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Barbara WALAWSKA – Inorganic Chemistry Division „IChN” in Gliwice of Fertilizers Research Institute, Gliwice; Arkadiusz SZYMANEK, Anna PAJDAK – Institute of Advanced Energy Technologies, Czestochowa University of Technology, Czestochowa; Marzena NOWAK, Bożena HALA – Inorganic Chemistry Division „IChN” in Gliwice of Fertilizers Research Institute, Gliwice Please cite as: CHEMIK 2012, 66, 11, 1169-1176 Introduction From the point of view of different technological processes, the knowledge of parameters describing the structure of sorbents, such as surface area or pore size distribution play an important role for application them in chemical, cement industries, or modification of mineral raw materials. The sorption properties are determined by surface area, what binds with surface energy and reactivity [1]. As it is well known, sorbents usually characterize in surface heterogeneity. That characteristic is due to the presence of varying sizes and shapes [2]. In general, the grains of fine-grained materials are of irregular shape, exhibiting a columnar, table, needle-shaped or lamellar morphology. Less often they can be found in the form of spherical bodies [1]. There is a close relationship between the type of pores prevailing in the sorbent and its surface. In accordance with the IUPAC (International Union of Pure and Applied Chemistry) recommendation, the surface area of sorbent can be calculated from the capacity of monolayer, which covers the pores, assuming, that surface area effectively occupied by particles of adsorbent in total monolayer is known [3]. Total surface area relates to the unit mass of the adsorbate. In accordance with th same reccomendations, pores, from the point of view of their linear dimensions, are classified into micropores (with a diameter below 2 nm), mesopores (with a diameter from 2 to 50 nm) and macropores (with a diameter above 50 nm). Macroporous materials are characterized by a poorly developed surface area from a few to several m2/g, mesoporous materials – several hundred m2/g, and microporous materials – up to several thousand m2/g. Sodium bicarbonate is a sorbent that is increasingly widely used in purification processes of gaseous products from combustion of solid fuels. In the seventies of the 20th century, studies on sodium sorbents were conducted. They included the use of nahcolite (natural sodium bicarbonate) in the dry flue gas desulphurization process [4]. Nahcolite changes its microstructure as a result of decomposition at elevated temperatures, forming an inhomogeneous structure, that is very reactive in contact with acid gases. Similar properties are possessed by synthetic sodium bicarbonate. As a result of its thermal activation, the decomposition of sodium bicarbonate to sodium carbonate occurs. It influence on decreasing of molar volume of decomposed sodium bicarbonate (NaHCO3) during releasing of gasous products of decomposition: carbon dioxide and water vapor, resulting in breaking apart of compact structure and forming of pores with high surface area. In respect to different sources of informations, the temperature of decomposions varies in the range of 60 to 400˚C [5]. Sodium carbonate produced in that proces is characterized by a more developed surface area in comparison with crystalline sodium bicarbonate. This translates into an increase in its reactivity. The process follows the reaction below [6]: 2NaHCO3→Na2CO3+CO2+H2O (1) The reactivity of sodium bicarbonate depends chiefly on its grain size and structure [7, 8, 9]. As fine grains react more efficiently, than larger grains, the examined material was subjected to grinding and then thermal activation in order to develop its surface area. In the nr 11/2012 • tom 66 present study, the surface area and pore size distribution in modified sodium bicarbonate was determined, using modern methods for obtaining the surface topography and structure. The knowledge of these parameters and their correct interpretation enable the proper selection and use of sodium bicarbonate for the dry flue gas desulphurization process. The presented study on the determination of the sorption properties of modified sodium sorbent has been carried out within the development of project nr NR05000910 “Modified sodium bicarbonate in the processes of dry purification of flue gases from various types of industrial installations”. Experimental Materials For the examination of the sorption properties of sodium bicarbonate, baking soda manufactured by Soda Polska Ciech SA, with characteristics shown in Table 1, was used. Table 1 Characteristics of sodium bicarbonate Parameter Value Content. %: NaHCO3 humidity (50oC) 99.9 0.04 Granulation. µm: < 50 50-100 100-150 150-200 200-250 250-300 200-350 13.9 24.8 25.5 20.0 11.7 3.8 0.3 Average grain. µm 126.0 Bases on the baking soda, four samples were prepared from the initial material and its mixtures with magnesium stearate, respectively. A small amount of magnesium stearate (below 0.5 %) facilitated the process of grinding, without the influence on further thermal modification. Analytical methods and apparatus Sodium bicarbonate, as a crystalline product, is characterized by a poorly developed porous structure. The purpose of the mechanical activation