Microsoft Word - 476hernandez.docx CHEMICAL ENGINEERING TRANSACTIONS VOL. 43, 2015 A publication of The Italian Association of Chemical Engineering Online at www.aidic.it/cet Chief Editors: Sauro Pierucci, Jiří J. Klemeš Copyright © 2015, AIDIC Servizi S.r.l., ISBN 978-88-95608-34-1; ISSN 2283-9216 Adsorption of FFA, Soap and Glycerine in Biodiesel Using Magnesium Silicate Pornsawan Assawasaengrat*, Pornrin Jintanavasan and Prakob Kitchaiya Department of Chemical Engineering, Faculty of Engineering, King Mongkut's Institute of Technology Ladkrabang, Bangkok 10520, Thailand pornsawank@hotmail.com The effect of SiO2/MgO molar ratios of magnesium silicate on adsorption of free fatty acid (FFA), soap and glycerine in biodiesel was studied. The magnesium silicate adsorbent was prepared by the precipitation of magnesium sulfate and sodium metasilicate. The molar ratios of SiO2/MgO in synthetic magnesium silicate,i.e.,0.31:1, 0.76:1 and 2.04:1 were obtained by varying concentrations of Na2SiO3:MgSO4. The element analysis, crystal structures and surface area and pore size of the adsorbents were characterized by X-ray fluorescence method (XRF), X-ray diffraction method (XRD) and Brunauer-Emmett-Teller technique (BET), respectively. FTIR technique was used to confirm the chemical characteristics of the adsorbents. The adsorption efficiency of synthesized magnesium silicate in biodiesel containing different amount of SiO2 / MgO molar ratios was studied by varying dosage amount of adsorbents (1, 2 and 3 g) for 150 g of biodiesel at 60˚C for 5 hours. The results showed that the magnesium silicate at 2.04:1 SiO2/MgO molar ratio and 3 g of adsorbent showed the highest efficiency in adsorption of FFA, soap and glycerine at 77.39%, 77.11% and 82.92%, respectively. While the adsorption capacity was 52.57 mg/g of FFA adsorption, 1.37 mg/g of soap adsorption and 155.06 mg/g of glycerine adsorption. The 2.04:1 molar ratio of SiO2/MgO in magnesium silicate had the biggest pore size, 105 A°, that was proportional to the contaminates adsorbed. Noticeably, the structure size of concerned contaminates were large, so the pore size of adsorbents could play a significant role on adsorptivity of adsorbate. 1. Introduction Nowadays, the demand of energy and environmental concerns about air pollution from gas cars are steadily increasing. Biodiesel is an alternative and renewable fuel (Ceclan et al, 2012). It presents outstanding characteristics as non-toxicity, absence of sulphur, high energy content and biodegradability. Transesterification is a chemical reaction relating triglycerides and alcohol using homogeneous or heterogeneous substances as catalyst to yield alkyl esters (biodiesel) and glycerol as by-product. The methyl ester has contaminants frequently that have effects on the quality of biodiesel. Glycerol is a potential cause of biodiesel instability. During transesterification, reaction conditions could result in the formation of oxidizes byproducts that cause discoloration, especially when glycerol is exposed to either high temperature or alkaline pH. Glycerol can oxidize or thermally degrade to form diols or acids that can contribute to biodiesel instability. (Sangita and Pradeep, 2010).The water content in biodiesel causes corrosion of the automobile system (such as fuel tubes and injector) or might react with glycerides to form soap and glycerine as by-products (Predojevic, 2008). In addition, soap and free fatty acids cause the deterioration of engine components. Therefore, the amount of water and free fatty acids affect the quality of biodiesel. Conventionally wet washing is the most employed technique to remove contaminants such as soap, catalyst, glycerine and residual alcohol from biodiesel. However, the major disadvantages in the use of water to purify biodiesel are emulsion formation (preventing the separation of the esters), formation of free fatty acids and soap, wastewater formation; which all increase in cost and production time (Ignat and Kiss, 2012). Adsorption technique was introduced to substitute wet washing to remove biodiesel contaminants. The use of adsorbents turns the process more rapid and there is not a formation of aqueous residues. The adsorbent such as magnesium DOI: 10.3303/CET1543190 