Abstract
In this work, compositions containing transparent glass bottles and banana leaves (desiccated and crushed), with different mass fractions (30-50%), were prepared for obtaining cellular materials for thermal insulation purposes. The formulated and prepared compositions were uniaxially pressed (10 MPa) and the compact powders fired between 700 and 850°C for 30 min in order to investigate the effect of the banana leaves on the formation of pores and on the thermal and mechanical properties of the processed glass foams. The results indicated that the obtained glass foams with porosities between 58.5 and 87.5%, compressive strength ranging between 1.17 and 3.50 MPa and thermal conductivity ranging between 0.06 and 0.15 W/mK, are potential candidates to work as thermal insulators with appropriate properties for a specific application.
Keywords
Cellular materials; wastes; glass foams; banana leaves
1. Introduction
Several different materials can be used for the manufacture of porous ceramics such as alumina, mullite, silicon carbide, zirconia and hydroxyapatite. However, recent studies have shown numerous advantages and possibilities for the use of discarded glasses to obtain glass foams11 Scheffler M, Colombo P, eds. Cellular Ceramics: Structure, Manufacturing, Properties and Applications. Weinheim: Wiley-VCH; 2005.
2 Rouquerol J, Avnir D, Fairbridge CW, Everett DH, Haynes JM, Pernicone N, et al. Recommendation for the characterization of porous solids. Pure and Applied Chemistry. 1994;66(8):1739-1758.-33 Zhu X, Jiang D, Tan S. Preparation of silicon carbide reticulated porous ceramics. Materials Science and Engineering: A. 2002;323(1-2):232-238..
The use of glass foams is viable in applications involving temperatures lower than 500 °C, for example in thermal insulation systems used in building such as panels, blocks, roofs, fireplaces, grills, among others11 Scheffler M, Colombo P, eds. Cellular Ceramics: Structure, Manufacturing, Properties and Applications. Weinheim: Wiley-VCH; 2005.. These materials are also characterized by high porosity (> 60% vol.) which can be opened, closed or mixed. The pore size, according to International Union of Pure and Applied Chemistry (IUPAC)22 Rouquerol J, Avnir D, Fairbridge CW, Everett DH, Haynes JM, Pernicone N, et al. Recommendation for the characterization of porous solids. Pure and Applied Chemistry. 1994;66(8):1739-1758. can be classified as micro (<2 nm), meso (2-50 nm) or macropores (>50 nm). The distribution and amount of pores determine specific properties, such as low density and thermal conductivity, high surface area, permeability and chemical and thermal stability11 Scheffler M, Colombo P, eds. Cellular Ceramics: Structure, Manufacturing, Properties and Applications. Weinheim: Wiley-VCH; 2005.,44 Barg S, Soltmann C, Andrade M, Koch D, Grathwohl G. Cellular ceramics by direct foaming of emulsified ceramic powder suspensions. Journal of the American Ceramic Society. 2008;91(9):2823-2829.,55 Zeschky J, Goetz-Neunhoeffer F, Neubauer J, Jason Lo SH, Kummer B, Scheffler M, et al. Preceramic polymer derived cellular ceramics. Composites Science and Technology. 2003;63(16):2361-2370.. Furthermore, glass foams have mechanical strength and chemical and thermal stabilities greater than the polymeric foams typically employed in such cases11 Scheffler M, Colombo P, eds. Cellular Ceramics: Structure, Manufacturing, Properties and Applications. Weinheim: Wiley-VCH; 2005.,66 Bernardo E, Cedro R, Florean M, Hreglich S. Reutilization and stabilization of wastes by the production of glass foams. Ceramics International. 2007;33(6):963-968.,77 Gibson LJ, Ashby MF. Cellular Solids: Structure and Properties. 2nd ed. New York: Cambridge University Press; 1999..
Several techniques or methods for producing porous ceramics are used and the process steps generally consist in preparing a suspension of a ceramic powder, forming and heat treatment (firing). Among the best known forming methods the replication method, gelcasting, foaming and incorporation of porogenic agents (pore formers) are highlighted11 Scheffler M, Colombo P, eds. Cellular Ceramics: Structure, Manufacturing, Properties and Applications. Weinheim: Wiley-VCH; 2005.,88 Studart AR, Gonzenbach UT, Tervoort E, Gauckler LJ. Processing routes to macroporous ceramics: A review. Journal of the American Ceramic Society. 2006;89(6):1771-1789.. Due to its simplicity, one of the techniques widely used for the production of glass foams, is the addition of a foaming agent to the powdered glass, followed by its removal in the heat treatment step (firing) to form a cellular structure 6, 7. The foaming agents can be synthetic (polymer) or natural (mineral and vegetable residues)77 Gibson LJ, Ashby MF. Cellular Solids: Structure and Properties. 2nd ed. New York: Cambridge University Press; 1999.,99 Sousa E, Rambo CR, Montedo ORK, Hotza D, Oliveira APN. Glass ceramics porous LZSA system using organic waste as pore-forming agent. Exacta. 2006;4(2):289-296 (in Portuguese)..
