaction conditions: [GOD] = 0.0101 g L -1; [CAT] = 0.0101 g L-1; temperature = 313.15 K, pH 5.5 and 0.0555 mol L-1 glucose (error bars are standard deviations). 414 9 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… 0.0045 0.004 C glucose = 0.0555 mol/L C glucose = 0.222 mol/L C glucose = 0.3885 mol/L C glucose = 0.555 mol/L CI&CEQ 19 (3) 411−422 (2013) 0.0035 r [mol L-1 hr-1] 0.003 0.0025 0.002 0.0015 0.001 0.0005 0 0 0.002 0.004 0.006 uG [m 0.008 0.01 0.012 s-1] Figure 3. Reaction rate versus oxygen velocity at various glucose concentrations (error bars are standard deviations). al. [15] concluded that the reaction rate depended on gas velocity for uG < 1.17 cm s-1 while it was independent of gas velocity for uG > 1.17 cm s-1. In the present work, the range of gas velocity was between 0.14-1.12 cm s-1 which is less than 1.17 cm s-1 and the reaction rate was found to be affected by the gas velocity. Higher oxygen velocity amplifies significantly supply of oxygen into the bioreactor and increases gas hold-up which assists to raise the intensity of mixing and leads to boosting the oxygen transfer rate and increases the reaction rate as a result. Figure 3 also shows that the reaction rate is nearly constant in the range of gas velocity of 0.0028 to 0.0056 m s-1. This trend can be related to the available interfacial area in the reactor. The effect of glucose concentration on the reaction rate can also be comprehended from this figure. It is obvious that with increasing glucose concentration the apparent reaction rate is increased. Figure 4 demonstrates the bubble size distribution at various gas velocities considered in this work. It can be seen in this figure that the bubbles at 0.0028 m s-1 are slightly smaller than that at 0.0056 m s-1. It is worth mentioning that according to Buwa and Ranade [18] at the gas velocity of 0.0112 m s-1 there was a transition regime in the bubble column reactor. While higher gas velocity provides more bubbles in the reactor, presence of larger bubbles reduces the inter-phase mass transfer area. As a result, it is suggested that gas velocities of 0.0028 and 0.0056 m s-1 provide almost the same concentration of oxygen in the liquid phase. Consequently, the reaction rates at these gas velocities become the same. In fact, below 0.0028 m s-1 the bubbles are small and relatively far separated each other. Therefore, increasing the gas velocity below this limit only increases the number of bubbles (corresponding to increase in inter-phase mass transfer area). At gas velocities higher than 0.0028 m s-1 the number of bubbles becomes so high that they become closer to each other and coalescence of bubbles begins. Although coalescence of bubbles still exists at gas velocities higher than 0.0056 m s-1, the increase in the number of bubbles outweighs the decrease in the interfacial area, thus, the concentration of oxygen in the liquid phase increases with increasing the gas velocity and the reaction rate increases accordingly. Figure 5 illustrates the effect of glucose concentration on gas hold-up. This figure demonstrates that the gas hold-up decreases with increasing the glucose concentration. In fact, the viscosity of solution increases with increasing the glucose concentration, resulting in formation of larger bubbles. Consequently, the number of bubbles decreases and their rise velocity increases, which makes the gas hold-up decrease. Figure 5 also shows that the gas hold-ups 415 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… CI&CEQ 19 (3) 411−422 (2013) 0.5 uG = 0.0014 m/s uG = 0.0028 m/s uG = 0.0056 m/s uG = 0.0112 m/s 0.45 0.4 0.35 Fraction 0.3 0.25 0.2 0.15 0.1 0.05 0 0 0.5 1 1.5 2 2.5 3 3.5 4 4.5 5 5.5 6 6.5 7 7.5 Bubble size [mm] Figure 4. Bubble size distribution at various gas velocities and glucose concentration of 0.555 mol L-1. 0.14 uG = 0.0014 m/s uG = 0.0056 m/s uG = 0.0028 m/s uG = 0.0112 m/s 0.12 Gas Hold-up (εG) 0.1 0.08 0.06 0.04 0.02 0 0 0.1 0.2 0.3 Glucose concentration 0.4 0.5 0.6 [mol L-1] Figure 5. Gas hold-up at various superficial gas velocities as a function of glucose concentration (error bars are standard deviations). 416 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… 140 uG = 0.0014 m/s uG = 0.0056 m/s CI&CEQ 19 (3) 411−422 (2013) uG = 0.0028 m/s uG = 0.0112 m/s 120 100 a [m-1] 80 60 40 20 0 0 0.1 0.2 0.3 0.4 0.5 0.6 Glucose concentration [mol L-1] Figure 6. Effect of glucose concentrations on specific gas-liquid interfacial area at various superficial gas velocities. for gas velocities of 0.0028 and 0.0056 m s-1 are reasonably close to each other. Variation of specific gas-liquid interfacial area with glucose concentration at various gas velocities is shown in Figure 6. It can be seen in this figure that the specific gas-liquid interfacial area decreases with increasing the glucose concentration. In fact, with increasing the glucose concentration, the gas hold-up decreases which results in decreasing the specific gas-liquid interfacial area (see Eq. (7)). Figure 6 also reveals that the specific gas-liquid interfacial area at both gas velocities of 0.0028 and 0.0056 m s-1 are very close. This also can be attributed to close values of gas hold-up and mean bubble size at these velocities. Figure 7 shows the effect of glucose concentration on volumetric oxygen transfer coefficient. This figure reveals that the mass transfer coefficient decreases with increasing the glucose concentration. This negative effect of glucose concentration on mass transfer coefficient can be attributed to the viscosity of solution. Increasing the glucose concentration increases the viscosity of solution, thus, the turbulent intensity and gas hold-up decrease. As a result, the specific gas-liquid interfacial area decreases and does the oxygen transfer coefficient. It can be seen in Figure 7 that oxygen transfer coefficient for gas velocities of 0.0028 and 0.0056 m s-1 are close. As stated before, the specific gas-liquid interfacial areas for these velocities are significantly close which is the reason for observing almost the same values of oxygen transfer coefficients at these velocities. The experimental results of this work were compared with existing experimental correlations for volumetric mass transfer coefficient. Among the correlations, the correlation proposed by Akita and Yoshida [24]: k LaDc2 = D AB μL = 0.6 ρLD AB 0.5 gDc2 ρL σ 0.62 gDc3 ρL2 2 μL (10) 0.31 ε 1.1 G is in satisfactory agreement with the experimental data as demonstrated in Figure 8. The relative disparity between these results with Akita and Yoshida [24] is attributed to difference in dimension of bubble column reactor, kind and diameter of sparger, physical properties of materials and superficial gas velocity. Since the reaction rate depends on the gas hold-up, the reaction rate should be presented as a function of this hydrodynamic parameter. Therefore, the apparent reaction rate obtained in Figure 2 with the unit of mol/m3 of liquid/h should be converted into mol/m2 of interfacial area/h through the following expression: 417 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… 0.03 uG = 0.0014 m/s uG = 0.0056 m/s CI&CEQ 19 (3) 411−422 (2013) uG = 0.0028 m/s uG = 0.0112 m/s 0.025 kLa [s-1] 0.02 0.015 0.01 0.005 0 0 0.1 0.2 0.3 0.4 Glucose concentration 0.5 0.6 [mol L-1] Figure 7. Effect of glucose concentration on volumetric mass transfer coefficient at various superficial gas velocities (error bars are standard deviations). 0.05 +30 % Calculated kLa from correlation [s-1] 0.045 0.04 0.035 0.03 -30 % 0.025 0.02 0.015 0.01 0.005 0 0 0.005 0.01 0.015 0.02 0.025 0.03 Experimental kLa 0.035 0.04 0.045 [s-1] Figure 8. Comparing the experimental results with the correlation proposed by Akita and Yoshida [24]. 418 0.05 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… r′ × mol mol =r 3 × m Interfacial area.hr m Liq.hr 2 (11) (1− ε G ) m3Liq 1 r m3Gas × = 3 2 ε G m Gas aG m Interfacial area aL where a = aGεG and aL = a/(1-εG). Converted reaction rate against glucose concentration is illustrated in Figure 9 at various gas velocities. It can be seen in this figure that the reaction rate decreases with increasing the gas velocity at various glucose concentrations. The reason for this change in trends of r’ with gas velocity is related to gas hold-up and specific gas-liquid interfacial area (aG) included in the converted reaction rate. With increasing the gas velocity, gas hold-up (εG) and specific gas-liquid interfacial area (aG) increase and the reaction rate decreases when the rate r is almost constant irrespective of the superficial gas velocity, i.e., when r is nearly equal to the chemical reaction rate. The parameter aL is in fact the specific interfacial area per unit volume of the liquid and is a function of the properties of gas and liquid. The variation of aL with glucose concentration is almost the same as that of a, which is shown in Figure 6. Therefore, it is related to the concentration of glucose in the solution. The parameter aL is a strong function of the glucose concentration at low gas velocity while with increasing the gas velocity becomes almost independent of the 14 CI&CEQ 19 (3) 411−422 (2013) glucose concentration. The reason for such a trend can be explained by the change in the physical properties of the solution with glucose concentration. The viscosity of the solution increases with increasing the concentration of glucose. As a result, larger bubbles are formed at higher glucose concentration which reduces the gas holdup and the specific interfacial area. This is the reason for observing the decreasing trend in aL with increasing the concentration of glucose. It is worth mentioning that the same effect of gas velocity on the reaction rate has been already pointed out by Bang et al. [15]. This factor can explain dependence of the reaction rate on the oxygen velocity at low superficial gas velocities and its independence at high gas velocities. Evaluation of apparent kinetic parameters The mechanism of glucose oxidation by GOD was proposed by Nakamura and Ogura [11] and in more details by Gibson et al. [5]. They proposed that oxidation of glucose consists of the following two steps with four apparent kinetic parameters: k k 1 2 Eox +G ⎯⎯ → Ered ⋅ Glu ⎯⎯→ Ered +Glu k (12) k 3 4 Ered +O2 ⎯⎯→ Eox ⋅ H2O2 ⎯⎯→ Eox +H2O2 (13) Duke et al. [25] developed a rate equation for this mechanism with the hypothesis of steady state uG = 0.0014 m/s uG = 0.0028 m/s uG = 0.0112 m/s uG = 0.0056 m/s 12 r' [mol m-2 hr-1] 10 8 6 4 2 0 0 0.1 0.2 0.3 0.4 0.5 0.6 Glucose concentration [mol L-1] Figure 9. Reaction rate per unit interfacial area vs. glucose concentration at various gas velocities (error bars are standard deviations). 419 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… condition. With the assumption that the observed rate r is the chemical reaction rate, the proposed rate equation is expressed as follows: C E,0 t 1 1 1 1 = + + + r k 1C G k 2 k 3C O2 k 4 r 2 According to Beltrame et al. [26], the following composite coefficient kc: kc = 1 k2 + 1 k 3CO2 + 1 (15) k4 can be substituted into Eq. (14) and the equation of apparent reaction rate would be converted into the Lineweaver-Burk form: 1 r = 2 1 1 1 + kc (16) CE,0 t k 1C G k cCE,0 t C G k c k1 + CG (17) In order to determine the apparent kinetic parameters of Michaelis-Menten rate equation (kc and k1), a least square nonlinear regression technique was utilized. Calculated rate constants are given in Table 2. It should be noted that the results in Table 2 are valid only for the limited ranges of enzyme concentration, partial pressure of oxygen and glucose concentration employed in this study. For comparison of these results with other publications, it is necessary to compromise the resulting units with the reported units. For attaining this purpose, the enzyme concentration should be reported in molar. Thereby, the results should be divided by 1.27×10-6, as our enzyme contains 1 mgFAD g-1GOD that is 1.27×10-6 molFAD g-1GOD. The converted values are illustrated in Table 2. These apparent kinetic parameters are compared with those reported in literature [25,26] as described below. Figure 10 demonstrates the variation of apparent reaction rate (14) 2 1 = CI&CEQ 19 (3) 411−422 (2013) or the analogous form of Michaelis-Menten equation: Table 2. Evaluation of kc and k1 for different oxygen velocity examined with two kinds of units Gas velocity, m s -1 kc -1 mol g h k1 -1 s -1 -1 Lg h -1 -1 L mol s 0.0014 0.0758 16.58 2.456 537.3 0.0028 0.1351 29.56 17.33 3791 0.0056 0.1424 31.16 16.25 3555 0.0112 0.2015 44.08 17.76 3884 0.005 Modeling apparent reaction rate [mol L-1 hr-1] +5% 0.004 -5% 0.003 0.002 0.001 0 0 0.001 0.002 0.003 Experimental apparent reaction rate [mol 0.004 L-1 hr-1] Figure 10. Parity plot of calculated apparent reaction rate vs. experimental data. 420 0.005 -1 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… (calculated based on the constants reported in Table 2) as a function of superficial gas velocity and compared with experimental data. It can be seen in this figure that the calculated results are in satisfying agreement with the experimental data with correlation coefficient geater than 0.9436. Beltrame et al. [26] estimated kc and k1 in the range of 0–30 °C. At 30 °C, they reported 0.6606 mol g-1 h-1 and 28.10 L g-1 h-1 for kc and k1, respectively. According to their results, larger values of kc and k1 would be expected at 40 °C. However, k1 and kc in this study are smaller than those reported by Beltrame et al. [26]. One possible reason for this difference is oxygen concentration which in this work is considerably less than that reported by Beltrame et al. [26]. In their research, C0, was equal to 1.18×10-3 mol L-1 while in this work C0 was between 4.27×10-5– –1.37×10-4 mol L-1. As kc is related to steps containing the oxidization of reduced enzyme, lower values resulted in this study compared to those in Beltrame et al. [26]. The lower amount of oxygen dissolved in the liquid phase leads to increase in the amount of reduced enzyme which is converted to Eox.H2O2 (Eq. (13)) and apparent kinetic parameter related to this step is decreased as a consequence. It is worth noting that the reaction rate is a weak function of oxygen velocity. In accordance with Beltrame et al. [26] and results of this work, it can be concluded that the reaction rate depends more on temperature than oxygen velocity. The values of k1 are between 537-3884 s-1 while in the literatures, those are fairly higher. Gibson et al. [5] reported 2100 s-1 for 0 °C and 