Please cite this article as: Assawasaengrat P., Jintanavasan P., Kitchaiya P., 2015, Adsorption of ffa, soap and glycerin in biodiesel using magnesium silicate, Chemical Engineering Transactions, 43, 1135-1140 DOI: 10.3303/CET1543190 1135 silicate has the potential of selectively adsorbing hydrophilic materials such as glycerine, mono- and diglycerides. Magnesium silicate surface consists of partially hydrophobic and partially hydrophilic sites. The hydrophobic part includes siloxane (≡Si−O−Si≡) groups and the hydrophilic portion contains isolated hydroxy groups (−Mg−OH), individual silanol groups (≡Si−OH) and hydrogen bonds formed due to close vicinity of hydroxy groups linked to neighboring silicon atoms. In this paper, the adsorption of free fatty acid, soap, and total glycerine in biodiesel was studied by using magnesium silicate as an adsorbent 2. Experimental 2.1 Synthesis of magnesium silicate Three different concentration ratios of sodium silicate and magnesium sulphate (VI) were chosen for magnesium silicate synthesis. The concentration (Molar) ratios of Na2SiO4: MgSO4 were 0.5:0.5, 0.5:1.5 and 3.0: 0.5. The sodium silicate was dropped into the magnesium sulphate (VI) solution with stirring speed of 200 rpm at room temperature. Centrifugation at 2000 rpm was used to separate the precipitate and the liquid phase was removed by filtration. The precipitate was dried at 100°C for 24 h, then mashed and sieved. 2.2 Characterization of magnesium silicate Chemical characterization of representative sample was undertaken by X-ray fluorescence spectrophotometer (XRFs) for major element detection. Analysis by X-ray diffractometer (XRD) revealed major crystalline phases in magnesium silicate samples. Structural characterization of the sample was investigated by Fourier transform infrared spectrometer (FT-IR). In order to determine magnesium silicate adsorptive potentials, their BET specific surface area and pore diameter were estimated using multipoint BET surface area, and meso pore volumes was determined by using BJH equation. 2.3 Adsorption capacity of synthetic magnesium silicate 1, 2 or 3 grams of adsorbent was added into 150 g of biodiesel (palm oil) to study the contaminates adsorption. The shaker machine (ZHWY-100B, ZHICHENG) was set at 60°C, 200 rpm and 2 h. After shaking, the adsorbent was removed and purified biodiesel was analysed for the contaminations. In order to determine the effectiveness of purification, the soap, free fatty acid, and total glycerine contents were measured before and after processing. The amount of remaining free fatty acid was determined by acid value titration according to AOCS Official Methods Cd 3a-63. Soap level was determined using AOCS Method Cc 17‐79. The amount of total glycerine was determined according to EN14105. Adsorption efficiency was defined as percentage of fraction between adsorbed and initial contaminate. 3. Results and discussion 3.1 Adsorption synthesis and characterization The synthesized magnesium silicate was a fine white powder. The chemical composition of the synthesized magnesium silicates was analysed by X-ray fluorescence (XRF). Table 1 exhibited the chemical compositions of magnesium silicate which were synthesized by varying Na2SiO4: MgSO4 concentration ratios. The molar ratio of SiO2: MgO in synthetic magnesium silicate was 0.36:1, 0.76:1 and 2.04:1 according to the Na2SiO4: MgSO4 concentration ratio of 0.5:1.5, 0.5:0.5 and 3.0:0.5, respectively. Na2SiO4: MgSO4 concentration ratio of 3.0:0.5 exhibited highest molar ratio of SiO2: MgO, while the concentration ratio of 0.5:1.5 showed lowest molar ratio of SiO2: MgO. Thus, the molar ratio of synthetic magnesium silicate was in agreement with the used concentration ratio. Table 1: Chemical compositions of magnesium silicate by various Na2SiO4: MgSO4 concentration ratios Concentration(Molar) ratios Na2SiO4: MgSO4 SiO2 (wt%) MgO (wt%) Other (wt%) Molar ratio of SiO2: MgO 0.5:1.5 26.34 72.31 1.35 0.36:1 0.5:0.5 3.0:0.5 43.18 52.88 56.81 25.85 0.01 21.27 0.76:1 2.04:1 The average surface area, pore volume and pore size of magnesium silicate were characterized by BET method. The result is showed in the Table 2. The magnesium silicate has surface area between 15 58 m2/g and average pore size is between 50-105 A° which could described that synthesized magnesium silicate was mesoporous. Higher SiO2: MgO molar ratio provided larger pore size. From the results, the 2.04:1 molar ratio of SiO2: MgO has the biggest pore size diameter, 105 A °. 