The natural residues show different constituents such as cellulose, hemicellulose and lignin, which open many value adding opportunities and can be a low cost alternative for use as foaming agents. Significant plant residues in tropical regions comes from banana cultivation, as banana leaves and pseudostem1010 Sellin N, Oliveira BG, Marangoni C, Souza O, Oliveira APN, Oliveira TMN. Use of banana culture waste to produce briquettes. Chemical Engineering Transactions. 2013;32:349-354.. Banana is one of the most consumed fruits in the world and it is commercially grown in about 120 countries. Currently, Brazil is the second largest producer (preceded by India) and is responsible for 7.5% of world production. Further, for every ton of bananas produced approximately 3,000 kg of pseudostem, 160 kg of stems, 480 kg of leaves and 440 kg of skins are generated1111 Bello RH, Linzmeyer P, Franco CMB, Souza O, Sellin N, Medeiros SHW, et al. Pervaporation of ethanol produced from banana waste. Waste Management. 2014;34(8):1501-1509..
The glass used in the manufacture of glass foams can, however, also be glass from the disposal. The recycling and the use of glass can contributes to the national energy matrix through the large amount of energy savings since to produce 1 kg of new glass 4500 kJ are needed, while to produce 1 kg of recycled glass 500 kJ only are needed1212 Alves OL, Gimenes IF, Mazalli IO. Vidros. Cadernos Temáticos - Química Nova na Escola - Novos Materiais. 2001;Edição Especial:9-20 (in Portuguese).,1313 Scarinci G, Brusatin G, Barbieri L, Corradi A, Lancellotti I, Colombo P, et al. Vitrication of industrial and natural wastes with production of glass ?bers. Journal of European Ceramic Society. 2000;20(14-15):2485-2490.. In order to reduce production costs and get raw materials, several modifications have been applied to the processing techniques and starting materials66 Bernardo E, Cedro R, Florean M, Hreglich S. Reutilization and stabilization of wastes by the production of glass foams. Ceramics International. 2007;33(6):963-968.. In addition, glass foams represent an interesting destination for glass wastes and vegetables from an economic and environmental point of view.
In this context, the objective of this work was to produce cellular materials (glass foams) from glass bottles and banana leaves in different mass fractions to be used as thermal insulators.
2. Materials and Methods
In this study transparent glass bottles, TGB (soda-lime type) and banana leaves (BL) were used as raw materials. The selected glass bottles were washed and dried at 110 °C for 2 h in a laboratory dryer (SP LABOR®). In a subsequent step, the glass bottles were crushed in a crusher hammer (Servitech, CT-058), and the resulting product milled for 30 min in a fast mill (Servitech, CT-242) constituted by a porcelain jar containing alumina balls and water such that powders with particle sizes lower than 44 µm (325 Mesh) were obtained. The average particle size distribution (d50 = 6 µm) of the resultant material was determined using a laser scattering particle size analyzer (Master Sizer 2000, Malvern). The chemical characterization of the obtained glass powders was performed by X-ray fluorescence spectroscopy (XRF, Philips PW 2400).
Samples of dried banana leaves were obtained directly from banana trees but only the dried leaves were collected. The pseudostem was obtained only from plants that had been cut for obtaining fruit and were decomposing in the soil. The pseudostem, since it has a high humidity content, was pressed in a hydraulic press to remove the largest liquid fraction and then it was dried in a forced ventilation muffle at 60 ºC for 24 h. Both samples were milled so that a powder with an average particle size of 2.5 mm was obtained. The obtained powder samples were characterized by proximate chemical analysis, following procedures described in ASTM E1871-82 (2006) for moisture, ASTM E872-82 (2006) for volatile materials, ASTM E1755-01 (2007) for ash and ASTM E1756-08 (2008) for total solids and fixed carbon; elemental chemical analysis (carbon, nitrogen and hydrogen) by elemental analyzer (Perkin-Elmer CHN 2400) and sulfur by atomic emission spectrometer with inductively coupled plasma (Spectro Ciros CCD). The samples of both wastes were dried at 110 °C for 2 h in a muffle and then mixed (dry mixing in a ball mill for 5 min) with different proportions of TGB (50-70 wt%) and BL (30-50 wt%) and with addition of 5% water. The prepared mixtures were at a later stage, uniaxially pressed (10 MPa) in a steel matrix by means of a hydraulic press (Bovenau P10 ST). The obtained powder compacts in the form of discs (10 x 6 mm) were dried at 110 °C for 2 h.