16000 s-1 for 38 °C. It is followed by Duke et al. [25] who disclosed 3700 s-1 at 0 °C and 23800 at 30 °C. These discrepancies between the results are related to an assumed enzyme concentration and activity which was mentioned about 10-8 mol L-1 [25] as well as the oxygen transfer limitation. However, the difference is within one order of magnitude which seems plausible. CONCLUSIONS The effect of oxygen velocity on the apparent reaction rate of oxidation of glucose by homogeneous glucose oxidase was investigated. It was observed that increasing the gas velocity results in increasing the apparent reaction rate due to higher oxygen transfer from gas phase to liquid phase. At two gas velocities of 0.0028 and 0.0056 m s-1 the apparent reaction rates are noticeably close due to the similarity of the gas hold-ups, specific gas-liquid interfacial areas and the volumetric oxygen transfer coefficients in these two velocities. To emphasize effects of the CI&CEQ 19 (3) 411−422 (2013) hydrodynamic parameters on the apparent reaction rate, the apparent reaction rate was expressed on the basis of the available interfacial area which includes gas hold-up and specific interfacial area. With assuming the apparent reaction rate in the form of MichaelisMenten equation, a satisfactory agreement between the experimental and calculated apparent reaction rates was observed. The apparent constants of the Michaelis-Menten equation were determined by the nonlinear regression method. Nomenclature aG specific gas-liquid interfacial area per unit gas volume (m-1) aL specific gas-liquid interfacial area per unit liquid volume (m-1) a specific gas-liquid interfacial area based on the dispersion volume (m-1) CAT catalase c* equilibrium dissolved oxygen concentration (mol L-1) CE,t initial total enzyme concentration (g L-1) CG glucose concentration (mol L-1) cL dissolved oxygen concentration for physical oxygen absorption (mol L-1) CO2 dissolved oxygen concentration for glucose oxidation (mol L-1) C O* 2 equilibrium dissolved oxygen concentration for glucose oxidation (mol L-1) c0 initial dissolved oxygen concentration for physical oxygen absorption (mol L-1) di sphere equivalent diameter (m) d32 mean bubble size (Sauter mean diameter) (m) E major axis of the ellipsoid (m) e minor axis of ellipsoid (m) Eox oxidized enzyme Ered reduced enzyme G glucose GOD glucose oxidase HG dispersion height (m) HL static liquid height (m) kc kinetic parameter of Michaelis-Menten equation (mol g-1 h-1) k1 kinetic parameter of Michaelis-Menten equation (L g-1 h-1) k2 kinetic parameter related to glucose oxidation (mol g-1 h-1) k3 kinetic parameter related to glucose oxidation (L g-1 h-1) k4 kinetic parameter related to glucose oxidation (mol g-1 h-1) 421 M. RAMEZANI, N. MOSTOUFI, M.R. MEHRNIA: EFFECT OF HYDRODYNAMICS ON KINETICS… volumetric oxygen transfer coefficient (s-1) LAC lactonase r apparent rate of gluconic acid production per unit liquid volume (mol L-1 h-1) r’ apparent rate of gluconic acid production per unit interfacial area (mol m-2 h-1) t time (s) uG superficial gas (oxygen) velocity (m s-1) kLa CI&CEQ 19 (3) 411−422 (2013) [9] J. Mirón, M.P. Gonzalez, J.A. Vázquez, L. Pastrana, M. Murado, Enzyme Microb. Technol. 34 (2004) 513-522 [10] H. Kojima, S. Suzuki, J. Chem. Eng. Jpn. 39 (2006) 1050–1053 [11] T. Nakamura, Y. Ogura, J. Biochem. 52 (1962) 214-220 [12] A. Blandino, M. Macı́ as, D. Cantero, Process Biochem. 36 (2001) 601-606 [13] D. Mislovicova, E. Michalkova, A. Vikartovska, Process Biochem. 42 (2007) 704-709 Greek letter [14] εG τp K. Nakao, A. Kiefner, K. Furumoto, T. Harada, Chem. Eng. Sci. 52 (1997) 4127-4133 [15] W. Bang, X. Lu, A. Duquenne, I. Nikov, A. Bascoul, Catal. 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Biotehnol. 12 (1992) 87-132 MOHAMMAD RAMEZANI NAVID MOSTOUFI MOHAMMAD REZA MEHRNIA School of Chemical Engineering, College of Engineering, University of Tehran, Iran NAUČNI RAD UTICAJ HIDRODINAMIKE NA KINETIKU ENZIMSKE PRODUKCIJE GLUKONSKE KISELINE U BARBOTAŽNOJ KOLONI Oksidacija glukoze slobodno suspendovane glukozo oksidaze je izvršena u pravougaonoj barbotažnoj koloni na 40 °C, atsmosferskom pritisku i pH 5,5, dok je površinska brzina kiseonika varirana u homogenom i prelaznom režimu u opsegu 0,0014–0,.0112 m/s. Određen je uticaj površinske brzine kiseonika na prividnu brzinu reakcije i njene parametre. Uočeno je da se prividna brzina reakcije po jedinici zapremine povećava sa povećanjem površinske brzine kiseonika. Pretpostavljeno je da prividna brzina reakcije sledi Michaelis-Menten-ovu jednačinu, čiji su parametri izračunati metodom nelinearne regresije. Ključne reči: barbotažna kolona, kinetika, hidrodinamika, Michaelis-Menten-ova jednačina, površinska brzina kiseonika. 422 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 423−433 (2013) WEI LI1,2 JINHUI PENG1 SHENGHUI GUO1 LIBO ZHANG1 GUO CHEN1 HONGYING XIA1 1 Key Laboratory of Unconventional Metallurgy, Ministry of Education, Kunming University of Science and Technology, Yunnan, China 2 Faculty of Science, Kunming University of Science and Technology, Yunnan, China SCIENTIFIC PAPER UDC 544.47/.478 DOI 10.2298/CICEQ120421077L CI&CEQ CARBOTHERMIC REDUCTION KINETICS OF ILMENITE CONCENTRATES CATALYZED BY SODIUM SILICATE AND MICROWAVEABSORBING CHARACTERISTICS OF REDUCTIVE PRODUCTS Carbothermic reduction kinetics of ilmenite concentrates catalyzed by sodium silicate were investigated; the reduction degree of ilmenite concentrates reduction reaction was determined as R = 4/7(16y + 56x)(ΔWΣ - fA-PW)/(16y + + 56x + 112). The results show that the reaction activation energy of initial stage and later stage is 36.45 and 135.14 kJ/mol, respectively. There is a great change in the reduction rate at temperatures of 1100 and 1150 °C; the catalysis effect and change of reduction rate were evaluated by TG and DSC curves of sodium silicate. Microwave-absorbing characteristics of reduction products were measured by the method of microwave cavity perturbation. It was found that microwave absorbing characteristics of reduction products obtained at temperatures of 900, 1100 and 1150 °C have significant differences. XRD characterization results explained the formation and accumulation of reduction product Fe, and pronounced changes of microwave absorbing characteristics due to the decrease of the content of ilmenite concentrates. Keywords: sodium silicate; ilmenite concentrates; catalytic reduction; kinetics; microwave absorbing characteristics. The mineral ilmenite (FeTiO3) is the main source of titanium dioxide which is widely used as a white pigment. The common treatment method is thermal reduction of ilmenite to form TiO2 and elemental iron followed by a leach to remove the iron. The reduction of ilmenite concentrate plays an important role in the titanium industry. It has been well documented that ilmenite concentrate usually needs high reductive temperature or needs additives to improve its reactivity when it is directly reduced [1,2]. Over the past several decades, many research studies have been done on the mechanism and kinetics of the reduction of different ilmenite. Wouterlood [3] investigated the reduction of ilmenite with carbon at temperatures of 900 to 1200 °C and found the reaction consisted of two stages: the fast first stage indicating the reduction of ferric to ferrous iron, and a slower second stage in which ferrous iron was reduced to metallic iron. Correspondence: J. Peng, Faculty of Science, Kunming University of Science and Technology, Yunnan,650093, China. E-mail: jhpeng_ok@yeah.net Paper received: 21 April, 2012 Paper revised: 10 August, 2012 Paper accepted: 13 August, 2012 Researches have shown that carbothermic reduction of ilmenite at temperatures below 1200 °C produces metallic iron and reduced form of oxides (TinO2n-1) [4,5]. Carbothermic reduction of ilmenite and rutile was investigated by Welham and Williams [6] at temperatures up to 1500 °C, indicating that the reduction of rutile was found to proceed through a series of oxides TinO2n-1 until the formation of Ti3O5. Kucukkaragoz [7] investigated the reduction of ilmenite concentrate with graphite under argon gas between 1250 and 1350 °C, showing that reduction rates increased with increasing temperature and decreasing particle size. Dewan [8] studied carbothermal reduction of ilmenites of different grades and synthetic rutile in different gas atmospheres. The carbothermal reduction of primary ilmenite concentrate was faster in hydrogen and occurred at a lower temperature than in argon and helium. The reduction in argon and helium had about the same rate and extent [8]. Eungyeul [9,10] researched the reduction of titania-ferrous ore by H2 and CO; Satoshi [11] also investigated the reduction kinetics of natural ilmenite ore with carbon monoxide and found the reduction rate 423 W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… increased with increasing temperature, the rate and the degree of reduction depended on the formation of a metallic shell of iron [9-11]. The reactivity of ilmenite can also be improved by using a pre-oxidization process, increasing the rate of ilmenite reduction and the rate of leaching [12-15]. Zhang and Ostrovski [15] investigated the effects of pre-oxidation and sintering on the phase composition, specific surface area, morphology and reducibility of ilmenite concentrates. It was demonstrated that both pre-oxidation and sintering increased the temperature required to reduce titanium oxides. Pre-oxidization is now a broadly adopted practice in the processing of ilmenite ore for production of TiO2 pigment and metallic titanium. Wang and Yuang [16] described the reduction degree and rate of Bama ilmenite concentrate by graphite at temperatures from 850 to 1400 °C. The reduction degree and reaction rate of the ilmenite increased with increasing temperature. The higher the temperature was, the faster the reaction rate was. The reduction degree of the ilmenite decreased due to the presence of impurities. The ilmenite deposit in Panzhihua region, Sichuan, China accounts for 35% of the titanium resource in the world, and for approximately of 92% in China [17]. So, it is very important to utilize the ilmenite resources efficiently for the development of the titanium industry. However, due to the higher contents of CaO and MgO and complex mineralogy in ilmenite in Panzhihua region, it is very difficult to upgrade the ilmenite to titanium-rich slag, which limits the development and utilization of ilmenite deposit in Panzhihua region; it is urgent to develop new processing technologies of ilmenite concentrates [13,18-20]. In recent years there has been a growing interest in microwave heating in mineral treatment. Advantages in utilizing microwave technologies for processing materials include penetrating radiation, controlled electric field distribution and selective and volumetric heating [21]. Because of these advantages, a number of potential applications of microwave processing materials have been investigated, such as microwave assisted ore grinding, microwave assisted carbothermic reduction of metal oxides, microwave assisted drying and anhydration, microwave assisted mineral leaching, microwave assisted roasting and smelting of sulphide concentrate, microwave assisted pretreatment of refractory gold concentrate, microwave assisted spent carbon regeneration, coke CI&CEQ 19 (3) 423−433 (2013) making and activated carbon production, and microwave assisted waste management, etc. [22-31]. For microwave processing of ilmenite, Itoh et al. described the microwave oxidation of rutile extraction process, in which rutile is extracted from a natural ilmenite ore by oxidation and magnetic separation followed by leaching with diluted acid [32]. Kelly and Rowson investigated microwave reduction of oxidized ilimenite concentrate [33]. Tong et al. evaluated the economic values of industrial applications of carbothermic reduction of metals oxide by microwave heating, showing that the cost is lowered about 15-50% compared to that of conventional method [34]. Cutmore et al. investigated dielectric properties of some minerals [35]. Microwave absorbing characteristics of ilmenite concentrate with different proportions of carbonaceous reduction agents were investigated by the authors’ group [20], which further confirms the feasibility of microwave reduction of ilmenite concentrate. All of these investigations present encouraging results. However, to the best of our knowledge, there is little information about carbothermic reduction kinetics of ilmenite concentrate by using catalyst and microwave absorbing characteristics of reactants and products during microwave irradiation, resulting in difficulty of investigations on the interaction mechanism between microwaves and materials, which limits the application of microwave heating technology in industry. So, there is an urgent need to investigate microwave-absorbing characteristics of materials and accumulation of data of dielectric properties, in order to prompt applications of microwave heating in all different kind of fields. The objective of the present study is to investigate carbothermic reduction kinetics of ilmenite concentrate synergistic catalyzed by sodium silicate and microwave-absorbing characteristics of reductive products measured by the method of microwave cavity perturbation. EXPERIMENTAL Materials The raw material, ilmenite, was obtained from Panzhihua (Sichuan province, PR China). The chemical compositions of ilmenite and proximate analysis of coke were listed in Tables 1 and 2, respectively. It can be seen from Tables 1 and 2 that both ilmenite and coke contain volatiles; especially for Table 1. Chemical compositions of ilmenite concentrate Component Content, mass% 424 TFe TiO2 CaO MgO SiO2 Al2O3 S 32.18 47.85 1.56 6.56 5.6 3.16 ≤0.1 W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… CI&CEQ 19 (3) 423−433 (2013) Table 2. Proximate analysis of coke Water content Ash Volatile Fixed carbon Total sulfur Calorific value 1.93% 27.80% 1.41% 70.80% 2.68% 23.64 MJ/Kg coke, the amount content of volatile, sulfur and water is more than 6.02%. If this amount were also calculated as weight of oxygen loss, it would lead to calculation errors of reduction degree by using the method of weight loss. So, calibrations of weight loss fraction at different reduction temperatures by using coke as reduction agent were investigated, in order to increase the calculation accuracy of reduction degree of ilmenite concentrate. Experimental set up The set-up of kinetics of reduction experiment was illustrated in Figure 1 which consists of a vertical carborundum furnace, a computer monitor system for monitoring the weight change of the reacting sample and a temperature controller. The balance is on the top of furnace and is connected through a suspending thread. The kinetics experimental conditions were as follows: ilmenite concentrate 2 g; addition amount of coke (particle size 180-200 mesh) 15 mass%; ratio of adhesive of sodium silicate 5 mass%. The weighed ilmenite concentrate and coke were thoroughly mixed by stirring over 30 min. Pellets of ilmenite concentrate containing coke were dried at temperature of 500 °C for 6 h in a muffle furnace. Measuring principles of microwave absorbing characteristics The measuring principle and equipment referred to our preciously published paper, in which the method of microwave cavity perturbation and equipment has been described in detail [20]. Reduction degree of ilmenite concentrates The weight loss of pellets containing coke during reduction process included: the evaporation of water, emission of volatiles in coke, reduction of Fe oxide and carbon gasification. According to the definition of basic reduction degree, the following equation could be obtained: R= ΔW 0 × 100% = M0 Δ W Σ − ΔW C − Δ W V − Δ W W = × 100% M0 (1) where ΔW0 is the removing amount of oxygen of iron oxides in ilmenite concentrates (g); M0 is total amount of oxygen in ilmenite concentrates (g); ΔWv is the emission amount of volatiles (g); ΔWw is the emission amount of water (g); ΔWΣ is the total weight loss amount (g); ΔWc is the amount of carbon loss (g). In order to eliminate the effects of release of volatile components and water on reduction degree, pellets of aluminum oxide powder containing coke were prepared using the same method as for pellets of ilmenite concentrates. The emission ratio of volatiles and water of pellets was calculated using the following equation: Figure 1. Schematic diagram of the reductive experimental setup. 