was to mill it and increase its active surface area. A mixture of baking soda with magnesium stearate prepared in an Eirich mixer was ground in a 160 UPZ impact mill at a rotor rotational speed of 11400 rpm and a material batching rate of 60 kg/h. Samples with the mean size – 13.17 μm were obtained. • 1173 XIII Conference Environmental Sorption properties of sodium bicarbonate XIII Conference Environmental The grain size measurement of the test samples, before and after milling, was made on a Beckman analyzer confirming to the ISO requirements for grain size determination by the laser diffraction method [10]. The examination of grain size composition was made, using a wet measuring module. Sodium bicarbonate, without and after mechanical activation, was subjected to thermal activation successively in the range of temperatures from 100°C to 400°C in a Nabetherm laboratory furnace for a duration of 30 minutes. The surface areas of the samples after thermal activation were obtained by experimental determinations of the low-temperature nitrogen adsorption isotherms. The adsorption data were obtained by the Brunauer, Emmet and Teller methods using a Gemini VII 2390 analyzer of surface area. The analyzer measures the volume of gas adsorbed at the temperature of -196°C in the relative pressure range of 0.03 – 0.5. The BET surface analysis enabled the determination of the micro and mesopores of analysed sorbents. The surface area of chosen samples of sorbents activated thermally at temperatures: 100 and 250˚C (Tab.2.) was measured. A method used for determination the parameters of the porous structure for macropores was the porosimetric analysis. An Auto Pore IV 9500 (Automated Mercury Porosimeters) was employed for this analysis. The device serves also for determination, among others, the total pore area, pore size distribution, percentage porosity, density, and the transfer properties of pores. Based on the BET and porosimetric analyses, the surface areas of the samples, i.e. the magnitude of the external surface (considering the surface area of the solid body and open pores, not taking into account closed pores) per unit material mass, m2/g, were determined. Also the distribution of pore volume as a function of pore size was established. It allowed the classification of the material to be made in accordance with the IUPAC recommendation. The structure of the sorbent was also analized, using a Scanning Microscope Philips XI 30 ESEM with analizer EDS Edax (SEM). A device was designed for examining the surface morphology of solid bodies on a micro- and nano-scale. It makes it possible to represent the surface of the examined samples and determine the mean length and width of pores in the samples. From each sample, a test preparation was made and then sputter coated with gold. Using an SE (Secondary Electron) detector, images were recorded at a zoom from 1000 to 20000x. EDS X-ray microanalyses were made at selected points on the samples. The examinations were carried out in a high-vacuum mode at a voltage of 15 kV. To assess the sorption properties of sorbents, the test of reactivity was performed. The testing method involved a cycle of tests used for determination the reactivity indexes (Ri) and absolute sorption (Ci). The indices were detected from the Ahlstrom test. The reactivity test was carried out by desulphuring the flue gas in the model conditions. It contained sulfur dioxide (SO2 – 5091 mg/m3), oxygen (O2 – 3 %), carbon dioxide (CO2 – 16 %) and nitrogen, keeping constant temperature in the reaction chamber. At the outlet of the reaction chamber the concentractions of individual gases were measured, using exhaust gases analyzer – Mahiak. After completion of the reactivity tests, the chemical composition of the flue gas desulfurization products were determined. Using the analyzer LECO SC-144, the amount of sulfur and carbon was obtained. Using standard chemical methods, the percentage of active compounds was measured. Investigation results The sorptive properties of sorbents in the processes of dry purification of flue gases are determined mainly by their surface area. Both, the mechanical (grinding) and thermal (temperature above 150 ˚C) activations are significant in increasing the surface area of 1174 • sodium bicarbonate. To determine the influence of these activations, surface areas of sorbents after mechanical and thermal activation in the range of temperatures: 100 – 400 ˚C were compared (Fig. 1). Fig. 1. Effect of mechanical and thermal activation of the surface area (BET) of sodium sorbent. The thermal activation has an significant influence on the surface area of analyzed sorbents, much less influence has mechanical activation. At the temperature range: 20 – 100 ˚C, a small surface area of sorbents is the result of the lack or not complete decomposition of the sodium bicarbonate. The significant increment of surface area occurs at the temperature range: 100 – 150˚C, touching the maximum values at the temperature range: 200 – 25˚C. Noted differences in surface area are related with occuring of pores created during thermal activation. At the temperature range: 250 – 300˚C decreasing in surface area is noticed, the results achieved at 400˚C are similar to the values obtained at the beginning range of the