The thermal behaviour during firing of raw materials and prepared compositions was studied by means of an optical dilatometer (Expert System Solution Misura ODHT) and by a thermal analyser equipment (TA Instruments, SDT Q600 - Simultaneous TGA-DSC) at a heating rate of 10 °C/min with a flow of synthetic air of 10 cm3/min.
Based on the thermal analyses, green compacts were heated in a muffle furnace (Jung J200) up to 600 ºC at 0.5 ºC/min with a holding time of 30 min (first step) and then heated at different temperatures (700, 800 e 850 °C) for 30 min at 10 °C/min (second step) and finally cooled to room temperature, ~25 °C (third step).
To identify the crystalline phases formed during firing, diffractometric analysis were carried out in a X-ray diffractometer (Philips, model X'Pert, The Netherlands). In this case, powdered samples fired in the 700-850 °C temperature range were prepared. A glass sample (unheat-treated one) was also prepared and subjected XRD analysis.
The true densities (ρ t) of powdered samples were determined by using a helium pycnometer (AccuPyc 1340, Micromeritics, USA). The apparent densities (ρ a) of fired samples were determined by relating their geometrical measurements, obtained using a caliper (Mitotoyo, accuracy ± 0.01 mm), and their masses (Shimadzu AX200 at 0.001 g). The relative densities (ρ r) were determined, relating the apparent densities and the true densities of the samples. From measurements of geometrical and true densities (same procedures used for powder compacts), the porosities (ε) of fired glass foams were calculated according to equation 1.
The microstructure of pores could be seen from images of fractured surfaces of fired samples, obtained in a scanning electron microscope, SEM (Philips, XL-30).
To determine the mechanical strength of the produced glass foams, compression tests (Stable Micro Systems TA. XT Plus Texture Analyzer - cell load of 500 N) at ~25 °C were performed on 5 cylindrical samples (10 mm diameter) with a loading speed of 1 mm/min.
The thermal conductivity of the obtained materials was determined by a TCi Thermal Conductivity C-THERM TECHNOLOGIES on disk-shaped samples of 30 mm diameter and 8 mm thick.
3. Results and Discussion
Table 1 shows the chemical composition of the transparent glass bottle (TGB) used in this work. It can be verified the predominant presence of SiO2, Na2O and CaO in amounts typically found in soda-lime-silica glasses.
Figure 1 shows linear shrinkage and differential scanning calorimetric (DSC) curves related to the TGB. As observed, combining the techniques of dilatometry and differential scanning calorimetry (DSC), it can follow the thermal behavior of the TGB. It is found that there is a discontinuity in the baseline around 520 ºC, which is characteristic of the glass transition temperature (Tg)1414 Padilha AF. Materiais de Engenharia: Microestrutura e Propriedades. São Paulo: Hemus; 2000 (in Portuguese)..
Linear shrinkage (also showing pictures of specimen tested in different temperatures) and DSC curves of the TGB.
It is also observed in Figure 1, an endothermic peak at about 1000 °C which may be attributed to the melting (Tm) of the glass (melting of the crystalline phases formed during the heating of the glass), which can be confirmed by observing the linear shrinkage curve and the images (in the same Figure) obtained during this thermal analysis. Moreover, according to X-ray diffractions (Figure 2), in fact, crystobalite, JCPDS 01.076-0939 (main crystalline phase) and calcium-sodium silicate, JCPDS 00.023-0671 toke place in the 700-850 °C temperature range (Figure 2 (b-d)) and from 800 °C (Figure 2 (c-d)), respectively. Thus, it clear, according to Figure 2 (a) for a glass sample (unheat-treated sample) that crystallization toke places in the studied temperature range explaining thus the observed (in Figure 1) melting temperature.