425 W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… f A-P = 100 ΔW V + ΔW W W A-P (2) where fA-P is ratio of weight loss for pellets of aluminum oxide powder containing coke and WA-P is the mass of pellets of aluminum oxide powder containing coke. When replacing the mass of pellets of aluminum oxide powder containing coke by using pellets containing carbon (W), W = W A-P , reduction degree was obtained as: R = 100 ΔW Σ − ΔW C − f A-PW M0 (3) Assuming the reaction process of the carbon reduction of iron oxides under the high temperature is: Fe x O y + C = Fe x O y −1 + CO (4) equation: ΔW C = 12 ΔW 0 16 was obtained; so the calculating formula for reduction degree was deduced as: R = 100 4( ΔW Σ − f A-PW ) 7M 0 (5) For carbothermic reduction of ilmenite concentrates within the appropriate reduction temperature, only the reduction process of iron oxides occurs; the reduction process of TiO2 to low-valence titanium will occur accompanying the reduction process only at a higher temperature. So, carbothermic reaction of ilmenite concentrates can be considered as: Fe x O y ⋅ TiO2 + C = Fe x O y −1 + CO + TiO2 (6) If controlling the appropriate temperature, assuming TiO2 formed during the carbothermic reduction process of ilmenite concentrates is not reduced, the reduction degree for ilmenite concentrates can be simplified according to Eq. (5), where M0 should be corrected, if M0r is the ratio of O in FexOy: M 0r = 16 y 16 y + 56 x R = 100 64 y (ΔW Σ − f A-PW ) 7(16 y + 56 x ) (7) (8) The oxygen amount of Fe x O y ⋅ TiO2 is: M 0• = 426 16 y 16 y + 56 x + 112 (9) CI&CEQ 19 (3) 423−433 (2013) At this point, the calculating equation for reduction degree for pellets of ilmenite concentrates containing carbon was finally obtained as: R = 100 4(16 y + 56 x )(ΔW Σ − f A-PW ) 7(16 y + 56 x + 112) (10) RESULTS AND DISCUSSION Calibrations of weight-loss fraction of coke and ilmenite concentrates It can be seen from Tables 1 and 2 that ilmenite and coke contain volatiles. The amount content of volatile, sulfur and water, especially for coke, is more than 6.02%. If this amount were calculated as weight of oxygen loss, it would lead to errors in calculation of reduction degree by using the method of weight loss. So, calibrations of weight loss fraction at different reduction temperatures by using coke as reduction agent were investigated, in order to increase the calculation accuracy of reduction degree of ilmenite concentrate. Calibration conditions: coke mass 0.3 g, ilmenite concentrates 2 g, the others were the same as defined in “Experimental set up”. The upper deck of coke and ilmenite concentrates were covered by Al2O3, which had been calcined to constant weight, in order to prevent coke injection and oxidation of ilmenite concentrates. Furthermore, the process was performed under a protective atmosphere of N2, preventing weight loss of coke oxidation or weight gain of oxidation of ilmenite concentrates. Figures 2 and 3 show the relationship between reduction time and weight loss fraction of coke at different reduction temperatures and the relationship between reduction time and weight loss fraction of ilmenite at different reduction temperatures, respectively. It can be found that the weight loss of both coke and ilmenite concentrates increases with increasing of temperature at the same heating time. Under the same constant temperature, weight loss of coke and ilmenite concentrates increases with increase in time and ilmenite concentrates, losing weight faster at early stage, while weight loss of volatiles is slower at final stage. Therefore, increasing constant temperature and heating time will enhance the weight loss of coke and ilmenite concentrates; if calibrations of weight-loss fraction of coke and ilmenite concentrates were not carried out, it would cause a large calculation error for the reduction degree. The sum of weight losses of coke and ilmenite concentrates at different reduction temperature for carbothermic reduction of ilmenite concentrate were W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… obtained from Figures 2 and 3, and the results are listed in Table 3. 30 1473 1423 1373 1323 20 1273 15 1073 1173 1123 1223 10 12 2g 1g 4g 8 0 300 600 900 Time/s 1200 Figure 2. Relationship between reduction time and weight loss fraction of coke at different reduction temperatures. 1423K 1373K 1323K 1273K 1223K 1173K 1123K 1073K 2.5 2.0 1.5 1.0 0.5 0.0 6g 6 7g 5g 8g 4 2 3.0 Percent mass loss/% 3g 10 5 0 of chemical reaction. If the diameter of pellets were small, it would cause the difficulty of follow-up sample characterization. The weight of pellets was investigated in the present study. The conditions were as follows: sodium silicate 3%; coke 15%, ilmenite concentrate 1-8 g (results shown in Figure 4); other set of conditions: sodium silicate 5%, others the same as defined in “Experimental set up” (results shown in Figure 5). R(%) Percent mass loss/% 25 CI&CEQ 19 (3) 423−433 (2013) 0 300 Time/s 600 900 Figure 3. Relationship between reduction time and weight loss fraction of ilmenite at different reduction temperatures. Carbothermic reduction of ilmenite concentrates catalyzed sodium silicate Generally speaking, the larger the diameter of pellets (weight of pellets), the lower the performance 0 0 500 1000 1500 2000 Time/s 2500 3000 3500 Figure 4. Relationships between reduction degree and different ball weights at 1050 °C. It can be seen from Figure 4 that the reaction rate and weight loss for pellets of 2 g are the highest, the maximum reduction degree is 10.73%, so the weight of pellet was chosen to be 2 g. From Figure 5 it can be seen that the reduction rate becomes faster at temperatures above 1423 K, the reduction degree is 22.74%, being larger compared to that in Figure 4 at the same conditions, while the corresponding amount of sodium silicate has increased only 2%, indicating that sodium silicate has a catalytic effect on the reduction process. If nuclei formation and growth are the controlling steps during the carbothermic reduction of ilmenite concentrates, the rate expression can be given by Table 3. Total weight loss of pellets; coke, 0.30 g; ilmenite concentrate, 2.00 g Temperature, °C Weight loss of coke, g Weight loss of ilmenite concentrate, g Total weight loss, g 800 0.048 0.035 0.083 850 0.052 0.041 0.093 900 0.054 0.042 0.096 950 0.057 0.043 0.10 1000 0.060 0.045 0.105 1050 0.066 0.048 0.114 1100 0.072 0.05 0.122 1150 0.078 0.054 0.132 427 W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… Avrami-Erofeev Equation [36-38], which is one of the equations often used to describe the nucleation kinetics and subsequent crystal growth: 1 ( − ln(1 − α )n ) = kt or α = 1 - exp(-ktn) (11) where α is conversion value, n the reaction order, k the rate constant and t the time. 30 1473K 25 1423K Table 4 that multiples of reaction rate increase from 4.43 to 9.0 rapidly, reaching stabilization at temperature of 1473 K. The linear equation y = −4.3841x − 8.0708 is obtained by fitting the data in Figure 6. The initial apparent activation energy for reduction of ilmenite concentrates catalyzed by Na2SiO3·9H2O was 36.45 kJ/mol; the pre-exponential factor was 60e-8.0708 min-1. By fitting Figure 7, the linear equation y = −16.254x + + 1.3425 was also obtained. The initial apparent activation energy for reduction of ilmenite concentrates catalyzed by Na2SiO3·9H2O was 135.14 kJ/mol; the pre-exponential factor was 60e-1.3425 min-1. -11.4 15 1373K 10 1273k 5 1073K 0 -11.5 1323K 0 1000 2000 3000 Time/s 4000 -11.6 1223K 1173K 1123K -11.7 lnK R/% 20 CI&CEQ 19 (3) 423−433 (2013) 5000 -11.9 Figure 5. Relationships between reduction degree and reduction time. -12.0 Rate equation described by the oxygen weight loss of reactants of TiO2 ⋅ Fe x O y (assumed random nucleation and its subsequent growth, n = 1) could be obtained as: -12.2 ln(1 − α ) = −kt y=-4.3841x-8.0708 -11.8 Experimental data Linear fit of experimental data -12.1 (12) where k is the reaction rate (1/min); α is the oxygen weight loss of reactants of TiO2 ⋅ Fe x O y , being the reduction degree of pellets containing carbon (%); t is reduction time (min). Making a plot by using the equation above and reduction degree data in Figure 5, reaction rate constants at different constant temperatures can be obtained (Table 4), and by making a plot of ln K vs. 1/T. Figures 6 and 7 can be obtained. It can be found from 0.78 0.80 0.82 0.84 0.86 0.88 0.90 0.92 0.94 1/T×10-3(K-1) Figure 6. Plot of ln K vs. 1/T (1023–1273 K range). The TG and DSC curves of Na2SiO3·9H2O were used to confirm its catalytic effect for carbothermic reduction process of ilmenite concentrates. It can be seen from TG curves of sodium silicate in Figure 8 that the temperature range of 348.5–494.3 K is attributed to the weight loss of crystallization water, of which the weight loss ratio being bigger more than 50%, losing almost all crystallization water, and appears as an endothermic peak in DSC curves shown in Figure 9. The melting point of sodium silicate is 1326 K, indicating that melting endothermic Table 4. Reduction temperature and corresponding reaction rate constant Temperature, K -6 -1 Reaction rate constant, 10 min Reaction rate multiplier 1073 5.41 1.00 1123 6.08 1.12 1173 7.51 1.39 1223 8.25 1.52 1273 10.36 1.91 1323 18.47 3.41 1373 23.96 4.43 1423 48.70 9.00 1473 58.50 10.81 428 W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… reaction for sodium silicate occurs, prompting the enhancement of activation of alkali metal of sodium ions, which are absorbed by coke, prompting the reaction of carbon gasification, in agreement with the great changes of reaction rate constant in the temperature range of 1373–1423 K. -9.6 -9.8 -10.0 lnK -10.2 y=-16.254x+1.3425 -10.4 -10.6 -10.8 Experimental data Linear fit of experimental data -11.0 0.67 0.68 0.69 0.70 0.71 0.72 0.73 0.74 0.75 0.76 -3 1/T×10 (K) Figure 7. Plot of ln K vs. 1/T (1323–1473 K range). Changes of microwave-absorbing characteristics and XRD characterization Figure 10 shows the microwave spectra of reduction products of ilmenite concentrates catalyzed by sodium silicate, and Table 5 lists the correspondence microwave absorbing characteristics parameters. Relative frequency shift, attenuations and quality factors (Q) at the first wave crest of microwave CI&CEQ 19 (3) 423−433 (2013) spectra were computed by computer software. From these parameters, the microwave-absorbing characteristics of reduction products at different conditions were compared (Figures 11 and 12). Through analyses of microwave-absorbing characteristics such as attenuation voltage, frequency, bandwidth and quality factor, combined with Table 5 and Figures 10-12, it can be concluded that there are great changes for microwave-absorbing characteristics of reduction products obtained at temperatures of 900 and 1100 °C. In order to confirm the changes for microwave-absorbing characteristics, reduction products obtained at temperatures of 900, 1100 and 1150 °C were also characterized by XRD (Figures 13 and 14). It can be seen from Figure 13 that the phases of reduction products at 1100 °C are FeTiO3 (artificial ilmenite), iron and salts of silicate and very small amount of Fe3O4. A characteristic peak of Fe at 44.68° is 683 cps, showing that the formation of Fe accumulates, and reduction reaction reaches to some extent. The FeTiO3 phase indicates that sodium silicate catalytic reaction is not complete. The Fe3O4 phase shows that mechanism of reduction reaction of ilmenite concentrates catalyzed by sodium silicate is similar to that of common iron ore. It is shown that the intensity of characteristic peak of Fe at 44.68° is 176, 683 and 933 cps from low temperature to high temperature, indicating that the intensity of Fe increases with increasing temperature, resulting in the increase of iron content (under the Figure 8. TG Curves of sodium silicate. 429 W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… CI&CEQ 19 (3) 423−433 (2013) Figure 9. DSC Curves of sodium silicate. Figure 10. Microwave spectra of reduction products. 2.440 Attenuation/v 1.90 2.435 1.85 2.430 1.80 Attenuation Frequency of microwave 1.75 2.425 1.70 2.420 1.65 1.60 2.415 800 900 1000 1100 Reduction temperature/℃ Frequency of microwave/Ghz 2.445 1.95 1200 Figure 11. Relationships between reduction temperature and attenuation, frequency of microwave. 