1136 Table 2: Chemical compositions of magnesium silicate by various Na2SiO4: MgSO4 concentration ratios Molar ratio of SiO2: MgO Surface area (m2/g) Pore volume (cm3/g) Pore size diameter (A°) 0.36:1 15.1 0.0192 50.9 0.76:1 2.04:1 67.2 57.8 0.1098 0.1516 65.3 105.0 Crystalline structure of magnesium silicate was characterized by X-ray diffraction technique. XRD patterns of magnesium silicate were demonstrated in Figure 1. The structure of the synthesized magnesium silicate was amorphous as there were no sharp peaks appearing at any 2θ. The XRD patterns of the samples were in an agreement with commercial magnesium silicate (Clowutimon et al., 2011). Figure 1: The XRD pattern of magnesium silicate with molar ratio of SiO2: MgO at (A) 0.36:1, (B) 0.76:1, (C) 2.04:1 1137 The FT-IR spectra of magnesium silicate with different molar ratio of SiO2:MgO are shown in Figure 2. Normally, the strong band between 1,100 - 900 cm-1 represented the characteristics of siloxane (Si-O-Si) groups (Battisha et al., 2007) and the band around 600 cm-1 due to Si-O-Si bending vibration (Mostafa et al., 2009).The synthesized adsorbent showed strongest absorption band at 1,025, 987 and 968 cm-1 according to Si-O-Si asymmetric stretching. At the right hand side of this band, there is a small shoulder, assigned to the Si-O stretching (Silva et al., 2011). The broad band between 3,800-3050 cm-1 assigned to the O-H stretching (Karbowiak et al., 2010) did not appeared in the adsorbent. The bending vibration band of molecular H2O appears at 1,632 cm-1 (Mostafa et al., 2009). The band at 1,400 cm-1 was related to the presence of Si-O-Na and Mg-O-Na (Narasimharao et al., 2014). The band at 400 - 450 cm-1 is attributed to Mg-O stretching vibration (Brew and Glasser, 2005). It was found that all magnesium silicate have a similar chemical nature. Nevertheless, only for magnesium silicate at 2.04:1 SiO2/MgO molar ratio was a peak detected at 1432 cm -1 that represent Si-O-Na and Mg-O-Na bonding. Figure 2: FT-IR spectra of magnesium silicate with the molar ratio of SiO2: MgO at (A) 0.36:1, (B) 0.76:1, (C) 2.04:1 1138 3.2 Adsorbent Efficiency Adsorption of free fatty acid, soap and total glycerine in biodiesel by synthesized magnesium silicate, which different molar ratio of SiO2/MgO were investigated and shown in Figure 3. Figure 3: Comparison of adsorption efficiency of contaminates from different molecular ratios of SiO2/MgO; (A) free fatty acid, (B) soap, and (C) total glycerine From the results, dosage amount of adsorbent had direct variation with efficiency of contaminates adsorption and trends of free fatty acid, soap and total glycerine adsorption. Magnesium silicate at 2.04:1 SiO2/MgO molar ratio and 3 g of adsorbent showed the highest efficiency in adsorption of FFA, soap and glycerine at 77.39 %, 77.11 % and 82.92 %. In addition the adsorption capacity was 52.57 mg/g of FFA adsorption, 1.37 mg/g of soap adsorption and 155.06 mg/g of glycerine adsorption. Magnesol, a commercial adsorbent for biodiesel purification, was reported to adsorb FFA 90 mg/g of adsorbent and soap 0.75 mg/g of adsorbent (Jintanavasan and Assawasaengrat, 2012). On the other hand the trends of magnesium silicate, 0.36:1 molecular ratio of SiO2/MgO, present low adsorbed efficiency of free fatty acid and soap (Figure 3A, 3B). This is because 2.04:1 molecular ratios of SiO2/MgO of magnesium silicate had high silica content than other concentration ratios of magnesium silicate which related to XRF result. It means that silica content in magnesium silicate effect on efficiency of free fatty acid and soap adsorption. However, the adsorption of glycerine was not affected by different molar ratios of SiO2/MgO as shown in Figure 3C. Physically, BET results presented the largest pore size, 105 A°, at 2.04:1 SiO2/MgO molecular ratio of magnesium silicate which influenced the adsorption efficiency. Free fatty acid and soap have larger molecular size than glycerine (Oleic acid and glycerine molecular size were estimated to be 28 A° (Eva et al., 2008) and 3.6 A° (Chen, 2013), respectively. Therefore, larger pore size can enhance diffusion of large molecules into the adsorbents. 