X-ray diffraction patterns of the glass sample (unheat-treated one) (a) and after firing at 700(b), 800(c), 850 ºC/30 min(d). ♦ Cristobalyte (JCPDS 01.076-0939) ● Calcium sodium silicate (JCPDS 00.023-0671)
It is observed further from the linear shrinkage curve that around 600 °C begins the sintering processes of the glass powder. At 850 °C the glass powder compacts start to lose their geometric shape, probably explained by the low glass viscosity with increasing temperature. At 900 °C the glass already has a ball-shape and at 1000 °C, it may realizes by dilatometry (in terms of shrinkage) and by DSC, that the glass melting (Tm) occurred.
Table 2 shows the results of proximate elemental and chemical analysis of BL samples1010 Sellin N, Oliveira BG, Marangoni C, Souza O, Oliveira APN, Oliveira TMN. Use of banana culture waste to produce briquettes. Chemical Engineering Transactions. 2013;32:349-354..
The moisture of the BL used was approximately 8%. The biomass moisture is an important factor since it interferes directly on other parameters such as the lower heating value, which decreases with increasing moisture content and thermal conductivity1010 Sellin N, Oliveira BG, Marangoni C, Souza O, Oliveira APN, Oliveira TMN. Use of banana culture waste to produce briquettes. Chemical Engineering Transactions. 2013;32:349-354.,1515 Fernandes ERK, Marangoni C, Souza O, Sellin N. Thermochemical characterization of banana leaves as a potential energy source. Energy Conversion and Management. 2013;75:603-608.. The volatile solid contents indicate the presence of organic matter and represent lignocellulosic and carbon fractions present in the samples, and expresses the weight amount of the components of biomass which first are combusted1515 Fernandes ERK, Marangoni C, Souza O, Sellin N. Thermochemical characterization of banana leaves as a potential energy source. Energy Conversion and Management. 2013;75:603-608.,1616 García R, Pizzaro C, Lavín AG, Bueno JL. Characterization of Spanish biomass wastes for energy use. Bioresource Technology. 2012;103(1):249-258.. The ashes represent 6.2% of the total. Studies indicate low ash concentration in biomass from 0.3 to 1%, but in agricultural residues such as rice husks, ashes may represent 23% and less than 3% for sugar cane bagasse1010 Sellin N, Oliveira BG, Marangoni C, Souza O, Oliveira APN, Oliveira TMN. Use of banana culture waste to produce briquettes. Chemical Engineering Transactions. 2013;32:349-354.,1515 Fernandes ERK, Marangoni C, Souza O, Sellin N. Thermochemical characterization of banana leaves as a potential energy source. Energy Conversion and Management. 2013;75:603-608.,1717 Demirbas A. Combustion characteristics of different biomass fuels. Progress in Energy and Combustion Science. 2004;30(2):219-230.. The carbon content found was 43.4%.
Figure 3 shows the weight loss, from thermogravimetry analysis (TGA), and differential scanning calorimetry (DSC) curves of the BL. The BL showed two stages of thermal degradation.
The first (a) from room temperature to about 150 °C, which is related to moisture loss from the sample, corresponding to a weight loss of 10.7% for the leaves. These values are close to those found by proximate analysis, presented earlier. In the second stage (b), between 150 °C and 580 °C, a largest weight loss attributed to volatile materials and degradation of hemicellulose (cellulose and lignin portion - constituents of the biomass) was registered, with mass losses for the leaves samples of 80.3%. At this stage it is also possible to identify the ignition temperature of the biomass combustion process1717 Demirbas A. Combustion characteristics of different biomass fuels. Progress in Energy and Combustion Science. 2004;30(2):219-230..
The results indicate that 91% of BL decompose up to 580 °C. Still according to Figure 2, the exothermic peaks correspond to thermal degradation of hemicellulose fractions stages, cellulose and lignin gradually. The greater release of energy in which occurs the degradation of volatiles was observed in the second event nearly at 400°C. The thermal degradation of biomass products consist of moisture, volatiles and ash55 Zeschky J, Goetz-Neunhoeffer F, Neubauer J, Jason Lo SH, Kummer B, Scheffler M, et al. Preceramic polymer derived cellular ceramics. Composites Science and Technology. 2003;63(16):2361-2370.. The volatiles are subdivided into gases, such as light hydrocarbons, carbon monoxide, carbon dioxide and tar. Yields depend on the temperature and heating rate1717 Demirbas A. Combustion characteristics of different biomass fuels. Progress in Energy and Combustion Science. 2004;30(2):219-230..