430 W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… CI&CEQ 19 (3) 423−433 (2013) 0.09 54 0.08 42 B andwidth Q uality fact 0.06 36 Quality fact Bandwidth 48 0.07 0.05 30 0.04 800 900 1000 1100 R eduction tem perature/ ℃ 1200 Figure 12. Relationships between reduction temperature and bandwidth, quality factor. Table 5. Microwave-absorbing characteristic parameters of reduction products Product Quality factor (Q) Attenuation voltage, V Frequency, GHz Bandwidth, GHz Empty cavity 2.2135 2.4755 0.0320 77.36 NZ800 1.9342 2.4379 0.0453 53.82 NZ850 1.9241 2.4373 0.0459 53.10 NZ900 1.9081 2.4401 0.0458 53.28 NZ950 1.9303 2.4391 0.0454 53.72 NZ1000 1.9288 2.4385 0.0438 55.67 NZ1050 1.9406 2.4418 0.0438 55.75 NZ1100 1.7955 2.4356 0.0539 45.18 NZ1150 1.6351 2.4234 0.0852 28.44 NZ1200 1.6341 2.4164 0.0782 30.90 Intensity(CPS) 1500 1000 500 0 29-0733> Ilmenite - Fe+2TiO3 35-0796> MgTi2O5 - Magnesium Titanium Oxide 06-0696> Iron - Fe 46-1473> Aenigmatite - Na2Fe5+2TiSi6O20 24-0203> Augite - Ca(Mg,Fe)Si2O6 19-0629> Magnetite - Fe+2Fe2+3O4 10 20 30 40 50 60 70 80 90 2θ / ° Figure 13. XRD Pattern of reductive product at 1100 °C. 431 W. Li et al.: CARBOTHERMIC REDUCTION KINETICS OF ILMENITE… CI&CEQ 19 (3) 423−433 (2013) 6000 Itensity(CPS) 5000 900 ℃ 4000 △ ▲ 3000 1150 ℃ 2000 1000 1100 ℃ 0 10 20 30 40 50 60 70 80 90 2-theta( ° Figure 14. XRD Patterns of reductive product at different reduction temperatures (△: FeTiO3, ▲: Fe). same measuring conditions). The intensity of the reduction product at temperature of 900 °C is low, which can be considered the initial formation of Fe, demonstrating that the reduction reaction of ilmenite concentrates catalyzed by sodium silicate starts at temperature of 900 °C. The intensity of characteristic peak of FeTiO3 at 32.58° is 1859, 1652 and 908 cps from low temperature to high temperature, showing that the content of FeTiO3 decreases with increasing reaction temperature, however, even though the temperature reaches 1150 °C, the reduction reaction of ilmenite concentrates is not complete. The sharp change of intensity becomes small at temperature range of 1100 to 1150 °C, indicating that reaction rate of carbothermic reduction of ilmenite concentrates becomes faster, which agrees with the results of multiples of rate increasing from 4.43 to 9.0 listed in Table 4. Therefore, the formation of reduction production iron and Fe accumulation and the decrease of content of ilmenite concentrates are the main reasons for the large changes of microwave-absorbing characteristics of reduction products. CONCLUSIONS The reduction degree of ilmenite concentrates reduction reaction has been deduced as R = 4/7(16y + 56x)(ΔWΣ - fA-PW)/(16y + 56x + 112) from reduction degree expression R = 100ΔW0/M0. Kinetics experimental results show that activation energies of initial and later stage are 36.45 and 135.14 kJ/mol, respectively. There is a great change for reduction rate at temperatures of 1100 and 1150 °C; the catalysis effect and great change for reduction rate were evaluated by TG and DSC curves of sodium silicate. Microwave-absorbing characteristics of reduction products were measured by the method of microwave cavity perturbation. It was found that mic- 432 rowave absorbing characteristics of reduction products obtained at temperatures of 900, 1100 and 1150 °C have significant differences. XRD characterization results explained the formation and accumulation of reduction product Fe, and pronounced changes of microwave absorbing characteristics due to the decrease of the content of ilmenite concentrates. Acknowledgments The authors would like to express their gratitude for the financial support of the Major Program of National Natural Science Foundation of China (Grant No. 51090385), the International S&T Cooperation Program of China (No. 2012DFA70570), the Yunnan Provincial International Cooperative Program (No. 2011IA004) and Reserve Talents of Middle-aged and Young Academic Technology Leaders in Yunnan Province (2011CI010). REFERENCES [1] C.S. Kucukkaragoz, R.H. Eric, Miner. Eng. 19 (2006) 334-337 [2] K.T. Suresh, V. Rajakumar, P. Grieveson, Metall. Mater. Trans., B 18 (1987) 713-717 [3] H.J. Wouterlood, J. Chem. Tech. Biotechnol. 29 (1979) 603–618 [4] S.Z. El-Tawil, I.M.Morsi, A.A. Francis, Can. Metall. Quart. 32 (1993) 281-288 [5] S.Z. El-Tawil, I.M. Morsi, A.Yehia, A.A. Francis, Can. Metall. Q. 35 (1996) 31-38 [6] N.J. Welham, J.S. Williams, Metall. Mater. Trans., B 30 (1999) 1075–1081 [7] C.S. Kucukkaragoz, R.H. Eric, Miner. Eng. B (2006) 334– –337 [8] a) M.A.R. Dewan, G. 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Technol. 113 (2001) 184-188 N. Cutmore, T. Evans, D. Crnokark, A. Middleton, S. Stoddard, Miner. Eng. 13 (2000) 729-736 [36] M. Avrami, J. Chem. Phys. 7 (1939) 1103-1112 [22] M. Al-Harahsheh, S.W. Kingman, Hydrometallurgy 73 (2004) 189-203 [37] M. Avrami, J. Chem. Phys. 8 (1940) 212-224 [38] M. Avrami, J. Chem. Phys. 9 (1941) 177-184. [23] K.E. Haque, Int. J. Miner. Process. 57 (1999) 1-24 WEI LI1,2 JINHUI PENG1 SHENGHUI GUO1 LIBO ZHANG1 GUO CHEN1 HONGYING XIA1 1 Key Laboratory of Unconventional Metallurgy, Ministry of Education, Kunming University of Science and Technology, Yunnan, China 2 Faculty of Science, Kunming University of Science and Technology, Yunnan, China NAUČNI RAD KINETIKA KARBOTERMALNE REDUKCIJE KONCENTRATA ILMENITA KATALIZOVANE NATRIJUM-SILIKATOM I MIKROTALASNO-APSORPCIONE KARAKTERISTIKE PROIZVODA REDUKCIJE U ovom radu je ispotivana kinetika karbotermalne redukcije koncentrata ilmenita katalizovane natrijum-silikatom. Stepen redukcije koncentrata ilmenita je određen kao R = = 4/7(16y + 56x)(ΔWΣ - fA-PW)/(16y + 56x + 112). Rezultati pokazuju da su vrednosti energije aktivacije početne i krajnje faze 36,45 i 135,14 kJ/mol, redom. Na temperaturama od 1100 i 1150 °C primećena je velika promena u brzini redukcije. Uticaj katalize i velika promena brzine redukcije je određena pomoću TG i DSC krive natrijum-silikata. Mikrotalasno-apsorpcione karakteristike proizvoda redukcije su merene metodom mikrotalasnih kavitacionih perturbacija. Ustanovljeno je da se mikrotalasne apsorpcione karakteristike proizvoda redukcije dobijenih na temperaturama 900, 1100 i 1150 °C jako menjaju i u kombinaciji sa XRD objašnjavaju stvaranje i akumulaciju proizvoda redukcije Fe. Velike promene mikrotalasnih apsorpcionih karakteristika se javljaju i zbog smanjenja sadržaja koncentrata ilmenita. Ključne reči: natrijum-silikat; koncentrati ilmenita; katalitička redukcija; kinetika; mikrotalasne apsorpcione karateristike. 433 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 435−440 (2013) CI&CEQ YU SUN1,2 SHUANGSHUANG XU1 YANLING GENG1 XIAO WANG1 TIANYOU ZHANG2 ISOLATION AND PURIFICATION OF LIGNANS FROM Schisandra chinensis BY COMBINATION OF SILICA GEL COLUMN AND HIGH-SPEED COUNTER-CURRENT CHROMATOGRAPHY Shandong Analysis and Test Center, Shandong Academy of Sciences, Jinan, China 2 Shandong MingRen Freda Pharmaceutical co., LTD, Jinan, Shandong, China Silica gel column combined with high-speed counter-current chromatography separation was successfully applied to the separation of schizandrin (I), angeloylgomisin H (II), gomisin A (III), schisantherin C (IV), deoxyschizandrin (V), γ-schisandrin (VI) and schisandrin C (VII) from the fruits of Schisandra chinensis (Turcz.) Baillon. The petroleum ether extracts of the fruits of S. chinensis were pre-separated first on a silica gel column and divided into two fractions as sample 1 and sample 2. 260 mg of sample 1 was separated by HSCCC using petroleum ether–ethyl acetate–methanol–water (10:8:10:8, v/v) as the two-phase solvent system and 18.2 mg of schizandrin, 15.7 mg of angeloylgomisin H, 16.5 mg of gomisin A and 16.7 mg of schisantherin C were obtained. 230 mg of sample 2 was separated using petroleum ether–ethyl acetate–methanol–water (10:0.5:10:1, v/v) as the two-phase solvent system and 19.7 mg of deoxyschizandrin, 23.4 mg of γ-schisandrin and 18.2 mg of schisandrin C were obtained. The purities of the separated compounds were all over 94% as determined by HPLC. The chemical structures of these compounds were confirmed by ESIMS and 1H-NMR. 1 SCIENTIFIC PAPER UDC 582.678.2:543.544:615.89 DOI 10.2298/CICEQ120504078S Keywords: Schisandra chinensis (Turcz.) Baillon., lignans, high-speed counter-current chromatography. Schisandra chinensis fructus (Wuweizi in Chinese), the dried fruits of Schisandra chinensis (Turcz.) Baillon, is officially listed in the Chinese Pharmacopoeia and one of the most famous traditional Chinese medicine [1]. It is distributed in northeastern China, Russia, Japan and Korea [2]. Traditionally, the fruits of S. chinensis are used for the treatment of chronic cough, nocturnal emission, spermatorrhea, enuresis, frequent urination, protracted diarrhea, night sweating, spontaneous sweating, palpitation and insomnia [1]. It is also widely used as a functional ingredient and nutritional in foods, such as beer, wine, beverages, jam and other products [3]. Additionally, it is known to be a rich source of lignans with a dibenzo[a,c]cyclooctadiene skeleton [4,5], which have attracted considerable interest because of their bipheCorrespondence: X. Wang, Shandong Analysis and Test Center, Shandong Academy of Sciences, 19 Keyuan Street, Jinan, 250014, China. E-mail: wxjn1998@126.com Paper received: 4 May, 2012 Paper revised: 13 August, 2012 Paper accepted: 19 August, 2012 nyl-type structures and multiple pharmacological activities. In particular, pharmacological research indicated that these lignans can inhibit LTB4 production [6], afford protection against hepatic damage induced by CCl4 [7] and protect the liver from injury after administration of acetaminophen [8]. Due to these particular pharmacological and clinical effects of lignans separated from S. chinensis, it is necessary to establish an efficient method for the preparative separation and purification of these compounds from this plant. Recently, several extraction, isolation and purification methods of S. chinensis lignans have been reported, such as ionic liquid-based ultrasonic-assisted, ionic liquid based microwave simultaneous, macroporous resins and ion exchange resin [9–12]. High-speed counter-current chromatography (HSCCC) is a liquid-liquid partition chromatographic technique that can eliminate irreversible adsorption of sample onto the solid support [13]. It has been widely used in preparative separation and purification of various natural products [14–17]. In the previous studies, Peng et al. [18] obtained schizandrin and gomisin A from S. chinensis by HSCCC and 435 Y. SUN et al.: ISOLATION AND PURIFICATION OF LIGNANS FROM S. chinensis… Huang et al. [19] separated deoxyschizandrin and γ-schisandrin from S. chinensis using this method too. In order to get more pure compounds, a simple and feasible method needs to be established. In this paper, an efficient method, combination of silica gel column and HSCCC, was reported. Seven lignans were successfully isolated and purified from S. chinensis by HSCCC. EXPERIMENTAL Reagents and materials Chromatographic grade methanol (Tedia Company Inc, Fairfield, USA) was used for HPLC analysis. Organic solvents including petroleum ether (60–90 °C), ethyl acetate, ethanol and methanol were all of analytical grade (Damao Chemical Factory, Tianjin, China). The water used in solutions and dilutions was treated with a Milli–Q water purification system (Millipore, USA). The fruits of S. chinensis were purchased from a local drug store. The botanical identification was made by Dr. Zongyuan Yu, Shandong Academy of Chinese Medicine, China. Silica gel (200–300 mesh, Haiyang Chemical Factory, Qingdao, China) was used for sample preparation. Apparatus A model GS10A–2 Preparative HSCCC (Beijing Emilion Science & Technology Co., Beijing, China) equipped with a PTFE multilayer coil (1.6 mmI.D.×110 m, with a total capacity of 230 mL). The β values of this preparative column range from 0.5 at internal to 0.8 at the external (β = r/R, where r is the distance or the rotation radius from the coil to the holder shaft, and R (R = 8 cm), the revolution radius or the distances between the holder axis and central axis of the centrifuge). The rotation speed is adjustable from 0 to 1000 rpm, and 800 rpm was used in this experiment. The two-phase solvent was pumped into the column with a model NS–1007 constant-flow pump. Continuous monitoring of the effluent was achieved with a model 8823A–UV monitor at 254 nm. A model 3057– 11 portable recorder was employed to record the chromatogram. The HPLC equipment used was a Waters Empower system (Milford, MA, USA) including a model 600 system controller, a model 600 pump, a model 600 multisolvent delivery system, a model 996 photodiode array detector. Preparation of crude extract About 500 g of the dried fruits of S. chinensis were milled to powder (about 40 mesh) and extracted 436 CI&CEQ 19 (3) 435−440 (2013) with 3 L 95% ethanol for three times (2 h each time) at the temperature of 70 °C. The extracts were combined and evaporated to dryness with a rotary evaporator at 50 °C. Then the ethanol extracts were dissolved in water and extracted with petroleum ether for 3 times. The petroleum ether extraction solutions were concentrated to dryness, which yielded 36.8 g of crude extract. Then the petroleum ether extract was further subjected to the silica gel column (200 g of silica gel H, 200–300 mesh) eluted stepwise with petroleum ether–ethyl acetate (5:1 and 2:1, v/v) to obtain two fractions. The petroleum ether–ethyl acetate (2:1, v/v) effluent was collected and evaporated to dryness with a rotary evaporator at 50 °C and about 28.6 g of powder was obtained (sample 1). The petroleum ether–ethyl acetate (5:1, v/v) effluent was also collected and evaporated to dryness with a rotary evaporator at 50 °C and about 4.2 g of powder was obtained (sample 2). All these samples were stored in a refrigerator until subsequent HSCCC separation. Selection of the two-phase solvent systems Approximately 2 mg of the test sample was weighed in a 10 ml test tube to which 2 ml of each phase of the equilibrated two-phase solvent system was added. The tube was capped and shaken vigorously for 1 min to equilibrate the sample thoroughly with the two phases. Equal volumes of each phase were then analyzed by HPLC to obtain the partition coefficients (KD). The KD value was expressed as the peak area of compound in the upper phase divided by the peak area of compound in the lower phase. HSCCC Separation In each separation process, the multilayer coiled column was first entirely filled with the upper phase (stationary phase) of the solvent. The apparatus was then rotated at 800 rpm, while the lower phase (mobile phase) was pumped into the column at a flow rate of 2 