activation temperatures. It can be probably related with softening process and closing of opened pores after treating the sorbent with high temperatures. The obtained surface area values of analyzed sorbents after thermal activation suggests, that most wide pores occur in their structure. The surface area of sorbents, reaching a few m2/g proves their macroporous character. To confirm that statement, the structural analysis, using a scanning microscope, was analized. Four samples of sorbents, differing in surface area, obtained in the result of their activation (according to Tab. 2.), were estimated. Table 2 Samples NaHCO3 used for the test Mechanical Thermal activation activation Sample Type of sample P1 NaHCO3 none none P2 mixture of NaHCO3 with magnesium stearate grinding none P3 mixture of NaHCO3 with magnesium stearate grinding 100°C by time 0.5 h P4 mixture of NaHCO3 with magnesium stearate grinding 250°C by time 0.5 h In order to establish the surface structure of sodium bicarbonate, the porous structure parameters, such as the surface area and the volume pore distribution function, were determined. The investigations were carried out experimentally by the BET nitrogen adsorption method (that determines micro- and mesopores) and by the mercury porosimetry method (that determines macropores). The obtained surface area values are summarized in Figure 1. Sodium bicarbonate not activated thermally (P1, P2) has a very poorly developed surface nr 11/2012 • tom 66 at 100°C did not cause well developed pores to form on all the grain surfaces. It is most likely that the transformation of NaHCO3 to Na2CO3 occurred here partially and only on some grain surfaces. Very numerous lamellar and columnar crystals of a size of several micrometers formed on the sample grain surface. The volume pore size distribution function determined by the mercury porosimetry method, confirmed these observation (Fig.3.). The area under the curves in the diagrams yields here the volume of open pores. The impact and thermal modification at 100°C (P3) resulted in the opening of pores with diameters of 70-160 nm, derived from the activation of shallow pore spaces with undifferentiated shapes. The pores formed were distinguished by a narrow range of sizes and quite a small volume. After heating up to 250°C (P4), crystals occuring on the surface of sorbent, disappeared, whereas the pores developed slightly better and almost completely covered nearly all surfaces of grains. Additionally pores with diameters of 160-200 nm occured. The pores were characterized by a narrow pore size range and a large volume, which indicates the opening of deep porous spaces with a well developed structure. Fig.2. Surface area of sodium bicarbonate determined by the BET method and mercury porosimetry method Fig. 3. The pore volume distribution of sodium bicarbonate determined by the mercury porosimetry method The EDS spectrum recorded at the point situated on a smooth grain’s surface of the sample (P3) not covered with pores is the spectrum of NaHCO3 (Fig.4). Also the composition of the lamellar and columnar crystals corresponds to NaHCO3. In contrast, the EDS spectrum from the grain’s surface of sample (P4) with well developed pores corresponds to the spectrum of Na2CO3 (Fig.5). Photo 1. Comparison of surface area of unmodified and modified sodium bicarbonate – magnification 10 000x The structural analysis using a scanning microscope (Photo 1) showed that the grains of the samples not subjected to thermal treatment had a relatively smooth surface and do not exhibit porosity, characterizing in compact crystalline surface, free from pores and cracks. It can be proved by obtained values of surface area. In the sample subjected to grinding, thermal activation nr 11/2012 • tom 66 Fig.4. EDS spectrum of NaHCO3 from the point on a smooth surface of the grain (100°C) • 1175 XIII Conference Environmental area, which is indicative of poor sorption properties of the material in that form. Activation at the temperature of 100°C (P3) resulted in developing the surface area values by 10 times (up to approx. 2-3 m2/g). At the temperature of 250°C (P4), a further increase in surface area was observed up to approx. 7-9 m2/g. Figure 2 illustrates the dynamics of development of the sodium bicarbonate sample surface area values, as determined by the BET method and the mercury porosimetry method, respectively. XIII Conference Environmental Literature Fig.5. EDS spectrum of Na2CO3 from the surface of the well-developed pore (250°C) The last stage of assessment of the sorption properties of sodium products provided for carrying the reactivity tests, which were performed on the laboratory scale. The reactivity index (Ri) and the absolute sorption index (Ci) were determined. For the assessment of reactivity, the Alhstrom scale was used (Tab.3). The test results are given in Table 4. Taking into account the obtained results, both – the modified and unmodified sodium bicarbonate were classified as exquisite sorbents. Table 3 Alhstrom’s reactivity scale Rating sorbent Ri, mol/mol Ci, g/kg excellent < 2.5 > 120 very good 2.5 – 3.0 100 -120 good 3.0 – 4.0 80 - 100 sufficient 4.0 – 5.0 60 - 80 low quality > 5.0 < 60 1. Radomski P., Jarosiński A.: Wyznaczanie powierzchni właściwej materiałów ziarnistych w aspekcie stosowania jej wielkości w wybranych procesach technologicznych. Czasopismo Techniczne, Kraków 2010, 10, 268-276. 