Based on the thermal behavior of the TGB and BL, it was defined the following firing cycle of the compacts constituted by TGB and BL: heating at 0.5 °C/min up to 600 °C for 120 min to decomposition of BL and thus the release of CO/CO2 gases which are responsible for the formation of pores. This temperature (600 °C) is near the glass transition (Tg) and the TGB, despite being in a viscous state, still retains the cell structure caused by the decomposition of leaves. Subsequently, the temperature was increased to 700, 800, 850 °C at 10 °C/min to promote the sintering of the bodies and thus the trapping of gases released in the decomposition step of the banana leaves. Figures 4 show the effect of the firing temperature and BL content on the apparent density of the produced glass foams.
Effect of the firing temperature and BL content on the apparent density of the produced glass foams.
It can be seen from Figure 4 that the apparent densities ranged between 0.31 and 1.03 g/cm33 Zhu X, Jiang D, Tan S. Preparation of silicon carbide reticulated porous ceramics. Materials Science and Engineering: A. 2002;323(1-2):232-238.. Compositions with 50% added BL showed the lowest densities for all tested sintering temperatures.
Figure 5 shows the results of mechanical strength (σf) tests and porosity (ε) of glass foams with additions of 30, 40 and 50% BL, fired at 700, 800 and 850 °C for 30 min.
Effect of the firing temperature on the mechanical strength (σf) and porosity (ε) of the produced glass foams for different compositions (BL/TGB).
As can be seen, the porosity of the produced glass foams ranged from 58.5 to 87.5%. As the firing temperature increases from 700 to 800 °C the porosity remained practically constant. However, at 850 °C there is a significant decrease in porosity for all studied compositions, in contrast to the apparent density, which is related to a decrease of the glass viscosity which was not sufficient to maintain the cell structure, since 850 °C is very close to its melting temperature, as previously mentioned. The sharp decreases of the mechanical strength of the glass foams of all compositions with increasing firing temperature, i.e., from 700 to 800 °C can be associated, probably, to the crystobalite formation as shown in the XRD (Figure 2) since it has a very high coefficient of thermal expansion which results in crack formation during cooling process. With the increment of temperature from 800 to 850 °C, the mechanical strength increases due a porosity decreasing associated, probably, to a decreasing of the glass (TGB) viscosity, as previously mentioned, which causes the rupture of the pore's walls allowing the gases to escape (specially for samples containing high BL concentrations) resulting in a lower porosity (glass densification). The rupture of the pore's walls and so the escape of gases is a consequence of the high internal pressure which expand the porous in the low viscous glass. In fact, in the glass working range temperature, the viscosity (106.6 to 1033 Zhu X, Jiang D, Tan S. Preparation of silicon carbide reticulated porous ceramics. Materials Science and Engineering: A. 2002;323(1-2):232-238. Pa·s) is low enough, allowing the pressure of the produced gases from the decomposition of the foaming agent, expands the glass producing porosity which can be controlled depending on the selected temperature and holding time at temperature. This can explain why samples fired at 850 °C have a reverse mechanical strength behavior. However, even if porosity values are lower than those of samples fired at 700 and 800 °C, crystobalite volume (Figure 2) seems to be higher (higher peak intensity) than that observed at 800 °C but in particular than the sample fired at 700 °C for 30 min. Thus, seems that crystobalite as porosity has an important influence on the mechanical strength.
Figure 6 shows the results of thermal conductivity of glass foams with additions of 30, 40, 50% BL fired at 700, 800, 850 °C for 30 min.
Thermal conductivity of glass foams with additions of 30, 40, 50% BL fired at 700, 800, 850 °C for 30 min, respectively.
It can be seen that the thermal conductivity of the produced glass foams decreases with increasing firing temperature (700 to 800 °C). This is due to the contribution of a higher porosity which reduces the thermal conductivity, especially in cases where the pores are closed and no interconnected. With the increment of temperature from 800 to 850 °C, it is found that the thermal conductivity increases due a porosity decreasing in good agreement with the literature11 Scheffler M, Colombo P, eds. Cellular Ceramics: Structure, Manufacturing, Properties and Applications. Weinheim: Wiley-VCH; 2005..
In fact, Figure 7 shows micrographs showing the mentioned before aspects.
As is known, in general, the porosity causes a decrease in the mechanical strength of the materials. Typically, the subjected foams have a mechanical (compressive strength) behavior characterized by three regimens, i.e., linear elastic, plateau and densification. Initially occurs the elastic deformation of the walls and/or struts of the glass foams. The plateau region, the second stage, begins when there is a sharp drop in the stress value which is associated with fracture of the material. This region presents large fluctuations of stress due to the successively breaking of struts which constitute the glass foam. In the third stage of the process, the stress increases due to densification of the glass foam77 Gibson LJ, Ashby MF. Cellular Solids: Structure and Properties. 2nd ed. New York: Cambridge University Press; 1999..