mL/min. After hydrodynamic equilibrium was reached, as indicated by a clear mobile phase eluting at the tail outlet, the sample solution was injected through the sample port. The effluent from the outlet of the column was continuously monitored with a UV detector at 254 nm. The chromatogram was recorded for 50 min after sample injection. Each peak fraction was manually collected according to the UV absorbance profile and analyzed by HPLC. Analysis and characterisation of HSCCC fractions The two samples and each peak fraction from HSCCC were analyzed by HPLC. The analyses were accomplished by a Shim–Pack VP–ODS column (250 mm×4.6 mm I.D., 5 μm) at a column temperature of Y. SUN et al.: ISOLATION AND PURIFICATION OF LIGNANS FROM S. chinensis… 25 °C. Mobile phase was performed with methanol– water (75:25, v/v). The flow rate was 1.0 mL/min. Detection wave was 254 nm. The HSCCC fractions were all analyzed by ESI– MS on an Agilent 1100/MS–G1946 (Agilent, Santa Clara, CA, USA) and NMR spectra on a Varian–600 NMR spectrometer (Varian, Palo Alto, CA, USA) with chloroform (CDCl3) as solvent. RESULTS AND DISCUSSION In HSCCC separation, the choice of a suitable two-phase solvent system, which can provide an ideal range of the KD for the targeted compounds, is the first and critical step. In general, the most suitable range of the KD value is close to 1 [13]. Too large KD values tend to produce excessive sample band broadening, while too small KD values usually result in poor peak resolution. Several two-phase solvent systems were tested and the KD values were measured, and summarized in Table 1. It was found that no two-phase solvent system was suitable for separation of the target compounds by one-step HSCCC separation according to the KD values shown in Table 1. Thus, the petroleum ether extracts of the fruits of S. chinensis were pre-separated first on a silica gel column. Different kinds of solvent systems such as petroleum ether–ethyl acetate, petroleum ether–diethyl ether, trichlormethane– methanol were tested for the separation. Different elution gradients were also investigated. It was found that when petroleum ether–ethyl acetate (5:1 and 2:1, v/v) was used for the separation, the crude extract was separated into two fractions. Sample 1 (2:1 fraction) mainly contained compounds I–IV, and sample 2 (5:1 fraction) mainly contained compounds V–VII. Meanwhile, these compounds were largely enriched after the separation of silica gel column. Thus, sample 1 was used for HSCCC separation of compounds I–IV, CI&CEQ 19 (3) 435−440 (2013) and sample 2 for compounds V–VII. The HPLC chromatograms of sample 1 and sample 2 are shown in Figure 1. In accordance with the KD values of compounds I–IV shown in Table 1, it can be seen that both petroleum ether–ethyl acetate–methanol–water with volume ratios of 10:8:10:8 and 10:8:9:8 were suitable for separation of compounds I–IV. So these solvent systems were tested for HSCCC separation. When petroleum ether–ethyl acetate–methanol–water (10:8:10:8, v/v) was used as the two-phase solvent system, the separation result was better than that of petroleum ether–ethyl acetate–methanol–water (10:8:9:8, v/v) was used. So 260 mg of sample 1 was separated by HSCCC with the solvent system of petroleum ether–ethyl acetate–methanol–water (10:8:10:8, v/v). The HSCCC chromatogram of sample 1 is shown in Figure 2A. The fractions of HSCCC were collected according to HPLC analysis. 18.2 mg of schizandrin (I), 15.7 mg of angeloylgomisin H (II), 16.5 mg of gomisin A (III) and 16.7 mg of schisantherin C (IV) were obtained with the purities of 98.5, 94.4, 97.7 and 95.6%, respectively. The HPLC chromatograms of compounds I–IV are shown in Figure 1a–d. From Table 1, it can be seen that petroleum ether–ethyl acetate–methanol–water with volume ratios of 10:1:10:1, 10:0.5:10:1 and 10:0.5:10:0.5 were all suitable for separation of compounds V–VII. When petroleum ether–ethyl acetate–methanol–water (10:1:10:1 and 10:0.5:10:0.5, v/v) were used as the two-phase solvent system, compounds VI and VII were successfully separated, however, compound V could not be obtained. While when petroleum ether– ethyl acetate–methanol–water (10:0.5:10:1, v/v) was chosen as the two-phase solvent system, compounds V–VII could all be obtained. So petroleum ether–ethyl acetate–methanol–water (10:0.5:10:1, v/v) was chosen to be the two-phase solvent system for the separation Table 1. Partition coefficient (KD) values of target compounds in different two-phase solvent systems Solvent system composition (petroleum ether–ethyl acetate–methanol–water), v/v Compound I II III IV V VI VII 1:1:1:1 1.38 2.73 3.72 5.23 15.40 — — 10:8:10:10 1.14 2.31 3.10 4.15 14.63 — — 10:8:12:8 0.25 0.62 0.97 1.28 5.74 13.14 10.84 10:8:10:8 0.65 1.11 1.48 1.96 11.62 — 13.76 10:8:9:8 0.92 1.65 2.02 2.43 10.01 17.21 14.66 10:5:10:5 0.24 0.35 0.57 0.96 3.37 8.73 6.68 10:2:10:2 0.13 0.17 0.29 0.62 1.77 3.02 2.17 10:1:10:1 0.06 0.07 0.10 0.11 0.43 1.55 1.00 10:0.5:10:1 0.06 0.07 0.13 0.15 0.74 1.98 1.28 10:0.5:10:0.5 0.02 0.02 0.06 0.07 0.36 1.03 0.70 437 Y. SUN et al.: ISOLATION AND PURIFICATION OF LIGNANS FROM S. chinensis… CI&CEQ 19 (3) 435−440 (2013) Figure 1. HPLC Chromatograms of the ethyl acetate fraction of Magnolia sprengeri and HSCCC peak fractions (I–VII). Experimental conditions: column, Shim–pack VP–ODS column (250 mm×4.6 mm i.d., 5μm); column temperature, 25 °C; mobile phase, methanol–water (25:75, v/v); flow rate, 1 mL/min; detection, 254 nm; injection volume, 20 µL. 438 Y. SUN et al.: ISOLATION AND PURIFICATION OF LIGNANS FROM S. chinensis… CI&CEQ 19 (3) 435−440 (2013) Figure 2. HSCCC Chromatograms. A) Sample 1. HSCCC Conditions: Two-phase solvent system: petroleum ether–ethyl acetate– methanol–water (10:8:10:8, v/v); mobile phase: lower phase; flow rate: 2 mL/min; detection, 254 nm; sample size: 260 mg dissolved in 5 mL of the upper phase and 5 mL of the lower phase. B) Sample 2. HSCCC Conditions: Two-phase solvent system: petroleum ether– ethyl acetate–methanol–water (10:0.5:10:1, v/v); mobile phase: the lower phase; flow rate: 2 mL/min; detection, 254 nm; sample size: 230 mg dissolved in 5 mL of the upper phase and 5 mL of the lower phase. and purification of compound V–VII. The HSCCC chromatogram of sample 2 was shown in Figre 2B. 19.7 mg of deoxyschizandrin (V), 23.4 mg of γ-schisandrin (VI) and 18.2 mg of schisandrin C (VII) were obtained from 230 mg of sample 2 with the purities of 94.3, 95.6 and 98.2%, respectively. The HPLC chromatograms of compounds V–VII are shown in Figure 1e–g. The chemical structure of each peak fraction of HSCCC was identified according to its ESI-MS and 1 H-NMR data. Compared with the data given in [20– -27], peaks I–VII in Figure 2 were indentified as schizandrin, angeloylgomisin H, gomisin A, schisantherin C, deoxyschizandrin, γ-schisandrin and schisandrin C. CONCLUDING REMARKS The results of our studies described above clearly demonstrated that the combination of silica gel column chromatography and HSCCC was successfully used in the separation and purification of schizandrin, angeloylgomisin H, gomisin A, schisantherin C, deoxyschizandrin, γ-schisandrin and schisandrin C from the fruits of S. chinensis. It is proved that the combined use of silica gel column chromatography and HSCCC is a good separation strategy that can also be used for the separation and purification of other lignans from natural products. Acknowledgments Financial supports from the Natural Science Foundation of China (20872083), scientific and technological major special project (2010ZX09401-302-512) and the Key Science and Technology Program of Shandong Province (BS2009SW047) are gratefully acknowledged. REFERENCES [1] State Pharmacopoeia Committee, Chinese Pharmacopoeia, 2010 ed., China Press of Traditional Chinese Medicine, Beijing, 2010, p. 61–62. [2] J.L. 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Sci. 29 (2006) 1630–1636 I. Yuinobu, T. Heihachiro, Y. Itiro, Chem. Pharm. Bull. 30 (1982) 3207–3211 [16] J.K. Li, X.C. Ma, F.Y. Li, J.K. Wang, H.R. Chen, G. Wang, X. Lv, C.K. Sun, J.M. Jia, J. Sep. Sci. 33 (2010) 1325– –1330 [27] D. Hu, X.K. Wang, Y.F. Cao, Z.H. Liu, N. Han, J. Yin, Asian J. Trad. Med. 4 (2009) 14-18. YU SUN1,2 SHUANGSHUANG XU1 YANLING GENG1 XIAO WANG1 TIANYOU ZHANG2 1 Shandong Analysis and Test Center, Shandong Academy of Sciences, Jinan, China 2 Shandong MingRen Freda Pharmaceutical co., LTD, Jinan, Shandong, China NAUČNI RAD IZOLACIJA I PREČIŠĆAVANJE LIGNINA IZ Schisandra chinensis KOLONSKOM HROMATOGRAFIJOM NA SILIKAGELU KOMBINOVANOM SA HSCCC HROMATOGRAFIJOM Kolonska hromatrografija na silikagelu kombinovana sa HSCCC hromatrografijom je uspešno primenjena za razdvajanje šizandrina (I), angeloilgomisina H (II), gomisina A (III), šisanderina C (IV), deoksišizandrina (V), γ-šisandrina (VI) i šisandrina C (VII) iz ploda Schisandra chinensis (Turcz.) Baillona. Petroletarski ekstrakti ploda S. chinensis prethodno razdvojeni na koloni sa silikagelom su podeljeni na dve frakcije: uzorak 1 i uzorak 2. Uzorak 1 (260 mg) je razdvojen HSCCC hromatografijom koristeći petroletar-etil acetat–metanol-voda (10:8:10:8, v/v) kao dvofazni sistem rastvarača, pri čemu je dobijeno 18,2 mg šizandrina, 15,7 mg angeloilgomisina H, 16,5 mg gomisina A i 16,7 mg šisanderina C. Uzorak 2 (230 mg) je razdvojen HSCCC hromatografijom koristeći petroletar-etil acetat–metanol-voda (10:0.5:10:1, v/v) kao dvofazni sistem rastvarača, pri čemu je dobijeno 19,7 mg deoksišizandrina, 23,4 mg γ-šisandrina i 18,2 mg šisandrina C. Čistoća izdvojenih jedinjenja je veća od 94%, što je određeno HPLC metodom. Hemijske strukture ovih jedinjenja su dokazane ESI-MS i 1H-NMR metodama. Ključne reči: Schisandra chinensis (Turcz.) Baillon., lignin, HSCCC hromatografija. 440 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 441−448 (2013) HUSEIN DIBAEI ASL1 MAJID ABDOUSS2 MAHMOUD TORABI ANGAJI3 AMINODDIN HAJI4 1 R&D Department, Asia Technology Pioneers Co. Ltd., Tehran, Iran 2 Department of Chemistry, Amirkabir University of Technology, Tehran, Iran 3 Polymers and Chemical Engineering Group, Faculty of Engineering, Tehran University, Tehran, Iran 4 Department of Textile Engineering, Birjand Branch, Islamic Azad University, Birjand, Iran SCIENTIFIC PAPER CI&CEQ SURFACE AND MECHANICAL PROPERTIES OF POLYPROPYLENE/CLAY NANOCOMPOSITE Huge consumption of polypropylene in the industries like automotive motivates academic and industrial R&Ds to find new and excellent approaches to improve the mechanical properties of this polymer, which has no degradation effect on other required performance properties like impact resistance, controlled crystallinity, toughness and shrinkage. Nowadays, nanoparticles play a key role in improving the mechanical and surface properties of polypropylene. In this study, three compositions of polypropylene/nanoclay, containing 0, 2 and 5% of nanoclay were prepared in an internal mixer. For characterizing the nanoclay dispersion in polymer bulk, TEM and XRD tests were used. For scratch resistance testing, scratch lines were created on the load of 900 grain on sheets and SEM images were taken and compared with neat PP scratch image. Crystallinity and mechanical behavior were studied. The results showed that mechanical properties and scratch resistance of the composites were improved. Keywords: nanocomposite, nanoclay, polypropylene, mechanical behavior. UDC 678.742.3 DOI 10.2298/CICEQ120226079D Polypropylene (PP) is an important thermoplastic material because of its good processing ability, high strength, chemical resistance, and low cost [1]. It has been used as the material of choice for interior auto parts and other component applications. However, the surface of polypropylene and its copolymers are generally very susceptible to damage [2]. Beside the improvement of stiffness and strength of polypropylene, its scratch resistance improvement is critical. A better understanding of the role of additives and fillers in the scratch behavior of thermoplastic polyolefins (TPOs) is needed for the maximum utilization of TPOs for automotive applications. A wide range of inorganic materials, such as glass fibers, talc, calcium carbonate and clay minerals have been successfully used as additives or reinforcement to improve the stiffness and strength of polypropylene, but scratch susceptibility has not been improved [3,4]. Correspondence: M. Abdouss, Department of Chemistry, Amirkabir University of Technology, Hafez Ave., Tehran, Iran. E-mail: phdabdouss44@aut.ac.ir Paper received: 26 February, 2012 Paper revised: 30 August, 2012 Paper accepted: 30 August, 2012 Nanocomposites are a new growing generation of polymer-composites, which can give us a good solution for this problem. Nanocomposites are able to play a magical role in the polymer industry [5,6]. Polymer nanocomposites are a new class of multiphase materials containing a dispersion of an ultrafine phase, typically in the range of 1–100 nm. Among the different nanoparticles, nanoclay has attracted significant attention because it provides two distinct opportunities for dispersion in the polymer matrix that include intercalation and exfoliation. These studies indicated that polymer nanocomposites exhibit enhanced strength, modulus, and flame retardancy that are not exhibited by the individual phases or conventional composites containing micrometer size particles or fibers [1,7-14]. Automakers such as Ford and General Motors Corp. are beginning to use nanocomposites, made by the conventional process, in nonstructural applications. For example, GM is using the material in the step-assist on the GMC Safari/Chevrolet Astro minivans [15]. 