TGA-FT-IR Analysis of Evolution of Oxygenated Organics by Isothermal Low-Temperature Decomposition of Rice Straw Hydrolysis Residue

Document Type : Research Article

Author

Department of Chemical Engineering, Sant Longowal Institute of Engineering and Technology, Longowal, Sangrur, Punjab, INDIA

Abstract

The study presents a TGA-FT-IR analysis of low-temperature thermochemical transformations of Rice straw hydrolysis residue (RSHR). Isothermal decomposition of RSHR was carried out for 3 h, at decomposition temperatures of 200, 250, 300, and 350 oC. At 200 oC, the rate of mass loss never exceeds %1/min and except for the first five minutes, it is less than %0.5/min. The initial rate of mass loss at 250 oC is %1.6/min which quickly drops to %0.6/min in the first 10 minutes and goes on further decreasing thereafter. At 300 oC, there is a rapid initial mass loss with the initial rate peaking at %8.8/min. At 350 oC, there is an initial burst of volatiles accounting for most of the mass loss with the initial rate of mass loss being %50/min. The residual mass obtained after these runs was 81.5, 38, 24, and 15%, respectively. FT-IR spectra of evolved gases suggest that volatile oxygenated organics along with non-condensable components like CO2, and CO are evolved during low-temperature thermal decomposition of RSHR. Carbonyls – acids, esters, aldehydes, and ketones – are the main functional groups in the volatiles. Strong absorption bands ranging 3400 – 3900 cm-1 indicated the presence of alcohols and phenols as other functional groups. Decomposition residues, the biochar, were demethoxylated and dehydrogenated compared to RSHR but retained their basic lignocellulosic nature.

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Main Subjects


[2] Borah N., Barua R., Nath D., Hazarika K., Phukon A., Goswami K., Barua D.C., Low Energy Rice Stubble Management Through in Situ Decomposition, Procedia Environ. Sci., 35: 771 – 780 (2016).
 http://164.100.94.214/sites/default/files/uploads/biofuel_policy_0.pdf. Accessed 11 March 2019.
[4] Taherzadeh M.J., Karimi K., Acid-Based Hydrolysis Processes for Ethanol From Lignocellulosic Materials: A Review, BioRes., 2: 472-499 (2007).
[5] Wang C., Duan X., Wang W., Li Z., Qin Y., Establishment and Verification of A Shrinking Core Model for Dilute Acid Hydrolysis of Lignocellulose, Front. En., 6: 413–419 (2012).
[6] Chandel A.K., Garlapati V.K., Singh A.K., Antunes F.A.F., da Silva S.S., The Path Forward for Lignocellulose Biorefineries: Bottlenecks, Solutions, and Perspective on Commercialization, Bioresource Technol., 264: 370-381 (2018).
[7] Zhang Y.H.P., Reviving the Carbohydrate Economy via Multi-Product Lignocellulose Biorefineries, J. Ind. Microbiol. Biotechnol., 35: 367–375 (2008).
[8] Baranitharan P., Jeyabalaganesh G., Ramesh K., A Complete Characterization of Solid, Liquid and Gas Phase Products Derived from the Thermochemical Pathway of New Feedstock Grevillea Robusta Sawdust, Iran. J. Chem. Chem. Eng. (IJCCE) [in Press], (2023). DOI: 10.30492/IJCCE.2023.2001861.6019.
[9] Tang Y., Ma X., Wang Z., Wu Z., Yu Q., A Study of the Thermal Degradation of Six Typical Municipal Waste Components in CO2 and N2 Atmospheres Using TGA-FT-IR, Thermochim. Acta, 657: 12–19 (2017).
[10] Chen T., Li L., Zhao R., Wu J., Pyrolysis Kinetic Analysis of the Three Pseudocomponents of Biomass–Cellulose, Hemicellulose and Lignin, J. Therm. Anal. Calorim., 128: 1825–1832 (2017).
[11] Hatakeyama H., Tsujimoto Y., Zarubin M.J., Krutov S.M., Hatakeyama T., Thermal Decomposition and Glass Transition of Industrial Hydrolysis Lignin, J. Therm. Anal. Calorim., 101: 289–295 (2010).
[12] Iliopoulou E.F., Antonakou E.V., Karakoulia S.A., Vasalos I.A., Lappas A.A., Triantafyllidis K.S., Catalytic Conversion of Biomass Pyrolysis Products by Mesoporous Materials: Effect of Steam Stability and Acidity of Al-MCM-41 Catalysts, Chem. Eng. J., 134: 51–57 (2007).
[13] Chen D., Gao A., Cen K., Zhang J., Cao X., Ma Z., Investigation of Biomass Torrefaction Based on Three Major Components: Hemicellulose, Cellulose, and Lignin, En. Conv. Mana., 169: 228–237 (2018).
[14] Reddy I.A.K., Ghatak H.R., Low-Temperature Thermal Degradation Behaviour of Non-Wood Soda Lignins and Spectroscopic Analysis of Residues, J. Therm. Anal. Calorim., 132: 407–423 (2018).
[16] Li M., Chen L., Li X., Chen C., Lai Y., Xiao X., Wu Y., Evaluation of the Structure and Fuel Properties of Lignocelluloses Through Carbon Dioxide Torrefaction, En. Conv. Mana., 119: 463–472 (2016).
[17] Sanchez G., Pilcher L., Roslander C., Modig T., Galbe M., Liden G., Dilute-Acid Hydrolysis for Fermentation of the Bolivian Straw Material Paja Brava, Bioresource Technol., 93: 249–256 (2004).
[18] Karimi K., Kheradmandinia S., Taherzadeh M.J. Conversion of Rice Straw to Sugars by Dilute-Acid Hydrolysis, Biomass Bioenergy, 30: 247–253 (2006).
[19] Rabemanolontsoa H., Saka S., “Holocellulose Determination in Biomass”, Springer, Tokyo, 135–140 (2012).
[20] Yuzbasi N.S., Selçuk N., Air and Oxy-Fuel Combustion Characteristics of Biomass/Lignite Blends in TGA-FT-IR, Fuel Process. Technol., 92: 1101–1108 (2011).
[21] Cao X., Zhong L., Peng X., Sun S., Li S., Liu S., Sun R., Comparative Study of the Pyrolysis of Lignocellulose and its Major Components: Characterization and Overall Distribution of their Biochars and Volatiles, Bioresource Technol., 155: 21–27 (2014).
[22] Xu F., Yu J., Tesso T., Dowell F., Wang D., Qualitative and Quantitative Analysis of Lignocellulosic Biomass Using Infrared Techniques: A Mini-Review, Appl. En., 104: 801–809 (2013).