4. Conclusions
Based on the proposed objectives of this work, it is concluded that produced glass foams fired between 700 and 850 °C for 30 min and with porosities between 58.5 and 87.5% had compressive strength ranging between 1.17 and 3.50 MPa and thermal conductivity ranging between 0.06 and 0.15 W /mK.
The dried banana leaves proved to be a vegetable residue with interesting properties for use as foaming agent, indicating new applications for this residue.
The values of the evaluated properties indicate that the obtained glass foams can be recommended as heat insulation panels which require an appropriate combination of thermal conductivity, porosity and mechanical strength.
5. Acknowledgments
The authors are grateful to FAPESC/CNPq (PRONEX T.O. N. 17431/2011-9) for funding this work.
6. References
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1Scheffler M, Colombo P, eds. Cellular Ceramics: Structure, Manufacturing, Properties and Applications Weinheim: Wiley-VCH; 2005.
-
2Rouquerol J, Avnir D, Fairbridge CW, Everett DH, Haynes JM, Pernicone N, et al. Recommendation for the characterization of porous solids. Pure and Applied Chemistry 1994;66(8):1739-1758.
-
3Zhu X, Jiang D, Tan S. Preparation of silicon carbide reticulated porous ceramics. Materials Science and Engineering: A 2002;323(1-2):232-238.
-
4Barg S, Soltmann C, Andrade M, Koch D, Grathwohl G. Cellular ceramics by direct foaming of emulsified ceramic powder suspensions. Journal of the American Ceramic Society 2008;91(9):2823-2829.
-
5Zeschky J, Goetz-Neunhoeffer F, Neubauer J, Jason Lo SH, Kummer B, Scheffler M, et al. Preceramic polymer derived cellular ceramics. Composites Science and Technology 2003;63(16):2361-2370.
-
6Bernardo E, Cedro R, Florean M, Hreglich S. Reutilization and stabilization of wastes by the production of glass foams. Ceramics International 2007;33(6):963-968.
-
7Gibson LJ, Ashby MF. Cellular Solids: Structure and Properties 2nd ed. New York: Cambridge University Press; 1999.
-
8Studart AR, Gonzenbach UT, Tervoort E, Gauckler LJ. Processing routes to macroporous ceramics: A review. Journal of the American Ceramic Society 2006;89(6):1771-1789.
-
9Sousa E, Rambo CR, Montedo ORK, Hotza D, Oliveira APN. Glass ceramics porous LZSA system using organic waste as pore-forming agent. Exacta 2006;4(2):289-296 (in Portuguese).
-
10Sellin N, Oliveira BG, Marangoni C, Souza O, Oliveira APN, Oliveira TMN. Use of banana culture waste to produce briquettes. Chemical Engineering Transactions 2013;32:349-354.
-
11Bello RH, Linzmeyer P, Franco CMB, Souza O, Sellin N, Medeiros SHW, et al. Pervaporation of ethanol produced from banana waste. Waste Management 2014;34(8):1501-1509.
-
12Alves OL, Gimenes IF, Mazalli IO. Vidros. Cadernos Temáticos - Química Nova na Escola - Novos Materiais 2001;Edição Especial:9-20 (in Portuguese).
-
13Scarinci G, Brusatin G, Barbieri L, Corradi A, Lancellotti I, Colombo P, et al. Vitrication of industrial and natural wastes with production of glass ?bers. Journal of European Ceramic Society 2000;20(14-15):2485-2490.
-
14Padilha AF. Materiais de Engenharia: Microestrutura e Propriedades São Paulo: Hemus; 2000 (in Portuguese).
-
15Fernandes ERK, Marangoni C, Souza O, Sellin N. Thermochemical characterization of banana leaves as a potential energy source. Energy Conversion and Management 2013;75:603-608.
-
16García R, Pizzaro C, Lavín AG, Bueno JL. Characterization of Spanish biomass wastes for energy use. Bioresource Technology 2012;103(1):249-258.
-
17Demirbas A. Combustion characteristics of different biomass fuels. Progress in Energy and Combustion Science 2004;30(2):219-230.
Publication Dates
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Publication in this collection
11 Aug 2016 -
Date of issue
Sep-Oct 2016
History
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Received
10 Oct 2015 -
Reviewed
02 May 2016 -
Accepted
25 July 2016