441 H.D. ASL et al.: SURFACE AND MECHANICAL PROPERTIES OF POLYPROPYLENE/CLAY … In this study, scanning electron microscopy (SEM) is used to characterize the scratch patterns on the polymer surface, and other changes on mechanical properties of polypropylene were investigated. EXPERIMENTAL The polypropylene (PI0800) used in the experiments was a product of Bandar Imam Co. Nanoclay (Nanoline DK1) was provided by Fenghong Clay Chem. Co. (China). PP-MAH, as a compatibilizer (trade name Fusabond-MD353D) was purchased from Dupont Chem. Co. An internal mixer (Haake HBI system 90, 300cc, fill factor 0.8) was used to prepare the required composites (Table 1). Initially PP-MAH and nanoclay were mixed with ratio of 2:1 and then PP was added to the mixer. The mixing temperature was kept at 180 °C, the rotation speed set at 100 rpm. The mixing time was 8 min. In order to prepare the film of desirable dimensions, 2.5 g of composite were pressed under 12 atm. at 220 °C for 5 min. The sample was then cooled to room temperature. Films with thickness of 1.5 mm were obtained. CI&CEQ 19 (3) 441−448 (2013) used for the measurement of notched impact strength according to ASTM D256. Differential scanning calorimetry (DSC) curves were recorded on a DSC 2010 machine (TA Instruments, New Castle, DE, USA) to examine the thermal behavior of samples. Approximately 5 mg of each sample was used and the measurements of the samples were performed by heating from 20 to 200 °C at a rate of 10 °C/min under nitrogen atmosphere. For the transmission electron microscopy (TEM) analysis, the specimen was microtomed to an ultra thin section of 70 nm thickness using an ultracryomicrotome with a diamond knife. The structure was observed under a Phillips CM 12. Scratch resistance and hardness of the specimens were tested following the procedure previously described [16]. To evaluate the depth of the scratches, SEM investigations were done using a Cambridge S-360 instrument. X-ray diffraction (XRD) data were collected on a Siemens D5000 XRD with a 2θ range of 1.2–12°. RESULTS AND DISCUSSIONS Mechanical properties Table 1: composition of the compounds Compound PP Nanoclay PP-gr-Ma D1 100 0 0 D2 96 2 2 D3 90 5 5 The tensile properties were determined in accordance with ASTM D-638 using Instron 6025 tensile testing equipment. A Zwick 5102 impact tester was The tensile and flexural strength of the samples are shown in Tables 2 and 3, and the impact resistance is presented in Table 4. As can be seen from these results, the strength and modulus were substantially increased compared with the neat PP without significant variations in toughness or impact strength as measured by standard nothed Izod Test. Beside the mechanical properties, XRD patterns of nanoclay D2 and D3 and have been achieved (Figure 1). Curve analysis for these three samples Table 2. Tensile strength test results of specimens Speciemen Width/thickness Strain at peak Elongation at break Peak stress Stress at yield Break stress Strain at yield Modulus mm % mm MPa MPa MPa % MPa D1 9.85/3.9 8.144 9.07 28.8 28.72 27.25 6.926 1100 D2 9.8/3.9 6.512 8.2 35.1 34.8 34.6 5.73 1450 D3 9.8/3.9 6.08 7.2 38.3 38.2 38 5.6 1720 Table 3. Flexural strength test results Speciemen Width/thickness, mm Strain at break, % Modulus, MPa Strain at peak, % D1 10.55/9.95 0.105 1094.41 0.095 Stress at yield, MPa 39.2 D2 9.9/9.65 0.081 1415.52 0.081 44.55 D3 9.9/9.65 0.076 1650.15 0.062 49.98 Table 4. Impact resistance results Sample Impact resistance; Izod, N m/m 442 D1 D2 D3 20.2 19 18 H.D. ASL et al.: SURFACE AND MECHANICAL PROPERTIES OF POLYPROPYLENE/CLAY… CI&CEQ 19 (3) 441−448 (2013) Figure 1. XRD Pattern of: a) nanoclay; b) nanocomposite D2; c) nanocomposite D3. indicates that the interlayer platelet spacing of nanoclay is about 21 Å. Dissapearance of the d001 diffraction peak in D2 and D3 indicates the exfoliated structure of layers in nanocomposite. TEM images (Figure 2) were taken in order to obtain visible evidence of nanoclay layers in the polymer matrix. Mechanical tests, TEM and XRD results and their comparison with other nanocmposite researches led us to conclude that D2 and D3 have mechanical properties expected from a nanocomposite [5,7,15]. The strong interaction in the polypropylene–clay system is responsible for significant changes in physical and mechanical properties [8]. Scratch resistance properties In typical studies of scratch behavior of polypropylene, many factors such as filler type, additive, lubricant, impact modifier and surface morphology have been considered but in nanocomposites scratch studies, filer-matrix adhesion, positioning and orientation of nanolayers and polymer chains in the matrix have appeared as new factors [17]. Here we discuss these factors. For characterizing the scratch patterns of sample surface, SEM images were taken (Figure 3) and the hardness of the surfaces was determined (Table 2). The crystallinity behavior of the samples was studied by DSC technique (Figure 4). There is a 443 H.D. ASL et al.: SURFACE AND MECHANICAL PROPERTIES OF POLYPROPYLENE/CLAY… D2 CI&CEQ 19 (3) 441−447 (2013) D3 Figure 2. TEM Images of D2 and D3. Figure 3. SEM Micrographs of the scratch damage region at load of 900 g on the surface of each sample. 444 H.D. ASL et al.: SURFACE AND MECHANICAL PROPERTIES OF POLYPROPYLENE/CLAY… CI&CEQ 19 (3) 441−448 (2013) Figure 4. Differential scanning calorimerty (DSC) graphs of samples; TmD1 = 165.81 °C, TmD2 = 167.2 °C, TmD3 = 169.3 °C. direct relation between the hardness and scratch resistance of polypropylene nanocomposites. Under load, plastic deformation and stress whitening appear when scratch resistance is not high enough; this is due to the formation of voids, microcrazing and debonding in polymer surface [3,17]. These fracture features of the surface lead to intense scattering of light from the surface and, in turn, 445 H.D. ASL et al.: SURFACE AND MECHANICAL PROPERTIES OF POLYPROPYLENE/CLAY … CI&CEQ 19 (3) 441−448 (2013) increase the scratch visibility. We can visually compare the fracture features of the specimen surfaces, but for a comprehensive study, visibility factor of the surfaces, was used for the comparison of scratch lines in D1, D2 and D3. To calculate the visibility factor, the gray value of every pixel in scratch image was determined using image analyzing software. The G function was as below: (scratch visibility). This bonding restricts the microcrazing and formation of voids and plastic deformation. The compatibilizer effect is considerable in better bonding strength. Also it could offset the positive effect from the increased clay dispersion and has shielding, plasticizing and miscibility effects [10]. For the rest of the paper, we describe the effective parameters, which have more influences on scratch resistance of nanoclay-filled polyolefin. G (image − pixel) = Gray value (0-255) in an image pixel (0 = black, 255 = white) Polymer chains positioning near the surface The fracture feature of the scratched surface of the polymer lead to increase of diversity of G on the image. So, the average value of G' (image differentiation) was considered as a visibility factor: n G′(image − pixel) n = visibility factor (n = number of pixels in image) The comparison in Table 5 suggested the sequence of visibility factor as D1 < D2 < D3. High visibility factor indicates weak scratch resistance. Therefore, the nanocomposite had more scratch resistance than neat polypropylene (Table 4) and D3 is fairly better than D2. The improvement of scratch resistance and mechanical properties of polypropylene without more destruction in other required properties can be a revolutionary development in the auto parts industry. Better bonding strength between the surfaces of nanoclay layers and the polymer is another important factor that determines the amount of fracture features Layered structure of clay is determined as a key factor in improving the properties of polymers. Difusion of polymer chains to basal spacing of layers and its interaction with layer surfaces lead to a new structure in polymer bulk with lower entanglements of the chains (Figure 5). In this situation, the chains had a more elastic behavior when they were under stress. Also, the high aspect ratio of layers leads to damp the stress down and restrict the advance of stress to depth of polymer. Crystallinity and nucleation The crystallinity percentage and morphology strongly influence the scratch behavior and have direct effects on scratch resistance. Incorporating nanoclay and pure montmorillonite in the polymer matrix provides additional nucleation sites, thereby increasing the crystallinity. In this study, the crystallinity of specimens increased according to χcD3 < χcD2 <χcD1, in which χcD3 is the percentage of crystallinity and is calculated as ΔHrev/ΔH°; where ∆Hrev is the endothermic melting enthalpy (Figure 4) and ∆H° is the melting enthalpy of Table 5. Comparison of visibility parameters and hardness of the specimens Specimen Visibility factor (image differentiation) Hardness (Shore D) D1 143.1 71 D2 97.2 74 D3 70.9 77 Figure 5. Schematics of chains and layers positioning near the surface. 446 H.D. ASL et al.: SURFACE AND MECHANICAL PROPERTIES OF POLYPROPYLENE/CLAY… 100% crystalline polypropylene [18]. High percentage of crystallinity increases the resistance of cracking and void creation under the scratch load. Nanoclay affects the crystallization behavior by increasing the equilibrium melting point of α and γ crystals indicative of thermodynamic interaction with the host matrix and is corroborated by the shift in the glass transition temperature [10]. CI&CEQ 19 (3) 441−448 (2013) REFERENCES [1] Y. Yang, J. Chen, Q. Yuan, R.D.K. Misra, Mater. Sci. Eng., A 528 (2011) 1857-1863 [2] J. Chu, C. Xiang, H.J. Sue, R. Hollis, Polym. Eng. Sci. 40 (2000) 944-955 [3] C. Xiang, H.J. Sue, Polym. Eng. Sci. 41 (2001) 23-31 [4] S. Zokaei, R. Lesan Khosh M.R. Bagheri, Mater. Sci. Eng., A 445 (2007) 526-536 Other parameters which may be considered [5] J. W. Cho, D.R. Paul, Polymer 42 (2001) 1083-1094 • Damping of stresses due to the layer structure of clay is the most influential factor in improving surface properties of D3. • Quality of organic modification of the montmorillonite, lubricant and other surface modifiers. [6] K. Friedrich, S. Fakirov, Z. Zhang, Polymer composites: from nano- to macro-scale, Springer, New York, 2005, p. 92 [7] C. Deshmane, Q. Yuan, R.D.K. Misra, Mater. Sci. Eng., A 460 (2007) 277-287 [8] C. Deshmane, Q. Yuan, R.S. Perkins, R.D.K. Misra, Mater. Sci. Eng., A 458 (2007) 150-157 [9] S.M. Lai, W.C. Chen, X.S. Zhu, Composites, A 40 (2009) 754-765 [10] R.D.K. Misra, Q. Yuan, J. Chen, Y. Yang, Mater. Sci. Eng., A 527 (2010) 2163-2181 [11] R.D.K. Misra, Q. Yuan, P.K.C. Venkatsurya, Mech. Mater. 45 (2012) 103-116 [12] V. Ramuni, Q. Yuan, J. Chen, R.D.K. Misra, Mater. Sci. Eng., A 527 (2010) 4281-4299 [13] Q. Yuan, S. Awate, R.D.K. Misra, Eur. Polym. J. 42 (2006) 1994-2003 [14] Q. Yuan, R.D.K. Misra, Polym. 47 (2006) 4421-4433 [15] S. Sinha Ray, M. Okamoto, Prog. Polym. Sci. 28 (2003) 1539-1641 [16] T. Koch, D. Machl, Polym. Test. 26 (2007) 927-936 [17] R.D.K. Misra, H. Nathani, A. Dasari, Mater. Sci. Eng., A 386 (2004) 175-185 [18] Ph. H. Nam, P. Maiti, M. Okamoto, Polym. 42 (2001) 9633-9640. CONCLUSION Addition of nanoclay in small amounts (2 and 5%) improves the scratch resistance and mechanical properties of polypropylene. This case does not credit for typical additives such as talc; they increase susceptibility for plastic deformation in the polymer surface. The layered structure of clay is an important factor that affects the damping of stresses. Because of the non-polar backbone of PP, a suitable compatibilizer is essential for the interaction of polypropylene and organo-layers. The nanoclay/polypropylene nanocomposite is a potential material for automotive industry with a wide range of usages and it can be a choice of substitution for other polymers in automotives. 447 H.D. ASL et al.: SURFACE AND MECHANICAL PROPERTIES OF POLYPROPYLENE/CLAY … HUSEIN DIBAEI ASL1 MAJID ABDOUSS2 MAHMOUD TORABI ANGAJI3 AMINODDIN HAJI4 1 R&D Department, Asia Technology Pioneers Co. Ltd., Tehran, Iran 2 Department of Chemistry, Amirkabir University of Technology, Tehran, Iran 3 Polymers and Chemical Engineering Group, Faculty of Engineering, Tehran University, Tehran, Iran 4 Department of Textile Engineering, Birjand Branch, Islamic Azad University, Birjand, Iran NAUČNI RAD CI&CEQ 19 (3) 441−448 (2013) POVRŠINSKE I MEHANIČKE OSOBINE NANOKOMPOZITA POLIPROPILEN/GLINA Ogromna potrošnja polipropilena u automobilskoj industriji motiviše akademska i industrijska istraživanja i razvoj radi pronalaženja novih pristupa u poboljšanju mehaničkih osobina ovog polimera, koji nema degradacioni efekat na druge tražene performance, kao što su otpornost na udar, kontrolisana kristalnost, žilavosti i skupljanje. Danas, nanočestice imaju ključnu ulogu u poboljšanju mehaničkih i površinskih osobina polipropilena. U ovom radu, mikserom su pripremljene tri kompozicije polipropilen/nanoglina koje sadrže 0, 2 i 5% nanogline. Karakterizacija nanogline dispergovane u polimeru je izvršena pomoću TEM i XRD analiza. Za test otpornosti na grebanje, ogrebotine su formirane pri opterećenju od 900 linija po ploči, nakon čega su snimljene SEM slike i poređene sa PP scratch slikama. Takođe je proučavana kristalnost i mehaničko ponašanje kompozita. Rezultati su pokazali da su mehaničke osobine i otpornost na grebanje kod kompozita znatno poboljšani. Ključne reči: nanokompoziti, nanoglina, polipropilen, mehaničko ponašanje. 