2. Choma J., Jaroniec M.: Nowe metody opisu struktury porowatej węgli aktywnych na podstawie danych adsorpcyjnych. Ochrona Środowiska 1999, 3, (74), 12-17. 3. Sing K. S. W., Everrett D. H., Haul R. A. W., Moscou L., Pierotti R A., Rouquerol J., Siezieniewska T.: Reporting phisisorption data for gas/solid systems with special reference to the determination of surface area and porosity. Pure Apel. Chem. 1985, 57, 603-619. 4. Howatson J., Smith J.W., Outka D.A., Dewald H.D.: Mat. 5th National Conf. on Energy and the Environment, American Institute of Chemical Engineers, Dayton (OH), 1977. 5. Fellows K.T., Pilat M.J.: HCl sorption by dry NaHCO3 for incinerator emissions control. Air & Waste Management Association 1990, 40, 6, 887‒893. 6. Kilgallon P., Mat. CIWM 2007, Waste. A global resource, Paignton (Wielka Brytania),12 –15 czerwca 2007 r., pobrano 20 lutego 2012 r. z http://www. carbonbaseddesign.co.uk/ciwm/. 7. Szymańska Czaja M.: Powierzchnia właściwa materiałów drobnouziarnionych funkcją współczynnika kształtu i wielkości ziarna. Prace Naukowe Instytutu Górnictwa Politechniki Wrocławskiej, 25, Konferencje 2000, Nr 88. 8. Keener T. C., Davis W. T.: Study of the reaction of SO2 with NaHCO3 and Na2CO3.JAPCA 1984, 34, 651 – 654. 9. Heda P. K., Dollimore D., Alexander Dun Chen K. S., Law E., Bicknell P.: A metod of assesing solid state reactivity illustrated by thermal decomposition experiments on sodium bicarbonate. Thermochimica Acta 1999, 255, 255 – 272. 10. ISO/DIN13320-1 Particle size analysis. Laser scattering methods, Part 1, General principles. Translation into English by the Author Barbara WALAWSKA – Ph.D., graduated from the Faculty of Technology and Chemical Engineering, Silesian University of Technology (1974). She is an adjunct in Inorganic Chemistry Division „IChN” in Gliwice of Fertilizers Research Institute. She is interested in inorganic technology and environmental protection. e-mail: [email protected], tel.: (32) 231-30-51÷54 Table 4 Sorption properties of sodium bicarbonate Indicator Ri , mol/mol Ci, g/kg Score Alhstrom’s scale P1 1.7 150 Excellent P2 1.6 157 Excellent Sample Conclusions For the assesment of the reactive properties of sodium bicabonate used in the processes of dry purification of flue gases, the analysis of surface structure, including surface area and morfology of pores were done. The investigations of the simultaneous effect of both: mechnical (grinding) and thermal activation on the development of surface area have shown a large increement in surface area and porosity because of the opening of pores on the grains surface. The structural analyses of samples, using a scanning microscope confirmed the results of the surface area examinations conducted by the BET and mercury porosimetry methods. The surface area measured by these methods can have different values. The surface area, measured by the mercury porosimetry method (determining the macropores) obtained after the complete decomposition of the ground sorbent at the temperature of 250°C, is larger, approx. 9 m2/g, than the surface area determined by the BET method (micro- and mesopores), approx. 7 m2/g. The increase of surface area values was from 0.07 m2/g for non – modified sorbent to 7-9 m2/g indicated the high reactivity of sodium bicarbonate. It was confirmed by Alhstrom tests. The reactivity indices were determined the high sorption potential of both unmodified and mechanically modified sodium bicarbonate. 1176 • Arkadiusz SZYMANEK – Sc.D., Professor of Czestochowa University of Technology, graduated from the Faculty of Civil and Environmental Engineering of Czestochowa University of Technology (1995). He obtained Ph.D. degree (2000) from the Institute of Thermal technique and Fluid Mechanics of Wroclaw University of Technology and habilitated in 2009 on Energeticko Stratelna Fakulta, Zilinska Universita. In 2010 he was an associated professor on Czestochowa University of Technology. Nowadays He is employed on the position of professor in the Institute of Advanced Power Technology from the Faculty of Engineering and Environmental Protection of Czestochowa University of Technology. Manyfold He has received the number of accolades from rector of Czestochowa University of Technology. Research topics: power engineering. He is the author and co-author of 2 monographs, 2 didactic scripts, over 90 original reviews, publications presented during national and foreign conferences. e-mail: [email protected], tel.: (34) 325‒09‒33. Anna PAJDAK – M.Sc., graduated from the Faculty of Engineering and the Environment Czestochowa University of Technology (2004). She is PhD student at the Institute of Advanced Energy Technologies of the university. He is co-author of the publication in the scientific – technical press and poster presented at the national conference. Interests: chemical engineering. e-mail: [email protected] Marzena NOWAK – M.Sc., graduated from Faculty Chemistry, Silesian University of Technology (2009). She is an technologist in Inorganic Chemistry Division „IChN” in Gliwice of Fertilizers Research Institute. She is interested in inorganic technology. e-mail: [email protected] nr 11/2012 • tom 66