1139 4. Conclusions The magnesium silicate adsorbent was prepared by the precipitation of magnesium sulphate and sodium metasilicate. The molar ratios of SiO2/MgO in synthetic magnesium silicate (0.31:1, 0.76:1 and 2.04:1) were obtained by varying concentrations of Na2SiO3:MgSO4. The adsorption efficiency of synthesized magnesium silicate in biodiesel containing different amount of SiO2/MgO molar ratios was studied by varying dosage amount of adsorbents (1, 2 and 3 g) for 150 g of biodiesel at 60˚C for 5 h. The magnesium silicate at 2.04:1 SiO2/MgO molar ratio and 3 g of adsorbent showed the highest efficiency in adsorption of FFA, soap and glycerine at 77.39 %, 77.11 % and 82.92 %. The adsorption capacity was 52.57 mg/g of FFA adsorption, 1.37 mg/g of soap adsorption and 155.06 mg/g of glycerine adsorption. The adsorption efficiency of free fatty acid and soap was increased when silica content in magnesium silicate increased. However, the adsorption of glycerine was not affected by different molar ratios of SiO2/MgO. BET results presented the largest pore size at 2.04:1 SiO2/MgO molecular ratio of magnesium silicate which influenced the adsorption efficiency. Free fatty acid and soap have larger molecular size than glycerine. Therefore, larger pore size can enhance diffusion of large molecules into the adsorbents. Acknowledgements This research was financially supported by Faculty of Engineering, King Mongkut's Institute of Technology Ladkrabang and National Research Council of Thailand. Support from the Center of Advanced Instrument for Research in Engineering is also acknowledged. References Battisha I.K., Beyally A.E., Mongy S.A.E., Nahrawi A.M., 2007, Developmentof the FTIR properties of nano- structure silica gel doped with different rare earth elements prepared by sol–gel route, J. Sol–Gel Sci. Technol., 41, 129–137. Brew D.R.M., Glasser F.P., 2005, Synthesis and characterisation of magnesium silicate hydrate gels, Cement and Concrete Research, 35, 85-98. Ceclan R.E., Pop A., Ceclan M., 2012, Biodiesel from Waste Vegetable Oils, Chemical Engineering Transactions, 29, 1177-1182. Chen L.Y., 2013, Glycerol inhibits water permeation through Plasmodium falciparum aquaglyceroporin, J. Struct. Biol., 181, 71-76. Clowutimon W., KItchaiya P., Assawasaengrat P., 2011, Adsorption of Free Fatty Acid from Crude Palm Oil on Magnesium Silicate Derived From Rice Husk, Engineering Journal, 15, 15-26. Eva R.G., Elias P.R., Laura I.C., Tomas B., 2008, Structure of submonolayer oleic acid coverages on inorganic aerosol particles: evidence of island formation, Phys. Chem. Chem. Phys., 10, 3156-3161. Ignat R.M., Kiss A.A., 2012, Energy efficient recovery of methanol and glycerol in biodiesel production, Chemical Engineering Transactions, 29, 1141-1146. Jintanavasan P., Assawasaengrat P., 2012, Synthesis of magnesium silicate as adsorbent in biodiesel, International Conference on Engineering, Applied Sciences and Technology, 531-534.Karbowiak T., Saada M.A., Rigolet S., allandras A., Weber G., Bezverkhyy I., Soulard M., Patarin J., Bellat J.P., 2010, New insight in the formation of silanol defects in silicalite-1 by water intrusion under high pressure, Phys. Chem. Chem. Phys., 12, 11454-11466. Mostafa N.Y., Kishar E.A., Abo-El-Enein S.A., 2009, FTIR study and cation exchange capacity of Fe 3+ and Mg2+ substituted calcium silicate hydrates, Journal of Alloys and Compounds, 473, 538-542 Narasimharao K., Tarek T.A., Bawaked S., Basahel S., 2014, Effect of Si precursor on structural and catalytic properties of nanosize magnesium silicates, Applied Catalysis A: General, 488, 208–218. Predojevic Z.J., 2008, The production of biodiesel from waste frying oils: A comparison of different purification steps, Fuel, 87, 3522-3528. Sangita B., Pradeep K.V., 2010, Effect of impurities on performance of biodiesel, Journal of Scientific & Industrial Research, 69, 575-579. Silva A.M.B., Queiroz C.M., Agathopoulos S., Corriea R.N., Fernandes M.H.V., Oliveira J.M., 2011, Structure of SiO2-MgO-Na2O glasses by FTIR, Raman and 29Si MAS NMR, Journal of Molecular Structure, 986, 16- 21. 1140