448 Available on line at Association of the Chemical Engineers of Serbia AChE www.ache.org.rs/CICEQ Chemical Industry & Chemical Engineering Quarterly 19 (3) 449460 (2013) A. ABDALLAH EL HADJ1 C. SI-MOUSSA1 S. HANINI1 M. LAIDI2 1 Laboratoir de BioMatériaux et Phénomène de Transfert (LBMPT), Université de Médéa, Quartier Ain D’heb, Médéa, Algérie 2 Unité de Développement des Equipement Solaires, Tipaza, Algérie SCIENTIFIC PAPER UDC 544:615:661.12 DOI 10.2298/CICEQ120407005E CI&CEQ APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE FOR THE CORRELATION OF SOLUBILITY OF SOME PHARMACEUTICAL AND STATIN DRUGS IN SC-CO2 In this work, the solubilities of some anti-inflammatory (nabumetone, phenylbutazone and salicylamide) and statin drugs (fluvastatin, atorvastatin, lovastatin, simvastatin and rosuvastatin) were correlated using the Perturbed-Chain Statistical Associating Fluid Theory (PC-SAFT) with one-parameter mixing rule and commonly used cubic equations of state Peng-Robinson (PR) and SoaveRedlich-Kwong (SRK) combining with van der Waals 1-parameter (VDW1) and van der Waals 2-parameter (VDW2) mixing rules. The experimental data for the studied compounds were taken from literature at temperature and pressure in ranges of 308–348 K and 100–360 bar, respectively. The critical properties required for the correlation with PR and SRK were estimated using Gani and Noonalol contribution group methods whereas, PC-SAFT pure-component parameters: segment number (m), segment diameter (σ) and energy parameter (ε/k) have been estimated by Tihic’s group contribution method for nabumetone. For phenylbutazone and salicylamide those parameters were determined using a linear correlation. For statin drugs, PC-SAFT parameters were fitted to solubility data, and binary interaction parameters (kij and lij) were obtained by fitting the experimental data. The results were found to be in good agreement with the experimental data and showed that the PC-SAFT approach can be used to model solid-SCF equilibrium with better correlation accuracy than cubic equations of state. Keywords: solid solubility, cubic equation of state, PC-SAFT, anti-inflammatory, supercritical carbon dioxide, correlation. The chemical industry conducts constant research in new technologies where the main objective is to satisfy the customer expectations by offering high-efficiency products and to comply with international standards, which are becoming more and more severe in terms of hygiene and environment protection. Super critical fluids are one of the most interesting technologies that became the target of several research studies in recent years. Such importance is related to the development of new cheap-priced pro- Correspondence: A.A. El Hadj, Laboratoir de BioMatériaux et Phénomène de Transfert (LBMPT), Université de Médéa, Quartier Ain D’heb, 26000, Médéa, Algérie. E-mail: a_abdallahelhadj@yahoo.fr Paper received: 7 April, 2012 Paper revised: 27 January, 2013 Paper accepted: 31 January, 2013 ducts without pollution constraints related to the environment. One of their major trumps is to be a plausible alternative to the organic solvents. In many cases, they offer some solutions that cannot be provided by traditional techniques in terms of efficient operation, non-toxicity, availability, low-cost and the easiness of separation compared to classic process. Thus, many works have been published on the application of this technology [1-3]. Carbon dioxide is the most commonly used supercritical fluid because of its ability to replace organic solvents with more advantages (its availability, inertness, non-toxicity, low critical temperature and pressure). Modelling of solubility of solids in supercritical fluids is needed for the separation process design, development and optimization. Undoubtedly, the most used models are the cubic equations of state, such as 449 A.A. EL HADJ et al.: APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE… Peng-Robinson (PR) [4] and Soave-Redlich-Kwong (SRK) [5]. Although those models are the basic tools for supercritical fluid-solid equilibrium calculations, their application is associated with some drawbacks, mainly the non-availability of the solids properties for pharmaceutical compounds, polymers and bio-molecules (critical properties, molar volume and sublimation pressure). For this reason, and in order to perform the estimation of those parameters, several studies [6-7] have been carried out based on the socalled group contribution techniques, but their prediction ability is limited to classes of components with simple structures. Therefore, the sensitivity of solubility correlations to solids’ properties can add a factor of uncertainly to the approach. For example, Coimbra [8] and Valderrama and Zavaleta [9] found that the variations of 10% in the sublimation pressure estimation of solute might produce deviations between 5 and 19% in solubility calculations. To surpass this problem, more accurate methods were developed, such as the Marrero and Gani [10] and Nannoolal method [11]. More theoretical equations of state were developed based on Werthiem’s perturbation theory [12–14] such as Statistical Associating Fluid Theory (SAFT) [15-17], Lennard-Jones (SAFT-LJ) [18-19], soft-SAFT [20-21], Variable Range (SAFT-VR) [22–23], Hard-Sphere (SAFT-HS) [24-26], and PerturbedChain (PC-SAFT) [27-28], and recently SAFT + Cubic equation of state [29], etc. In the last decade, attempts were carried out in order to model the phase equilibrium with the latter SAFT-EOS where numerous applications were reported in the literature and have been recently reviewed by McCabe and Galindo [30]. SAFT models require five pure associating-component parameters and three parameters for nonassociating fluids: the segment number (m), the interaction energy (ε/k) and the segment diameter (σ). The application of PC-SAFT-EOS for modeling of solid compounds-SCF phase equilibrium is limited because of the non-availability of pure component parameters for multifunctional molecules. Several works treating this subject can be found in the literature [31-33]. The purpose of this work is the application of both PC-SAFT equation of state, Peng-Robinson (PR) and Soave-Redlich-Kwong (SRK) cubic equations of state for correlating the solubility of some anti-inflammatory drugs (compounds that are non-steroidal antiinflammatory drugs (NSAIDs) with analgesic and antipyretic properties and are used to treat fever, headache and pain associated with cold influenza and arthritis) and statin drugs in supercritical CO2 (components are used to reduce cholesterol and risk of heart attack [34]). The chemical structures of the studied solid drugs are shown in Figure 1. THERMODYNAMIC MODELS In this work, the PC-SAFT, PR and SRK equations of state were used for correlating of solid drugs in the supercritical carbon dioxide. The PR and SRK equation of state The PR equation of state The explicit form of PR equation of state for mixture can be written as: P am T RT v bm v v bm bm v bm Figure 1. Chemical structures of the studied drugs. 450 CI&CEQ 19 (3) 449460 (2013) (1) A.A. EL HADJ et al.: APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE… where P is the pressure, T is the temperature, R is the gas constant, v is the molar volume of the component, and am and bm are van der Waals energy and volume parameters for mixture, respectively. The latter parameters can be obtained using mixing rules. In this work, the van der Waals 1-parameter (VDW1) and van der Waals 2-parameter (VDW2) rules were applied: VDW1 mixing rule: CI&CEQ 19 (3) 449460 (2013) The SRK equation of state SRK cubic equation of state for mixture is given by the following expression: P RT v bm am (T ) v v bm For pure components, ai and bj are expressed as follows: am y i y j ai a j 1 k ij (2) a (T ) 0.42747 bm y i bi (3) with: i j i am y i y j a i a j 1 k ij (4) bm y i y j bij (5) i (6) where k ij and l ij are the binary interaction parameters; ai and bj are energy and volume parameters for pure components defined as: R 2Tc2 ai 0.45724 (Tr ,w ) Pc (7) with Tr , being a temperature-dependent function in the attractive parameter of EOS defined as: Tr , 2 1 0.37464 1.5422 0.26992 2 1Tr 0.5 (8) bi 0.077796 RTc Pc (9) where is the acentric factor, Tc and Pc are the critical constants, and Tr is the reduced temperature. The expression for the fugacity coefficient for a mixture can be written as: ln i b 0.08664 j (12) bi ( Z 1) ln(Z B ) bm n 2 y j a ij A j 1 bi Z (1 2)B ln am bm Z (1 2)B 2 2B (10) 1 0.480 1.574 0.176 2 1 Tr 0.5 j b bj bij i 1 l ij 2 R 2Tc2 (Tr ,w ) Pc (Tr ,w ) VDW2 mixing rule: i (11) RTc Pc 2 (13) (14) It should be mentioned that am and bm for SRKEOS can be obtained using the van der Waals 1parameter (VDW1) and 2-parameter (VDW2) rules cited in the PR-EOS section. The expression of fugacity coefficient is given by: ln i bi (Z 1) ln( Z B ) bm ai bi A B (2 )ln(1 ) B b Z am m (15) The PC-SAFT equation of state The Perturbed-Chain Statistical Associating Fluid Theory (PC-SAFT) is an equation of state that is expressed in terms of Helmholtz energy for mixtures of non-associating molecules: ǎ = A /NkT = aid + ahc + adisp (16) id where a is the ideal gas contribution that is considered as unit, ahc is the contribution of hard sphere chain reference system and adisp is the contribution of dispersion force. As it can be seen, this equation consists of the hard-chain reference contribution and the dispersion contribution, and it can be expressed in terms of Helmholtz energy for N-component of non-associating chains as: ãres = ãhc + ãdisp (17) The hard-chain reference contribution is given by: 451 A.A. EL HADJ et al.: APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE… N a hc ma hs y i (mi 1)ln g iihs ( ii ) (18) i 1 where m is the mean segment number in the mixture: N m y i mi (19) i 1 where yi is the mole fraction of chains of component i, mi is the number of segments in a chain of component i. Dispersion contribution a disp 2 I 1,xk m 2 3 I 1(m 2 3 )xk { mk C1I 2 mC1,xk I 2 mC1I 2,xk (20) CI&CEQ 19 (3) 449460 (2013) a res kres (T ,v ) res a Z 1 kT x k T ,v ,xj k res a y i x T ,v ,x ij (27) Modeling solid-SCF phase equilibrium The solubility of a non-volatile pure solid (2) in a supercritical fluid (1), y2, is determined from standard thermodynamic relationships by equating fugacities in the solid phase and in the supercritical phase for each component (the isofugacity condition): f 2solid f 2SCF (28) m 2 2 3 mC1I 2 (m 2 2 3 )xk } The fugacity of component (2) in the supercritical phase is expressed by: Pairs of unlike segments are obtained by using conventional combining rules: f 2solid y 22SCFP ij 1 i j 2 ij i j 1 k ij (21) The solubility can be expressed as the solute mole fraction: (22) y2 where kij is a binary interaction parameter that is introduced to correct the segment-segment interactions of unlike chains. The density to a given system pressure, Psys, is determined iteratively by adjusting the reduced density of molecules, , until Pcalc = Psys. For a converged value of , the number density of molecules, ρ (Å-3), is calculated from: 6 N y i mi d i3 i 1 1 (23) Equation for the compressibility factor is derived from the relation: a 1 Z hc Z disp T ,x i Z 1 res (24) The pressure can be calculated in units of Pa by applying the relation: P ZkT 1010 A m 3 (25) The expression for the fugacity coefficient is given by: ln k kres (T ,v ) ln Z kT (26) The chemical potential can be obtained from: 452 (29) P2sub E P (30) where E is the enhancement factor defined as: v 2s 2sub exp E (P P sub ) RT 2SCF (31) where P is the equilibrium pressure, T is the equilibrium temperature, v 2s is the molar volume of the pure solid, 2sub is the fugacity coefficient of pure solid at its sublimation pressure, and 2SCF is the fugacity coefficient of pure solid in the supercritical phase. Physical properties The Pitzer acentric factor and the molar volume of solutes have been estimated by the Lee-Kesler correlation using PE software [35] and the Fedors method [36], respectively. Values of the required physical properties for all compounds using in the calculation and estimation methods are displayed in the Tables 1 and 2. PC-SAFT pure-component parameters PC-SAFT pure-component parameters for nabumetone have been estimated by the Tihic group contribution method. For the other compounds (phenylbutazone, salicylamide and statin drugs), it is shown that this method cannot be applied for missing functional groups (i.e., this method does not offer the values of contributions for all group-assignments of those compounds). The solution was the use of a A.A. EL HADJ et al.: APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE… CI&CEQ 19 (3) 449460 (2013) Table 1. Required physicals properties of anti-inflammatory drugs used Compound T ca / K Pca / bar w 3 –1 Vsb / cm mol Carbon dioxide 304.2 73.76 0.225 - 23.68 0.602 d 0.412 d 1.348 d 843.93 Nabumetone 984.71 Phenylbutazone Salicylamide 13.39 796.95 a 56.03 b Psub / barc 308.2 K 318.2 K - -7 195.8 1.46210 266.9 -10 79.9 9.210 5.83310 c 328.2 K - 4.58610 -7 1.31310 -6 3.48810 -9 1.35710 -8 6.21610 -7 -8 210 -7 d Estimated by Gani Method [10]; estimated by Fedors method [36]; estimated by Nannoolal method [11]; estimated by Lee-Kesler correlation [35] Table 2. Required physicals properties of statin drugs used Tc / K Compound Pc / bar Atorvastatine 1028.89 Lovastatine 901.80 a a c Rosuvastatine 1065.21 Simvastatine 878.52 a 921.70 a Fluvastatine 3 –1 Vs / cm mol Psub / bar 308 K 12.08 a 1.1616 368.9 2.0010 13.49 a 1.295 335.4 5.9010 c 0.7648 293.3 13.01 a 1.2803 350.7 15.40 a 18.92 a w 1.4726 288.1 b 318 K -16b 1.7310 -8b 1.7110 4.2410 -13b 1.1910 -11a 8.4110 -16b 328 K -15b 1.2910 -7b 4.6110 338 K -15b 8.3510 -7b 1.1610 2.3110 -12b 1.1110 6.5410 -11a 7.8310 -15b 4.7710 -6b 2.7410 -11b 4.8610 3.1210 -10a 1.3110 6.2110 -14b 4.2510 348 K -14b -13b -6b -11b -10b 1.9210 -9a 4.9410 -9a -13b 2.5510 -12 c Estimated by Nannoolal method [11]; estimated by Ambrose–Walton corresponding method [7]; estimated by Gani Method [10] linear correlation developed by Tihic et al. [37] for estimating phenylbutazone and salicylamide parameters. While for statin drugs, PC-SAFT-parameters were considered adjustable parameters and were fitted to solubility data (Table 3). This is because the Tihic’s linear correlations gave very large values for the segment number (m) and the segment diameter (σ), and small values for the segment energy parameter (ε/k) that lead to an overestimate of the solubility. Such a result is expected because the statin molecules are characterized by multiple functional groups (aromatic nitrogen, alcohol and acid functions, fluorine, sulfone, etc.) which makes it difficult to have a good representation with those correlations or the right classification into families that have been adopted by Tihic and his co-workers [37]. Table 3. PC-SAFT pure component parameters for all compounds used m σ/Å ε /k , K 2.07 2.78 169.21 Nabumetone 6.29 3.66 319.18 Phenylbutazone 6.86 4.14 312.05 Compound Carbon dioxide a Salicylamide 3.39 3.86 334.30 Atorvastatine 9.40 4.20 309.10 Lovastatine 5.60 4.10 233.10 Rosuvastatine 7.70 4.20 299.90 Simvastatine 6.40 4.17 299.60 Fluvastatine 8.90 4.19 342.00 a Pure component parameters for CO2 is taken from literature [27] RESULTS AND DISCUSSION In this work, the solubilities of three anti-inflammatory and five statin drugs in sc-CO2 were correlated. The experimental data were taken from literature [38,39]. The correlation was performed by minimizing the objective function, which is the absolute average relative deviation (AARD) usually defined as: OF AARD (%) 100 N n y calc y exp 1 y exp (32) The absolute average relative deviation (AARD ,%) values along with values of regressed binary interaction parameters for studied equations of state for CO2 + nabumetone, CO2 + phenylbutazone and CO2 + salicylamide are shown in Table 4 at various temperatures. This table shows that AARD values obtained with PR-VDW1 model varied from 4.7% at 308.2 K for the nabumetone-CO2 system to 34.3% at 328.2 K for the salicylamide-CO2 system, whereas with the PRVDW2 model the AARD values varied from 4.5 to 32.3% for the same binary system at the same temperatures, respectively. Also, the application of SRKVDW1 model gave deviations that range from 3.8% at 328.2 K for nabumetone-CO2 system to 32.2% found at 328.2 K for the salicylamide-CO2 system. Meanwhile, with SRK-VDW2 model the deviation varied from 3.4 to 32.1% for the same binary systems at the same temperatures, respectively. For PC-SAFT, the deviation varied between 1.4% obtained for nabumetone-CO2 system at 318.2 K to 22% found in correlating of salicylamide-CO2 system at 328.2 K. It is also 453 A.A. EL HADJ et al.: APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE… CI&CEQ 19 (3) 449460 (2013) Table 4. Correlation results for solubility of nabumetone, phenylbutazone and salicylamide in sc-CO2 with PR, SRK EoS’s using VDW1 and VDW2 and PC-SAFT with BR1 mixing rules at various temperatures T = 308.2 K Model PR-vdw1 PR-vdw2 SRK-vdw1 SRK-vdw2 PC-SAFT T = 318.2 K T = 328.2 K Parameter Nabumetone Phenylbutazone Salicylamide Nabumetone Phenylbutazone Salicylamide Nabumetone Phenylbutazone Salicylamide 0.1098 k12 0.1076 0.0154 0.1501 0.1017 0.0123 0.1331 0.095 0.0101 AARD / % 4.7 6.6 21.2 7.1 11.62 8.6 5.1 15.0 32.3 k12 0.1057 0.013 0.15 0.098 0.0068 0.13 3 0.101 -0.002 0.1095 -0.45 l12 -0.65 -0.50 -0.3868 -0.717 -0.70 -0.2911 0.81 -0.72 AARD / % 4.5 6.2 21.2 6.8 10.7 28.6 5.0 10.7 32.3 k12 0.1191 0.0269 0.0174 0.1124 0.0222 0.1559 0.1024 0.0188 0.1323 AARD / % 6.3 8.8 20.7 7.7 12.0 27.9 3.8 14.4 32.2 k12 0.1169 0.024 0.1738 0.11 0.0173 0.1558 0.11 0.11 0.1319 l12 -0.59 -0.54 -0.12 -0.47 -0.69 -0.70 0.80 -0.70 -0.67 AARD / % 6.1 8.5 20.7 7.6 11.3 27.9 3.4 13.1 32.1 k12 0.1123 0.0921 0.0048 0.095 0.0871 0.0996 0.083 0.0109 AARD / % 1.6 3.9 8.8 1.4 6.4 1.9 16.0 22.0 worth mentioning that the values of AARD increased with the increase of temperature. For example, AARD values obtained with PR-VDW1 for salicylamide-CO2 system at 308.2 K (21.2%) were higher for the same system at 328.2 K (32.3%). The correlation results for five statin drugs (Tables 5 and 6) confirm the superiority of PC-SAFT in predicting of the solubility compared to cubic equation of state. AARD values obtained with the PC-SAFT model ranged between 2.9 and 27.3%. However, very important deviations were observed by applying the cubic equations of state. For example, the values of AARD obtained with PR-VDW1 varied from 10.3% at 308 K for RV-CO2 system to 74.7% found at 328 K for LVCO2 system, whereas with SRK-VDW1 model the devi- -6.53.10 -4 14.9 ations ranged from 16.2 to 75% for the same binary system at the same temperatures, respectively. Fitting the experimental solubility data provided best-fit values to the binary interaction parameter k12 that is introduced to correct energetic interaction between the solute-SCF (it ranges between -0.0091 obtained in (FV + CO2) system with PR-VDW2 at 348 K to 0.437 obtained in (LV + CO2) system with SRKVDW2 model). However, high and negative values for interaction parameter, l12, were obtained, the highest one being for the (AV + CO2) system at 348 K with SRK-VDW2 model. Such results are not surprising since l12 is introduced in the bm parameter to correct the volumetric interaction between the solute and solvent. An analysis of the treated binary systems shows that they consist of small solvent molecules (molar Table 5. Correlation results for solubility of statin ( AV, LV and RV) in sc-CO2 with PR, SRK EoS’s using VDW1 and VDW2 and PCSAFT with BR1 mixingrules at various temperatures Model Parameter PRvdw1 k12 308 K AV PRvdw2 AARD / % SRKvdw2 454 AV LV RV AV LV 338 K RV AV LV 348 K RV AV LV RV 0.0537 0.353 0.1014 0.0418 0.3627 0.0975 0.03 0.3802 0.0932 0.0146 0.3977 0.0885 0.0017 0.4115 0.081 44.6 64.7 10.3 35.4 70.3 11.9 30.6 74.7 12.2 28.9 72.9 18.1 24.4 68.4 23.9 0.053 0.353 0.1016 0.0424 0.3628 0.098 0.031 0.3804 0.093 0.0269 0.3977 0.0882 0.0058 0.4115 0.0817 l12 -0.79 -0.493 -0.793 0.856 -0.85 0.97 0.9 -0.77 -0.545 0.88 44.7 70.1 12.0 29.9 74.7 27.5 k12 AARD / % k12 l12 AARD / % PCSAFT RV 328 K k12 AARD / % SRKvdw1 LV 318 K k12 AARD / % 64.6 10.3 35.3 12.2 -0.745 -0.63 72. 4 18.0 0.88 -0.788 0.88 22.5 68.3 23.6 0.0807 0.3861 0.1187 0.0774 0.395 0.1135 0.063 0.411 0.1079 0.0499 0.426 0.1006 0.029 0.4368 0.09 51.4 68.2 16.2 42.6 72.9 14.8 36.7 75.0 14.4 34.0 72.0 18.3 27.7 66.8 21.9 0.086 0.3864 0.1186 0.0757 0.395 0.1131 0.0625 0.4112 0.1076 0.045 0.426 0.1011 0.031 0.437 0.0911 -0.1574 -0.88 -0.778 0.852 51.4 68.3 16.2 42.7 -0.75 -0.80 0.89 -0.80 -0.796 0.88 -0.79 0.88 0.90 -0.79 -0.79 72.9 14.8 35.8 75.6 31.5 72.1 18.4 24.6 66.8 21.9 0.0377 0.0785 0.0558 0.0293 0.0784 0.055 11.6 4.9 9.0 9.4 4.1 8.5 14.4 0.02 0.3977 0.046 0.0113 0.085 0.0405 0.023 0.0878 0.0345 13.4 4.2 8.3 20.0 6.6 15.1 28.0 7.4 20.5 A.A. EL HADJ et al.: APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE… CI&CEQ 19 (3) 449460 (2013) Table 6: Correlation results for solubility of Statin (FV and SV) in sc-CO2 with PR, SRK EoS’s using VDW1 and VDW2 and PC-SAFT with BR1 mixing rules at various temperatures Model Parameter SV FV SV FV SV FV SV FV SV FV PR-vdw1 k12 AARD / % k12 0.1485 0.0355 0.1537 0.0263 0.1592 0.0165 0.165 0.006 0.1758 -0.0062 49.5 14.3 51.8 20.8 56.5 24.4 55.8 29.2 55.4 36.3 0.148 0.0357 0.1533 0.0263 0.1592 0.0157 0.1653 0.0044 0.1743 -0.0091 l12 -0.88 0.4553 -0.80 0.0978 0.0313 -0.769 0.894 -0.789 0.74 -0.875 49.2 14.3 51.7 20.8 56.5 24.3 55.7 28.7 55.4 34.7 0.1824 0.0745 0.1865 0.0645 0.1908 0.0518 0.1949 0.0408 0.1948 0.0274 PR-vdw2 AARD / % k12 SRK-vdw1 AARD / % k12 SRK-vdw2 PC-SAFT 308 K 318 K 328 K 338 K 348 K 56.5 15.5 57.9 20.0 60.4 23.7 56.2 28.0 56.9 33.8 0.1845 0.0746 0.1834 0.0643 0.1908 0.051 0.195 0.0404 0.1961 0.0247 l12 -0.80 0.1922 -0.79 -0.3895 0.238 -0.87 0.90 -0.228 0.89 -0.736 AARD / % k12 AARD / % 56.7 15.5 57.9 20.0 60.4 23.6 56.0 28.1 56.7 32.3 0.0526 0.0783 0.0529 0.0727 0.0508 0.0667 0.0485 0.06 0.0473 0.054 9.5 13.7 7.9 15.2 5.0 19.9 2.9 24.3 19.4 27.3 is usually close to zero (mole fraction, y2), and that of the solvent is usually on the order of 0.999. Consequently, the behaviour of solid-SCF is governed by the energetic interaction (due to the nature of atoms and liaisons formed the complex) more than the relative number of solute molecules in sc-CO2. 2. Some important deviations for both cubic equation of state and PC-SAFT models may be the result of either the formation of aggregates that need to be taken into account in the application of any model with more experimental studies about this phenomenon for correlating solubility, or the fluctuation of the density of solvent close to the critical region. Figures 2 and 3 show the solubility curves of nabumetone and phenylbutazone in sc-CO2. These include a comparison between experimental data and weight of carbon dioxide is 44 g/mol) and very large solute molecules (molar weight values vary between 137 for salicylamide to 540 g/mol for AV) providing highly asymmetric systems. In this case, large values of l12 are expected for well representing the complex forming as a result of the association of solute-solvent. Despite these large values, there is no remarkable influence on AARD values when the two-parameter mixing rule VDW2 was used instead of the oneparameter mixing rule VDW1. This can be explained by the following: 1. The binary interaction parameter, l12, is related to the volumetric interaction between supercritical fluid (CO2) and solid solute. Such correction has a small effect on the correlation of the solubility of solid in SCF since the concentration of solid in the solvent 0.0030 Solubility (mole fraction) 0.0025 0.0020 Experimental 308.2 K SRK 308.2 K PC-SAFT 308.2 K Experimental 318.2 K PR 318.2 K SRK 318.2 K PC-SAFT 318.2 K Experimental 328.2 K PC-SAFT 328.2 K 0.0015 0.0010 0.0005 0.0000 100 120 140 160 180 200 220 Pressure (bar) Figure 2. Experimental solubility in sc-CO2 of nabumetone and correlation results obtained by PC-SAFT and PR-VDW2 at various temperatures. 455 A.A. EL HADJ et al.: APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE… CI&CEQ 19 (3) 449460 (2013) 0.0030 Experimental 308.2 K PR 308.2 K PC-SAFT 308.2 K Experimental 318.2 K PR 318.2 K PC-SAFT 318.2 K Experimental 328.2 K PR 328.2 K PC-SAFT 328.2 K Solubility (mole fraction) 0.0025 0.0020 0.0015 0.0010 0.0005 0.0000 100 120 140 160 180 200 220 Pressure (bar) Figure 3. Experimental solubility in sc-CO2 of phenylbutazone and correlation results obtained by PC-SAFT and SRK-VDW2 at various temperatures. solubility predicted by PC-SAFT, PR and SRK equations. For the three experimental temperatures, the figures show an excellent agreement between experimental literature data (shown as circles, squares and upward-triangles), and the solubility estimated by PCSAFT more than those estimated by cubic-EOS (shown as solid and dashed lines, respectively). For the correlation results of lovastatin and rosuvastatin, it is clear from the graphical analysis considered in Figures 4 and 5 that the solubility predicted by PC-SAFT (shown as lines) follows the trend of the experimental data (shown as circles, triangles and squares), which suggests a good predictive ability of this equation at various temperatures. CONCLUSION In this work, PC-SAFT EOS were used with conventional combining rule to evaluate the capability of this approach for modeling the solubility of solid solutes in SCFs and the commonly used PR and SRK 0.00012 0.00011 0.00010 Slubility (mole fraction) 0.00009 0.00008 Experimental 308 K Experimental 328 K Experimental 348 K PC-SAFT 308 K PC-SAFT 328 K PC-SAFT 348 K 0.00007 0.00006 0.00005 0.00004 0.00003 0.00002 0.00001 0.00000 100 150 200 250 300 350 Pressure(bar) Figure 4. Experimental solubility in sc-CO2 of lovastatin and correlation results obtained by PC-SAFT. 456 A.A. EL HADJ et al.: APPLICATION OF PC-SAFT AND CUBIC EQUATIONS OF STATE… CI&CEQ 19 (3) 449460 (2013) 0.00026 0.00024 0.00022 slubility (mole fraction) 0.00020 0.00018 0.00016 Experimental 308 K Experimental 328 K Experimental 348 K PC-SAFT 308 K PC-SAFT 328 K PC-SAFT 348 K 0.00014 0.00012 0.00010 0.00008 0.00006 0.00004 0.00002 0.00000 -0.00002 100 150 200 250 300 350 (Pressure (bar) Figure 5. Experimental solubility in sc-CO2 of rosuvastatin and correlation results obtained by PC-SAFT. cubic equations of state along with VDW1 and VDW2 mixing rules for correlating the solubility of NSAIDs and statin drugs in supercritical carbon dioxide. The obtained results show that PC-SAFT has an advantage over cubic EOS and gives a good correlative accuracy than the cubic-EOS. Also, it should be mentioned that the use of the VDW2 (two binary interaction parameters, k ij and l ij ) mixing rule does not substantially improve the results of the modeling obtained with the VDW1 (one binary interaction parameter, k ij ) mixing rule for both the SRK and PR equations of state. The accurate values of physical properties are very important to the success of the correlation of solubility data using equation of state, mainly the sublimation pressure. One of the most critical factors that can influence the ability of estimation is the complexity of the molecules’ structure, including poly-functional groups and several cycles and aromatic cores. It can be the origin of an important deviation in its estimating as well as in the calculated solubility (case of statin drugs) as it has been confirmed in previous works [40]. Special attention was paid to the estimation of PC-SAFT pure component parameters for non-associating substances because of the non-availability and the complexity of structure. Tihic’s method used for estimating PC-SAFT parameters for nabumetone gave good correlation results of solubility in terms of relative deviations, AARD. The Tihic linear correlation for polyaromatic family used for calculating phenylbutazone and salicylamide gave accurate values and could describe well the PC-SAFT component parameters, as well as the solubility estimate, compared to those found using cubic-EOS. More complicated systems were treated (CO2 (1) + statins (2)) where the results obtained by PC-SAFT were obviously more accurate than cubic EOSs. The PC-SAFT pure component parameters were determined by fitting the solubility data, as it was done by Spyriouni et al. [41]. Despite the complexity of their structures, the nonavailability of parameters and the limitation of the available estimation techniques, this approach can represent the experimental data of solubility of solid drugs in supercritical fluid with more accuracy than the other models. Nomenclature AARD average absolute relative deviation a attractive term in PR and SRK-EOS ǎ Helmoltz free energy AV am, bm EOS FV atorvastatin EOS mixture parameter equation of State fluvastatin k Boltzmann constant, J/K kij binary interaction parameter lij binary interaction parameter LV lovastatin NC number of compounds NSAID non steroidal anti-inflammatory drug OF objective Function P pressure (bar) Pc critical pressure 457 A.A. 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LAIDI 1 Laboratoir de BioMatériaux et Phénomène de Transfert (LBMPT), Université de Médéa, Quartier Ain D’heb, Médéa, Algérie 2 Unité de Développement des Equipement Solaires, Tipaza, Algérie NAUČNI RAD CI&CEQ 19 (3) 449460 (2013) PRIMENA PC-SAFT I KUBNE JEDNAČINE STANJA ZA KOERELISANJE RASTVORLJIVOSTI NEKIH FARMACEUTSKIH I STATINSKIH AKTIVNIH SUPSTANCI U SUPEKRITIČNOM CO2 U ovom radu su rastvorljivosti nekih antiinflamatornih (nabumeton, phenilbutazon i salicilamid) i statinskih (fluvastatin, atorvastatin, lovastatin, simvastatin I rosuvastatin) aktivnih supstanci korelisani PC-SAFT (sa jednoparametarskim pravilom mešanja) i uobičajenim kubnim jednačinama Peng-Robinson-a (PR) i Soave-Redlich-Kwong-a (SRK) kombinovanim sa van-der Waals-ovim jedno- i dvo-parametarskim pravilima mešanja (VDW1 i VDW2). Eksperimentalni podaci za ispitivana jedinjenja u opsegu temperature 308-348 K i pritiska 100-360 bar su uzeti iz literature. Kritična svojstva potrebna za korelisanje pomoću PR i SRK jednačina su izračunate Gani-Noonalol-ovom metodom doprinosa grupa, dok su u slučaju nabumetona parametri PC-SAFT jednačine za čiste komponente (segmentni broj, segmentni prečnik i energetski parameter, ε/k) izračunati metodom doprinosa grupa. U slučaju fenilbutazona i salicilamida, ovi parametri su određeni linearnom korelacijom. PC-SAFT parameteri statinskih jedinjenja su određeni iz podataka za rastvorljivost, a parametri binarne interakcije su dobijeni fitovanjem eksperimentalnih podataka. Dobijeni rezultat je bio u saglasnosti sa eksperimentalnim podacima. Pokazano je da se PC-SAFT jednačina može upotrebiti za modelovanje ravnoteže čvrsto-superkritični fluid boljom korelacionom tačnošću od kubnih jednačina stanja. Ključne reči: rastvorljivost čvrstih jedinjenja, kubna jednačina stanja, PC-SAFT, antiinflamatoran, supekritičan CO2, korelacija. 460